A Pilot Study of
 Children's Total Exposure
to Persistent Pesticides and
   Other Persistent Organic
          Pollutants (CTEPP)
    M.K. Morgan, L.S. Sheldon, and C.W. Croghan.
          U.S. Environmental Protection Agency
                  Research Triangle Park, NC

    J.C. Chuang, R.A. Lordo, N.K. Wilson, C. Lyu,
            M. Brinkman, N. Morse, Y.L. Chou,
            C. Hamilton, J.K. Finegold, K. Hand,
       and S.M. Gordon. Battelle, Columbus, Ohio
                     PB2006-101286
                     Volume I: Final Report
                     EPA/600/R-04/193

               Contract Number 68-D-99-011
                         Task Order 0002
                 Task Order Project Officer
                         Marsha K. Morgan
          U.S. Environmental Protection Agency
          National Exposure Research Laboratory
          Research Triangle Park, North Carolina
            Office of Research and Development
          National Exposure Research Laboratory
Human Exposure and Atmospheric Sciences Division
                  Research Triangle Park, NC

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                                    EPA Disclaimer
The information in this document has been funded wholly by the United States Environmental
Protection Agency under EPA contract number 68-D-99-011 to Battelle Memorial Institute.  It
has been subjected to the Agency's peer and administrative review and has been approved for
publication as an EPA document. Mention of trade names or commercial products does not
constitute endorsement or recommendation for use.
                                 Battelle Disclaimer
Battelle does not engage in research for advertising, sales promotion, or endorsement of our
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result obtained from Battelle, and Battelle, its employees, officers, or Trustees have no legal
liability for the accuracy, adequacy, or efficacy thereof.

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                                      Foreword
       The mission of the National Exposure Research Laboratory (NERL) is to provide
scientific understanding, information and assessment tools that will quantify and reduce the
uncertainty in EPA' s exposure and risk assessments for environmental stressors. These
stressors include chemicals, biologicals, radiation, and changes in climate, land use, and water
use.  The Laboratory's primary function is to measure, characterize, and predict human and
ecological exposure to pollutants.  Exposure assessments are integral elements in the risk
assessment process used to identify populations and ecological resources at risk. The EPA relies
increasingly on the results of quantitative risk assessments to support regulations, particularly of
chemicals in the environment. In addition, decisions on research priorities are influenced
increasingly by comparative risk assessment analysis.  The utility of the risk-based approach,
however, depends on accurate exposure information.  Thus, the mission of NERL is to enhance
the Agency' s capability for evaluating exposure of both humans and ecosystems from a holistic
perspective.

       The National Exposure Research Laboratory focuses on four major research areas:
predictive exposure modeling, exposure assessment, monitoring methods, and environmental
characterization. Underlying the entire research and technical support program of the NERL is
its continuing development of state-of-the-art modeling, monitoring, and quality assurance
methods to assure the conduct of defensible exposure assessments with known certainty. The
research program supports its traditional clients — Regional Offices, Regulatory Program
Offices, ORD Offices, and Research Committees — as well as ORD's Core Research Program in
the areas of health and ecological exposure analysis and assessment.

       Human exposure to multimedia contaminants, including persistent organic pollutants is
an area of concern to EPA because of the possible adverse health effects of these compounds.
These compounds may originate from industrial processes and combustion and are present in a
variety of microenvironments. The efforts described in this report provide an important
contribution to our ability to measure and evaluate human exposure to pollutants.
                                               Dr. Gary J. Foley
                                               Director
                                               National Exposure Research Laboratory
                                           in

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                                       Abstract
       The Pilot Study of Children's Total Exposure to Persistent Pesticides and Other
Persistent Organic Pollutants (CTEPP) investigated the aggregate exposures of 257 preschool
children and their primary adult caregivers to pollutants commonly detected in their everyday
environments. The target compounds include organophosphate (OP) pesticides, OP metabolites,
organochlorine (OC) pesticides, pyrethroid pesticides and metabolites, acid herbicides,
polycyclic aromatic hydrocarbons (PAH), phthalates, phenols, polychlorinated biphenyls (PCB),
PAH metabolites, and atrazine.  Some of the target compounds are persistent indoors and
sometimes outdoors, so that very low levels may exist in the children's surroundings and provide
a source of non-acute exposure. The primary purposes of the research were to increase the
understanding of children's exposures to persistent and non-persistent organic pollutants, and to
gain information on the various activities, environmental media, and pollutant characteristics that
may influence children's exposures. The overall objectives were to measure the aggregate
exposures of approximately 260 preschool children and their adult caregivers to low levels of a
suite of pesticides and other organic pollutants that the children may encounter in their everyday
environments and to apportion the routes of exposure and estimate the relative contributions of
each route. Within these objectives, four major, specific goals for the CTEPP study were
accomplished in this report. These goals were: (1) to measure the concentrations of the target
pollutants in multimedia samples collected at the homes and at day care centers of 257 preschool
children in six North Carolina (NC) counties and six Ohio (OH) counties, (2) to determine the
distributions of child characteristics, activities, and locations that contributed to their exposures,
(3) to estimate the aggregate exposures of the preschool children to these pollutants that they
may encounter in their everyday environments, and (4) to apportion the routes of exposure.
Results will also be used to identify important hypotheses to be tested in future research.

       A two-state sampling plan was used to select and recruit study participants.  In each state,
a total of four urban and two rural counties were randomly selected. The counties were located
in three distinct geographical regions of each state.  These regions were the mountains, the
Piedmont, and the coastal plain of NC, and the northern, central, and southern regions of OH.
Dual sampling frames (the day care and the telephone components) were used in each state.  To
recruit participants in households whose children attended child day care centers, 13 centers in
the six NC counties and 16 centers in the six OH counties were selected using probability
sampling. Children were then selected randomly from classrooms having children in the eligible
age group of two to five years, and their participation was recruited through their parents. To
recruit participants in households whose children did not attend child day care centers, list-
assisted, random digit dialing telephone sampling in the selected counties was used.
                                            IV

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       The calculated response rates in NC were 53% for day care centers and 50% for day care
parents. In OH these response rates were 57% for OH day care centers and 31% for OH day care
parents. The calculated response rate for the telephone sample was 58% in NC and 57% in OH.
In NC, children and their caregivers in 130 households participated in the study; in OH, 127
households participated. Approximately half of the children in each state attended child day care
centers (63 in NC and 58 in OH). About 84% of the NC participants and 87% of the OH
participants lived in urban locations. Low-income households, classified according to federal
guidelines for the Women,  Infants, and Children (WIC) program (185% of the federal poverty
level), comprised 46% of the sampled households in NC and 38% of those in OH.

       More than 5,000 discrete personal and environmental samples, including quality control
samples, were collected in  each state and analyzed.  Additionally, house/building characteristics
observation surveys, pre- and post-monitoring questionnaires, day care food menus, and detailed
child/adult time-activity and food diaries provided ancillary information necessary to estimate
aggregate exposures and to aid in interpretation of the CTEPP data.

       Field sampling for the day care component took place over a 48-h period at each child's
day care center and simultaneously at his/her home. Field sampling for the telephone component
took place over a 48-h period at each participant's home. Environmental samples included
indoor and outdoor air, outdoor play area soil, indoor floor dust (carpet dust) or if no carpet, hard
floor surface wipes, and household/day care drinking water.  Personal samples included
duplicate diet, hand wipes,  and urine. If a pesticide had been applied in the seven days prior to
or during sampling, transferable residues, hard floor surface wipes and food preparation surface
wipes were also collected. Approximately 10% of the children were videotaped for about 2 h at
their homes in OH during sampling to supplement and validate the activity diaries and
observations.

       All samples, including quality control samples, were extracted, and then analyzed by gas
chromatography/mass spectrometry for over 50 target compounds. These compounds included
two organophosphorus (OP) pesticides, two OP metabolites, ten organochlorine (OC) pesticides,
three pyrethroid pesticides, one pyrethroid metabolite, three acid herbicides, nine polycyclic
aromatic hydrocarbons (PAHs), six PAH metabolites, two phthalates, three phenols, 17
polychlorinated biphenyls (PCBs), and atrazine. These compounds, with the exception of
atrazine, PAH metabolites  and pyrethroid metabolites, were analyzed in the environmental and
personal samples. Atrazine was analyzed only in drinking water samples. Only one OP
metabolite, 3,5,6-trichloro-2-pyridinol (3,5,6-TCP), was analyzed in the NC environmental and
personal samples; both 2-isopropyl-6-methyl-4-pyrimidinol (IMP) and 3,5,6-TCP were measured
in the OH samples. In the NC urine samples, two OP metabolites; IMP and 3,5,6-TCP; 2,4-
dichlorophenoxyacetic acid (2,4-D), two hydroxy PAHs: 1-hydroxybenz[a]anthracene and 3-
hydroxychrysene; and pentachlorophenol were analyzed. In the OH urine samples, these same
metabolites and/or parent compounds were analyzed, in addition to five hydroxy PAHs (1-
hydroxypyrene, 3-hydroxybenz[a]anthracene, 3-hydroxybenzo[a]pyrene, 6-hydroxychrysene,
and 6-hydroxyindeno[l,2,3-cd]pyrene) and 3-phenoxybenzoic acid (3-PBA).

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       Two similarly formatted CTEPP databases were developed, one for the NC study and one
for the OH study. Each database contained questionnaire data, analytical data, and metadata, and
provided sufficient documentation to allow the data to be understood by a diverse set of users.
Descriptive statistics were calculated for sample size, mean, standard deviation, percentage
detected, minimum and maximum reported values, and selected percentiles (25th, 50th, 75th, and
95th). The distributions of participant characteristics, activities, and locations that are important
for exposure were quantified, based on the questionnaire data. Potential exposures and potential
absorbed doses were estimated for selected target compounds, based on the percentage of the
samples that had detectable levels of these compounds, the measured concentrations, the
participants' activity patterns, and assumed physiological parameters. Statistical analyses to
meet the four goals of the study were performed on log-transformed data, using analysis of
variance (ANOVA) models. The data summaries presented in this report represent only the
children and their primary caregivers in NC and OH who participated in this study.
                                            VI

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           DISCLAIMER
This document has been reproduced from the best
   copy furnished by the sponsoring agency.

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                                      Contents

Volume 1                                                                        Page
Foreword 	iii
Abstract  	iv
Contents	viii
Figures	x
Tables	 xii
Acknowledgments	 xvii

   Chapter 1 Introduction	1-1
             1.1    Background  	1-1
             1.2    Study Overview	1-2
   Chapter 2 Conclusions 	2-1
             2.1    Overview  	2-1
             2.2    Goal 1	2-2
             2.3    Goal 2	2-7
             2.4    Goal 3	2-8
             2.5    Goal 4	2-15
   Chapter 3 Recommendations 	3-1
   Chapter 4 Sampling Design and Participant Recruitment 	4-1
             4.1    Sampling Design 	4-1
             4.2    Recruitment	4-4
             4.3    Recruitment Results	4-9
             4.4    Evaluation 	4-15
             4.5    Recommendations  	4-16
   Chapter 5 Field Monitoring  	5-1
             5.1    Overview  	5-1
             5.2    Field Data Collection	5-2
             5.3    Results  	5-10
             5.4    Evaluation 	5-15
             5.5    Recommendations  	5-16
   Chapter 6 Sample Analysis Procedures  	6-1
             6.1    Overview  	6-1
             6.2    Procedures for North Carolina and Ohio Samples	6-4
             6.3    Evaluation 	6-36
             6.4    Recommendations  	6-37
   Chapter 7 CTEPP Database  	7-1
             7.1    Overview  	7-1
             7.2    Quality Assurance Procedures for the Database  	7-1
             7.3    EPA Review	7-4
             7.4    Evaluation 	7-5
             7.5    Recommendations  	7-5
   Chapter 8 Statistical Analyses  	8-1
                                          Vlll

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             8.1    Overview of Data Analysis 	8-1
             8.2    Preparation for Statistical Analysis	8-3
             8.3    Strata Considered in the Statistical Analysis	8-8
             8.4    Procedures for Calculating Potential Exposure and Potential Absorbed
                    Dose	8-9
             8.5    Statistical Analysis	8-15
   Chapter 9 Results and Discussion  	9-1
             9.1    Overview 	9-1
             9.2    Method Quantifiable Limits and Compound Prevalence  	9-1
             9.3    Goal 1: To measure the environmental concentrations of pesticides
                    and other persistent and non-persistent organic pollutants in
                    multimedia (environmental and personal samples) at participating
                    homes and day care centers	9-14
             9.4    Goal 2: To quantify the distributions of child characteristics, activities,
                    and location that are important for exposure	9-35
             9.5    Goal 3: To estimate the exposures of the preschool children to these
                    Pollutants that they may encounter in their everyday environments . . 9-40
             9.6    Goal 4: To apportion exposures among the inhalation, dietary
                    ingestion, and indirect ingestion routes	9-70
   References 	R-l
Volume 2
   Appendix A      Summary of CTEPP Standard Operating Procedures (SOPs)   	  A-l
   Appendix B      CTEPP North Carolina and Ohio Field Study Recruitment Reports . . . B-l
   Appendix C      Summary of Analytical Methods for Determining Target Pollutants in
                    Multimedia Samples 	C-l
   Appendix D      Quality Assurance/Quality Control Summary for CTEPP North Carolina
                    and Ohio Data Collection  	  D-l
   Appendix E      EPA SAS Program for QA/QC  	E-l
   Appendix F      Median Indoor Air Sample Concentrations (ng/m3) in the NC and OH
                    Portions of the CTEPP study	F-l
   Appendix G      Algorithms for Estimating Daily Ingestion Rate of Dust and Soil in
                    Children Participants	  G-l
   Appendix H      Percentages of NC and OH Multimedia Samples with Pollutant Levels
                    At or Above the MQL 	  H-l
   Appendix I       Descriptive Statistics of CTEPP Pollutant/Metabolite Measurements in
                    NC Multimedia Samples  	 1-1
   Appendix J       Descriptive Statistics of CTEPP Pollutant/Metabolite Measurements in
                    OH Multimedia Samples	J-l
   Appendix K      Detailed Results of Statistical Analyses to Test for Significant Differences
                    in Multimedia Pollutant Measurements Between Selected Strata, by State
                    and Media Type	  K-l
   Appendix L      Descriptive Statistics of Potential Exposure Level and Potential
                    Absorbed Dose Estimates for Target Pollutants in Participating NC
                    Children	L-l
                                          IX

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Appendix M      Descriptive Statistics of Potential Exposure Level and Potential
                 Absorbed Dose Estimates for Target Pollutants in Participating OH
                 Children	M-l
Appendix N      Descriptive Statistics of Potential Exposure Level and Potential
                 Absorbed Dose Estimates for Target Pollutants in Participating NC
                 Adults	  N-l
Appendix O      Descriptive Statistics of Potential Exposure Level and Potential
                 Absorbed Dose Estimates for Target Pollutants in Participating OH
                 Adults	  O-l
Appendix P      Descriptive Statistics of Urinary Biomarker Concentrations for Target
                 Pollutants in NC Study Participants	P-l
Appendix Q      Descriptive Statistics of Urinary Biomarker Concentrations for Target
                 Pollutants in OH Study Participants  	  Q-l
Appendix R      Detailed Results of Statistical Analyses Performed on Potential
                 Exposure Level and Potential Absorbed Dose Estimates and on Urinary
                 Biomarker Concentrations for the Study Participants	R-l
Appendix S      Detailed Results of Statistical Analyses to Investigate the Apportioning
                 of Aggregated Potential Exposure Level and Aggregated Potential
                 Absorbed Dose Estimates for the Study Participants Across Exposure
                 Routes  	S-l
                                     Figures
                                                                               Pas
Figure 2.4.1      Estimated Median Aggregate Potential Exposures of NC and OH
                 Preschool Children to Eight Pollutants in Their Everyday
                 Environments	2-11
Figure 2.4.2      Estimated Median Aggregate Potential Doses of NC and OH Preschool
                 Children to Eight Pollutants in Their Everyday Environments	2-13
Figure 2.5.1      Estimated Mean Proportion of Aggregate Potential Exposure and
                 Potential Absorbed Dose for NC Children by Exposure Route	2-16
Figure 2.5.2      Estimated Mean Proportion of Aggregate Potential Exposure and
                 Potential Absorbed Dose for OH Children by Exposure Route	2-17
Figure 4.1.1      CTEPP Overall Sampling Design 	4-2
Figure 4.1.2      Six Counties in North Carolina (A) and Ohio (B) Selected by Stratified
                 Random Sampling	4-3
Figure 4.2.1      Procedures for Recruiting Day Care Center Component	4-5
Figure 4.2.2      Procedures for Recruiting Telephone Sample Component	4-8
Figure 9.3.1      Boxplots  of Pollutant Concentrations in Indoor Air and Outdoor Air
                 Samples Collected at the Homes and Day Care Centers of
                 Participating NC and OH Children, for Eight Pollutants	9-20
Figure 9.3.2      Boxplots  of Pollutant Concentrations in Dust and Soil Samples
                 Collected at the Homes and Day Care Centers  of Participating

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                 NC and OH Children, for Eight Pollutants  	9-21
Figure 9.3.3      Boxplots of Pollutant Loadings in Dust, Hard Floor Surface Wipe,
                 Food Preparation Surface Wipe, Transferable Residues, and Children
                 and Adult Dermal Wipe Samples Collected at the Homes and Day Care
                 Centers of Participating NC Children, for Eight Pollutants	9-22
Figure 9.3.4      Boxplots of Pollutant Loadings in Dust, Hard Floor Surface Wipe,
                 Food Preparation Surface Wipe, Transferable Residues, and Children
                 and Adult Dermal Wipe Samples Collected at the Homes and Day Care
                 Centers of Participating OH Children, for Eight Pollutants	9-23
Figure 9.3.5      Boxplots of Pollutant Concentrations in Solid Food Samples
                 Collected from Participating NC and OH Children and Adults,
                 for Eight Pollutants  	9-24
Figure 9.5.1      Boxplots of Estimated Potential Exposure and Potential Absorbed
                 Dose via Inhalation for Participating NC and OH Children, for Eight
                 Pollutants	9-47
Figure 9.5.2      Boxplots of Estimated Potential Exposure and Potential Absorbed
                 Dose via Dietary Ingestion for Participating NC and OH Children,
                 for Eight Pollutants  	9-48
Figure 9.5.3      Boxplots of Estimated Potential Exposure and Potential Absorbed
                 Dose via Indirect Ingestion for Participating NC and OH Children,
                 for Eight Pollutants  	9-49
Figure 9.5.4      Boxplots of Estimated Potential Exposure and Potential Absorbed
                 Dose via Inhalation for Participating NC and OH Adults, for Eight
                 Pollutants	9-50
Figure 9.5.5      Boxplots of Estimated Potential Exposure and Potential Absorbed
                 Dose via Dietary Ingestion for Participating NC and OH Adults, for
                 Eight Pollutants Measured in Adult Food	9-51
Figure 9.5.6      Boxplots of Estimated Potential Exposure and Potential Absorbed
                 Dose via Indirect Ingestion for Participating NC and OH Adults, for
                 Eight Pollutants  	9-52
Figure 9.5.7      Boxplots of Estimated Aggregate Potential Exposure and Aggregate
                 Potential Absorbed Dose for Participating NC and OH Children, for
                 Eight Pollutants  	9-56
Figure 9.5.8      Boxplots of Estimated Aggregate Potential Exposure and Aggregate
                 Potential Absorbed Dose for Participating NC and OH Adults, for
                 Eight Pollutants  	9-57
Figure 9.5.9      Boxplots of Urinary Biomarker Concentrations for Participating
                 NC and OH Children and Adults, for Eight Pollutants	9-61
                                        XI

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                                     Tables
Table 2.2.1       Median Concentrations of Frequently Detected Pollutants in
                 Environmental and Personal Media at the Homes and Day Care
                 Centers of Preschool Children in NC and OH	  2-3
Table 2.2.2       Median Concentrations of Pollutants That Were Measurable in Surface
                 Samples That Were Collected After Recent Pesticide Applications at
                 Homes in NC and OH	2-5
Table 2.5.1       The Relative Importance of the NC and OH Children's Exposures to
                 the Eight Pollutants Through the Inhalation, Dietary Ingestion, and
                 Indirect Ingestion Routes of Exposure	2-18
Table 4.3.1       Summary of CTEPP North Carolina Response Rates	4-10
Table 4.3.2       Summary of CTEPP North Carolina Participant Characteristics  .... 4-11
Table 4.3.3       Summary of CTEPP Ohio Participant Response Rates	4-13
Table 4.3.4       Summary of CTEPP Ohio Participant Characteristics  	4-14
Table 5.2.1       Summary of Field Data Collection Procedures and Sampling Activities
                 over a 48-h Period at a Participant's Home and/or Day Care Center  . . 5-3
Table 5.2.2       Types of Questionnaires, Diaries, or Menus Collected from
                 Participants	5-7
Table 5.3.1       Summary of the Completeness of the NC Sample Collection	5-11
Table 5.3.2       Summary of the Completeness of the NC Questionnaire/Diary
                 Collection	5-12
Table 5.3.3       Summary of the Completeness of the OH Sample Collection	5-13
Table 5.3.4       Summary of the Completeness of the OH Questionnaire/Diary
                 Collection	5-14
Table 6.1.1       Neutral Target Pollutants for the CTEPP Study  	6-2
Table 6.1.2       Acidic Target Pollutants and Metabolites for the CTEPP Study	6-3
Table 6.1.3       Target Pollutants and Metabolites Measured in the CTEPP Urine
                 Samples  	6-3
Table 6.2.1       Surrogate Recovery Standards and Internal Standards for Chemical
                 Analysis	6-5
Table 6.2.2       Summary of Sample Extraction Methods 	6-6
Table 6.2.3       Summary of GC/MS Operating Conditions	6-9
Table 6.2.4       Results for Duplicate Samples for Neutral Pollutants - North Carolina 6-13
Table 6.2.5       Results for Duplicate Samples for Acidic Pollutants/Metabolites -
                 North Carolina	6-14
Table 6.2.6       Results for Duplicate Samples for Urine Analysis - North Carolina .  . 6-14
Table 6.2.7       Results for Duplicate Analyses of the Same Sample Extract for
                 Neutral Pollutants - North Carolina	6-15
Table 6.2.8       Results for Duplicate Analyses of the Same Sample Extract for Acidic
                 Pollutants/Metabolites - North Carolina  	6-17
Table 6.2.9       Results for Duplicate Analyses of the Same Sample Extract for Urine -
                 North Carolina	6-17
                                       Xll

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Table 6.2.10      Results for Matrix Spike Samples for Neutral Pollutants - North
                 Carolina	6-18
Table 6.2.11      Results for Matrix Spike Samples for Acidic Pollutants/Metabolites -
                 North Carolina	6-20
Table 6.2.12      Results for Matrix Spike Samples for Urine Analysis - North
                 Carolina	6-20
Table 6.2.13      Results for Surrogate Recovery Standards for Neutral Pollutants -
                 North Carolina	6-21
Table 6.2.14      Results for Surrogate Recovery Standards for Acidic Pollutants -
                 North Carolina	6-21
Table 6.2.15      Results for Surrogate Recovery Standards for Urine Analysis -
                 North Carolina	6-22
Table 6.2.16      Results for Blank Samples Having Detectable Neutral Pollutants -
                 North Carolina	6-22
Table 6.2.17      Results for Blank Samples Having Detectable Acidic
                 Pollutants/Metabolites - North Carolina 	6-23
Table 6.2.18      Results for Water Samples - North Carolina	6-23
Table 6.2.19      Results for Duplicate Samples for Neutral Pollutants - Ohio 	6-25
Table 6.2.20      Results for Duplicate Samples for Acidic Pollutants/Metabolites -
                 Ohio	6-26
Table 6.2.21      Results for Duplicate Samples for Urine Analysis - Ohio	6-26
Table 6.2.22      Results for Duplicate Analyses of the Same Sample Extract for
                 Neutral Pollutants - Ohio	6-27
Table 6.2.23      Results for Duplicate Analyses of the Same Sample Extract for
                 Acidic Pollutants/Metabolites - Ohio  	6-29
Table 6.2.24      Results of Duplicate Analyses of the Same Sample Extract for Urine -
                 Ohio	6-29
Table 6.2.25      Results for Matrix Spike Samples for Neutral Pollutants - Ohio  ....  6-30
Table 6.2.26      Results for Matrix Spike Samples for Acidic Pollutants/Metabolites -
                 Ohio	6-32
Table 6.2.27      Results for Matrix Spike for Urine Analysis - Ohio  	6-32
Table 6.2.28      Results for Surrogate Recovery Standards for Neutral Pollutants -
                 Ohio	6-33
Table 6.2.29      Results for Surrogate Recovery Standards for Acidic Pollutants -
                 Ohio	6-33
Table 6.2.30      Results for Surrogate Recovery Standards for Urine Analysis - Ohio  6-33
Table 6.2.31      Results for Blank Samples with Detectable Neutral Pollutants - Ohio  6-34
Table 6.2.32      Results for Blank Samples with Detectable Acidic Pollutants/
                 Metabolites - Ohio	6-35
Table 6.2.33      Results for Blank Samples with Detectable Urine Pollutants - Ohio  .  6-35
Table 6.2.34      Results of Analysis of Water Samples - Ohio	6-36
Table 8.3.1       Number of Study Participants in Each Stratum, by State 	8-9
Table 8.4.1       Pollutants Considered for Estimating Potential Exposure and Potential
                 Absorbed Dose for Study Participants in a Given State  	8-11
                                       Xlll

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Table 9.2.1      Median MDL Values for Neutral Pollutants Measured in Multimedia
                Samples from North Carolina and Ohio 	9-3
Table 9.2.2      Median MDL Values for Acidic Pollutants and Metabolites Measured
                in Multimedia Samples from North Carolina and Ohio	9-4
Table 9.2.3      Median MDL Values for Pollutants and Metabolites Measured in Urine
                Samples from North Carolina and Ohio 	9-4
Table 9.2.4      Percentages of NC Samples With Detectable Pollutant and Metabolite
                Levels (At or Above the MDL) in Multimedia and Urine Samples .  . . 9-5
Table 9.2.5      Percentages of OH Samples With Detectable Pollutant and Metabolite
                Levels (At or Above the MDL) in Multimedia and Urine Samples .  . . 9-7
Table 9.2.6      Percentages of NC and OH Samples With Detectable Pollutant and
                Metabolite Levels (At or Above the MDL) in Surface Samples	9-9
Table 9.2.7      Pollutants Were Classified Into Three Groups, Separately for Each
                State, Based On Their Level of Detection in the Multimedia Samples 9-13
Table 9.3.1      Median Levels of 27 Target Pollutants in NC Multimedia Samples
                Collected from Home Environments	9-16
Table 9.3.2      Median Levels of 27 Target Pollutants in NC Multimedia Samples
                Collected from Day Care Center Environments  	9-17
Table 9.3.3      Median Levels of 26 Target Pollutants in OH Multimedia Samples
                Collected from Home Environments	9-18
Table 9.3.4      Median Levels of 26 Target Pollutants in OH Multimedia Samples
                Collected from Day Care Center Environments  	9-19
Table 9.3.5      Environmental and Food Samples:  Estimated Ratios of Geometric Mean
                Pollutant Levels Between Urban and Rural, Low-Income and Middle/
                High-Income, and Home and Day Care Environments, When These
                Ratios Were Significantly Different from One at the 0.05 Level .... 9-27
Table 9.3.6      Dermal Wipe Samples: Estimated Ratios of Geometric Mean Pollutant
                Levels Between Urban and Rural, Low-Income  and Middle/High-Income,
                and Home and Day Care  Environments, When These Ratios Were
                Significantly Different from One at the 0.05 Level	9-31
Table 9.4.1      Summary of Selected Physical Characteristics of the Participating
                Children and Their Primary Caregivers, for NC  and OH 	9-36
Table 9.4.2      Prevalence of Selected Daily Activities Among  the Participating
                Children, as Recorded on Study Questionnaires	9-38
Table 9.4.3      Daily Percentage of Time that Participating Children Spent Indoors or
                Outdoors at Homes, Day Care Centers, or Other Places	9-40
Table 9.4.4      Daily Percentage of Time that Participating Adults Spent Indoors or
                Outdoors at Homes or Other Places	9-40
Table 9.4.5      Summary Statistics on the Daily Amount of Solid and Liquid Food
                Collected from Participating Children and Their Primary Caregivers,
                According to Location From Which Samples Were Taken	9-41
Table 9.5.1      Median Values of Estimated Potential Exposure and Potential Absorbed
                Dose for Target Pollutants in Participating NC Preschool Children, by
                Exposure Route  	9-43
                                      XIV

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Table 9.5.2       Median Values of Estimated Potential Exposure and Potential Absorbed
                 Dose for Target Pollutants in Participating OH Preschool Children, by
                 Exposure Route 	9-44
Table 9.5.3       Median Values of Estimated Potential Exposure and Potential Absorbed
                 Dose for Target Pollutants in Participating NC Adults, by Exposure
                 Route 	9-45
Table 9.5.4       Median Values of Estimated Potential Exposure and Potential Absorbed
                 Dose for Target Pollutants in Participating OH Adults, by Exposure
                 Route 	9-46
Table 9.5.5       Summary of Aggregate Potential Exposure and Aggregate Potential
                 Absorbed Dose Estimates for Eight Pollutants in NC Study
                 Participants  	9-54
Table 9.5.6       Summary of Aggregate Potential Exposure and Aggregate Potential
                 Absorbed Dose Estimates for Eight Pollutants in OH Study
                 Participants	9-55
Table 9.5.7       Summary of Unadjusted Biomarker Concentrations (ng/mL) for Three
                 Pollutants and Metabolites Measured in the Urine of Participating NC
                 Children	9-59
Table 9.5.8       Summary of Unadjusted Biomarker Concentrations (ng/mL) for Three
                 Pollutants and Metabolites Measured in the Urine of Participating OH
                 Children	9-60
Table 9.5.9       Estimated Ratios Between Selected Strata of Geometric Mean Potential
                 Exposure and Potential Absorbed Dose Estimates in Participating NC
                 and OH Children, When These Ratios Were Significantly Different
                 from One at the 0.05 Level  	     9-63
Table 9.6.1       Estimated Mean Proportion of Aggregate Potential Exposure Level
                 and Potential Absorbed Dose in Participating NC and OH Children
                 That is Attributable to Each Exposure Route,  Calculated Across All
                 Children	9-72
Table 9.6.2       Estimated Mean Proportion of Aggregate Potential Exposure Level
                 and Potential Absorbed Dose in NC Children That is Attributable to
                 Each Exposure Route, Calculated by Stratum, When Differences
                 Between Pairs of Strata Were Significant at the 0.05 Level  	9-73
Table 9.6.3       Estimated Mean Proportion of Aggregate Potential Exposure Level
                 and Potential Absorbed Dose in OH Children That is Attributable to
                 Each Exposure Route, Calculated by Stratum, When Differences
                 Between Pairs of Strata Were Significant at the 0.05 Level  	9-74
Table 9.6.4       Estimated Mean Proportion of Aggregate Potential Exposure Level
                 and Potential Absorbed Dose in Participating NC and OH Adults
                 That is Attributable to Each Exposure Route,  Calculated Across
                 All Adults	9-75
Table 9.6.5       Estimated Ratios Between Two Exposure Routes of Geometric  Mean
                 Potential Exposure Level and Potential Absorbed Dose Estimates in
                                       XV

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                 Participating NC Children, When These Ratios Were Significantly
                 Different From One at the 0.05 Level	9-78
Table 9.6.6       Estimated Ratios Between Two Exposure Routes of Geometric Mean
                 Potential Exposure Level and Potential Absorbed Dose Estimates in
                 Participating OH Children, When These Ratios Were Significantly
                 Different From One at the 0.05 Level	9-79
Table 9.6.7       Estimated Ratios Between Two Exposure Routes of Geometric Mean
                 Potential Exposure Level and Potential Absorbed Dose Estimates in
                 Participating NC Adults, When These Ratios Were Significantly
                 Different From One at the 0.05 Level	9-80
Table 9.6.8       Estimated Ratios Between Two Exposure Routes of Geometric Mean
                 Potential Exposure Level and Potential Absorbed Dose Estimates in
                 Participating OH Adults, When These Ratios Were Significantly
                 Different From One at the 0.05 Level	9-80
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                                 Acknowledgments
       In a large study such as CTEPP, many people contribute to its success. The CTEPP study
was conceptualized by EPA's National Exposure Research Laboratory (NERL) on the basis of
three small studies of preschool children's exposures conducted earlier by NERL.  NERL staff,
with support from Battelle, developed the study design.  Battelle performed the recruitment, field
sampling, sample analysis, and statistical and data analysis of the two (NC and OH) field
exposure studies.

       We would especially like to thank the following EPA staff members for their valuable
contributions during the study: E. Streib, G. Robertson, K. Thomas, R. Fortmann, E. Betz, C.
Stevens, P. Jones, H. Ozkaynak, and G. Evans.

       We would like also like to thank the Battelle field team, recruitment team, and laboratory
team members for their support and contributions to this study: C. Aselage, S. Benny, T.
Branch, L. Bryan, M. Chapman, C. Dagnino, L. Dibiase, S. Hubbard, L. Lantz, J. McConnell, F.
Patterson, J.  Sabula, C. Tucker, L. Wilson, K. Bradley, T. Brogdon, R. Chaffin, D. Conley, R.
Cunningham, K. Esser, B. Follosco, L. Griffin, M. Hankins, L. Harris, S. Harrison, T. Hawley,
E. Hill, V. Hoskins, E. Howard, R. Huggins, N. Humphreys,  S. Jeter, K. Juan, V. Macrae, B.
Marsh, A.  Miller, M. Millsap, A..Moore, V. Mulcare, D. Neesz, L. Beiter, T. Rhodes, M.
Sanders, V. Tarascio, K. Taylor, A. Thorpe, S. Thrower, K. Umstead, L. White, D. Davis, M.
McCauley, J. Satola, J. Sowry, E. Weller, P. Tefft, D. Magbag, and G. McDevitt.
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                                 Executive Summary
       The Children's Total Exposure to Persistent Pesticides and Other Persistent Organic
Pollutants (CTEPP) study is one of the largest aggregate exposure studies of preschool children
(i.e., 2 to 5 years of age) performed in the United States. These young children are suspected of
having greater exposures to pesticides and other pollutants in their everyday environments
compared to older children and adults. These greater exposures may result from what preschool
children drink or eat, where they spend their time, and what they do in these locations.  The
primary goals of this landmark study were:

       1.      to measure the concentration of chemical pollutants in multimedia samples
              collected at the homes and day care centers of preschool children,
       2.      to determine the distribution of child characteristics, activities, and locations that
              contributed to their exposures,
       3.      to estimate the aggregate exposures to the pollutants they may come in contact
              with in their everyday environments, and
       4.      to evaluate the contribution of each route of exposure.

This report presents the results of statistical analyses conducted to address these primary study
goals. Data analysis will continue over the next year to more fully characterize those factors that
are responsible for preschool children's exposure and to evaluate the relationship between
environmental concentrations, exposure factors, and biomarkers of exposure. The entire CTEPP
study database will be made available to  scientists in EPA program and regional offices, to
researchers in industry and academia, and to the general public to allow the data to be used in
additional analysis, as input to exposure models, and in developing risk assessments for
preschool children.

       The CTEPP study was conducted in six counties in North Carolina (NC) and  six counties
in Ohio (OH). These two states were selected to provide exposure information in two different
geographical  regions of the United States (i.e., the Southeast and Midwest).  Overall, 257
preschool children and their adult caregivers took part in the study. Participants were recruited
from eligible  homes and child day care centers in the twelve counties. Participants were selected
from several categories to allow for comparisons between home vs. day care settings, urban vs.
rural locations, and low income vs. middle/high income environments. Although, the study
focused on preschool children, information was also collected on the adult caregivers for
comparison purposes. The results presented in this report apply only to the study participants;
they have not been generalized to preschool children living in either state or to children in
general.

       Monitoring was performed over a 48-h period at the children's homes and/or day care
centers. Environmental (air,  dust,  and soil) and personal (hand wipe, diet, water, and urine)
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samples were collected.  Surface wipe samples were collected from homes with recent pesticide
applications. Questionnaires and diaries were used to collect information on housing
characteristics, products used in the home, and activities of the participants. Multimedia samples
were analyzed for over 50 pollutants belonging to such classes as the organophosphate (OP)
pesticides, OP metabolites, organochlorine (OC) pesticides, pyrethroid pesticides, pyrethroid
metabolites, acid herbicides, polycyclic aromatic hydrocarbons (PAHs), PAH metabolites,
phthalates, phenols, and the polychlorinated biphenyls (PCBs).  These pollutants were selected
because they have been commonly detected in  indoor and outdoor environments and/or because
they are potentially carcinogenic, mutagenic, or endocrine-disrupting chemicals in humans.

       Results of the study showed there were low levels of many pollutants in both the homes
and day care centers where preschool children  spend their time.  Children can become exposed
to these pollutants when they breathe the  air, ingest food and water, ingest soil and dust, and
touch contaminated surfaces.  An absorbed dose occurs when pollutants are taken into the body
though such routes as the lungs, intestines, and skin. Exposure and absorption into the body has
been confirmed by measuring the same pollutants or metabolites of these pollutants in urine
samples collected from children in the study.

       The most frequently detected pollutants in environmental media were those commonly
used in the home, those found in products used throughout the home, or those formed as a result
of common processes. These pollutants included chlorpyrifos, diazinon, cis- and
trans-permethrin, alpha- and gamma-cUordane, and pentachlorophenol, which are pesticides
used in households. CTEPP was the first study to measure the metabolites of chlorpyrifos
(3,5,6-trichloro-2-pyridinol [TCP]) and diazinon (2-isopropyl-6-methyl-4-pyrimidinol [IMP]) in
environmental samples. These two compounds were detected at a very high rate in most sample
types. Benzybutylphthalate, di-w-butylphthalate, and bisphenol-A, are commonly used
plasticizers that were frequently detected. The PAHs were also frequently detected in most
environmental samples. PAHs are formed during processes which involve burning of specific
substances, with indoor sources including smoking and cooking, and outdoor sources  including
motor vehicles,  incinerators, fires, and power plants. Target pollutants were detected most often
in dust and indoor air samples.  Only the PAHs were detected at a high rate in soil samples.
Very few pollutants were detected in liquid food samples.

       Median values of measured concentrations for selected pollutants are shown in Table ES-
1 by state. The  highest concentrations in  most  samples were found for the two phthalates,
benzylbutylphthalate and di-w-butylphthalate.  For the other pollutants, concentration rankings
depended upon the media and the properties of the chemicals.
                                           XIX

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Table ES-1.  Median Concentrations of Selected Pollutants Measured in Multiple Media.
Pollutants/Metabolite
Chlorpyrifos
3,5,6-TCP
cw-Permethrin
/r
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       For 27 target pollutants, information on environmental and personal sample
concentrations was combined with activity data to estimate potential exposure (ng/day) for each
study participant by the inhalation, dietary ingestion, and indirect ingestion exposure routes. For
each of these three exposure routes, potential absorbed dose (ng/kg/day) was also calculated by
assuming a 50% absorption rate and dividing potential exposure by body weight. Results through
the dermal route were not reported due to uncertainties in the assumptions required for the
calculations. However, absorbed doses of these pollutants through the dermal route of exposure
were assumed to be low.

       For eight of the target pollutants (chlorpyrifos, diazinon, 3,5,6-TCP, c/s-permethrin,
frYms-permethrin, 2,4-D, di-w-butylphthalate, and bisphenol-A), aggregate potential exposure and
absorbed dose estimates were calculated by summing over all three routes. In both states,
aggregate exposure and dose estimates were highest for di-w-butylphthalate, bisphenol-A, and
3,5,6-TCP. The NC and OH children had the highest median aggregate potential exposure levels
to di-w-butylphthalate (42,900 and 8,310 ng/day), bisphenol-A (2,560 and  1,880 ng/day), and
3,5,6-TCP (1,230 and 930 ng/day).  Median aggregate potential absorbed dose was highest
among the NC and OH children for these same three pollutants (1,250 and 262 ng/kg/day for
di-w-butylphthalate, 71.4 and 60.8 ng/kg/day for bisphenol-A, and 37.7 and 25.4 ng/kg/day for
3,5,6-TCP for NC and OH children, respectively).  The median aggregate potential absorbed
doses of di-w-butylphthalate was over four times greater in NC  children compared to OH
children. For di-w-butylphthalate, bisphenol-A, and 3,5,6-TCP, the relative importance of the
exposure routes was dietary ingestion, followed by inhalation and indirect ingestion. In addition
in both states, the children had the highest estimated aggregate  exposures and absorbed doses to
di-w-butylphthalate.

       In several cases, there were significant  differences in the calculated exposure and dose
estimates between different groups of children. Those differences for which the geometric mean
estimate was at least three times higher (when rounded) in one category than another included
the following:

•      Day Care vs. Stay-at-Home Children.  In OH, exposure and dose estimates for diazinon,
       the PAHs, and benzylbutylphthalate via the indirect ingestion route were higher for day
       care children than stay-at-home children. Likewise,  dietary exposure and dose estimates
       for benzylbutylphthalate and the permethrins were higher for the same group of children.

•      Urban vs. Rural Children.  In NC, exposure and dose estimates for 2,4-D by the indirect
       ingestion route were higher for children in urban compared to rural locations. In OH,
       PAHs showed higher estimates via the indirect ingestion route for urban children.

•      Low Income vs. Middle/High Income Children.  In  NC, exposure and dose estimates for
       2,4-D via the indirect ingestion route were higher for children in middle/high-income
       compared to low-income environments.
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Because the indirect ingestion route was most frequently associated with sizable (and
statistically significant) differences in exposure and dose estimates between groups of children,
but yet accounted for a relatively small amount of the total or aggregate exposure for each child,
it is not surprising that similar differences were not observed for aggregate exposure.

       Some pollutants or metabolites were frequently detected and measurable in the children's
urine samples, including 3,5,6-TCP, 2,4-D, and pentachlorophenol. Median urinary
concentrations of 3,5,6-TCP, 2,4-D, and pentachlorophenol were 5.3, 0.7, and 0.4 ng/mL,
respectively, for NC children. For OH children, median urinary concentrations of 3,5,6-TCP,
2,4-D, and pentachlorophenol were 5.1,  1.0, and 0.8 ng/mL, respectively.  On average, levels of
3,5,6-TCP in urine samples for both NC and OH children were at least five times greater than
those for 2,4-D or pentachlorophenol. As with estimates of aggregate potential exposure and
absorbed dose, there were no incidences where differences in urinary concentrations were  highly
significant between various groups of children.

       Finally, comparisons between children and their adult caregivers showed that children
were generally exposed to higher levels of pollutants than adults in the same household, with the
difference being statistically significant. Much of these differences was likely attributable to
differences in physiological factors (i.e., ventilation rates and body weights) and activity patterns
(i.e., daily soil and dust ingestion rates) between children and adults.
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                                      Chapter 1
                                     Introduction
1.1    Background

       Young children, especially those of preschool age, are hypothesized to have greater
exposures than do older children or adults to pesticides and semivolatile organic pollutants,
including some compounds that may have endocrine-disrupting effects or developmental
toxicity. These greater exposures may result from what children eat and drink, where they spend
their time, and what they do there. The impact of the exposures may be greater on young
children because of their smaller body masses, immature body systems, and rapid physical
development.

       Organochlorine (OC) and organophosphate (OP) pesticides, pyrethroid pesticides, acid
herbicides, polycyclic aromatic hydrocarbons (PAHs), phthalates, phenols, and polychlorinated
biphenyls (PCBs), are pollutants commonly found in multiple environmental media.  Many of
these compounds are  persistent in the indoor and outdoor environments.  Some have been shown
to have deleterious effects on health, exhibiting not only acute toxicity, but also possible chronic
effects at low levels.  Many are sufficiently volatile or soluble to evaporate and condense, or to
move otherwise through environmental media - air, water, and soil.  They can enter indoor
microenvironments through intrusion of outdoor air,  inadvertent transport by people or pets, and
other means (1-4).  Additionally, there are many potential sources of these pollutants indoors,
such as pesticides, home chemicals, environmental tobacco smoke, consumer products, and
building materials.

       With the passage of the Food Quality and Protection Act of 1996 (FQPA), new, more
stringent standards for pesticide residues in foods were set, to provide increased emphasis on
health protection for infants and children. The exposure component of the risk assessment for
pesticides is now required to

             Consider the potentially greater susceptibility of children to pesticide exposure,
             compared to adults, and

             Account for aggregate exposures to the pesticides from all  sources, including
             food, drinking water, and non-occupational applications of the pesticides in
             homes, schools, day care centers, and other microenvironments.

       Essentially, the FQPA states that exposure assessments must be conducted for infants and
children and that these exposure assessments must include and be  reliable for all sources of
pesticide exposure. Because young children learn about their environment by exploring not only
the appearance and texture of objects,  but also their taste and smell, both dietary and indirect

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ingestion can play an important role in their exposures. However, very little information on
children's aggregate exposures is available at the present time, and the dominant pathways and
media through which such exposures may take place are known uncertainly. The Children's
Total Exposure to Persistent Pesticides and Other Persistent Organic Pollutants (CTEPP) study
provides some of this information.

       In our previous work, methods to measure and estimate the exposures of preschool
children in low-income families to PAHs were developed and evaluated (5,6).  Preschool
children's aggregate exposures to PAHs through three exposure routes including inhalation,
dietary and indirect ingestion were estimated for 24 children (7).  Further studies of an extensive
suite of pollutants including OP and OC pesticides, acid herbicides, PAHs, phthalates, phenols,
and PCBs concentrations in multiple media at nine child day care centers and of the aggregate
exposures of nine preschool children to these pollutants were conducted (8-10). Results from
these studies suggested that dietary and indirect ingestion could be important contributors to
children's exposures. In addition, the children's potential absorbed doses resulting from their
exposures could exceed those of adults living in the same households. This background work,
along with the new requirements of the FQPA, led  to the conceptualization, development, and
realization of the CTEPP study.

1.2    Study Overview

       The CTEPP study provides data on aggregate exposures of 257 children to pesticides and
other persistent and non-persistent organic pollutants in several microenvironments, and has
improved the methods for determining their exposures and the routes of exposure. The study
results also allow identification of important hypotheses to be tested in future research. The
following  four major, specific goals were established for the CTEPP study:

1.      To measure the environmental concentrations of pesticides and other persistent and non-
       persistent organic pollutants in multiple media  at the homes  and day care  centers of 257
       preschool children in six North Carolina and six Ohio counties,

2.      To determine the distributions of child characteristics, activities, and locations that
       contributed to these children's exposures to the selected pollutants,

3.      To estimate the exposures of the preschool  children to these pollutants that they may
       encounter in their everyday environments, and

4.      To apportion the exposures through the ingestion, inhalation, and dermal routes.

In meeting these goals, the following seven hypotheses were tested in the study:

1.      Exposures of children to the target pollutants are similar at home and at day care.
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2.     Exposures of children to the target pollutants are similar for low-income households
       compared to those in other households.

3.     Exposures of children to the target pollutants are similar for urban and rural households.

4.     Routes of exposure and their relative importance are different for the different chemical
       classes of pesticides and other persistent and non-persistent organic pollutants.

5.     Ingestion is a major route of exposure of the selected children and adults living in the
       same household.

6.     Diet is a major contributor to children's ingestion exposures.

7.     Children's exposures to the target pollutants (and the potential absorbed doses resulting
       therefrom) are significantly greater than those of adults living in the same household.

       CTEPP investigated the exposures of 257 preschool children  and their adult care givers
to a large number of persistent and non-persistent organic pollutants  in their everyday
surroundings.  These exposures, through the dietary and indirect ingestion, inhalation, and
dermal absorption routes, were measured in the participants' homes and child day care
environments, in non-occupational settings.  The target compounds include OP pesticides and
metabolites, OC pesticides, pyrethroid pesticides and a metabolite, acid herbicides, PAHs,
phthalates, phenols, PCBs, PAH metabolites, and atrazine. The specific compounds were
selected because they may be carcinogenic, mutagenic, acutely or chronically toxic, or possibly
disruptive to the human endocrine system, and because they are commonly found in both indoor
and outdoor environments.

       To minimize selection bias, a population-based, multistaged stratified random sampling
plan was devised for the CTEPP study (11).  The target population for CTEPP was children
between the ages of 18  months and five years. The study consisted of two separate field studies,
one conducted in North Carolina (NC) and the other in Ohio (OH). Within each state, four urban
and two rural counties were selected randomly according to population, distributed among three
distinct geographical regions of each state to ensure a broad range  of likely exposures. These
regions were the mountains, the Piedmont, and the coastal plain of NC, and northern, central,
and southern regions of OH. Two sampling frames, (1) the telephone component (households
containing children who do not attend day care) and (2) the day care  component (households
containing children attending day care centers) were constructed within each state. For the
telephone  component, a list-assisted, random digit dialing telephone  sampling in the selected
counties was used. The calculated response rate for the telephone  sample was 58% in NC and
57% in OH. For the day care component, 13  centers in the six chosen NC counties and 16
centers in  the six chosen OH counties were recruited.  Children were then selected randomly
from classrooms having children in the eligible age group of two to five years, and their
participation was recruited through their parents. The calculated response rates in NC were 53%
for day care centers and 50% for day care parents. In OH, the response rates were  57% for OH
                                           1-3

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day care centers and 31% for OH day care parents.  For ease of discussion, the participants from
the telephone component are referred to as stay-at-home participants (children) and the
participants from the day care component are referred to as day care participants (children)
throughout the report

       In NC, children and their caregivers in 130 households participated in the study, while in
OH, 127 households participated.  Approximately half of the children in each state attended day
care centers (63 in NC and 58 in OH). About 84% of the NC participants and 87% of the OH
participants lived in urban locations.  Low-income households, classified according to federal
guidelines for the  Women, Infants, and Children (WIC) program (185% of the federal poverty
level), comprised 46% of the sampled households in NC and 38% of those in OH.

       Fifty Standard Operating Procedures (SOPs) were prepared for the CTEPP study,
covering subject recruitment, field sampling, storing and shipping of samples, administering
questionnaires, data processing, and laboratory procedures.  All field activities, laboratory
operations, and data handling were performed following these SOPs. The list of the CTEPP
SOPs is given in Appendix A.

       More than 5,000 discrete personal and environmental samples, including quality control
samples, were collected in each state (NC and OH) and analyzed. Additionally, house/building
characteristics observation surveys, pre- and post-monitoring questionnaires, day care food
menus, and detailed child/adult time-activity and food diaries provided ancillary information
necessary to estimate aggregate exposures and to aid in interpretation of the  CTEPP data.

       Field sampling for the participants from the day care component took place over a 48-h
period at each participating child's day care center and simultaneously at his/her home. Field
sampling for the participants from the telephone survey component took place over a 48-h period
at each participant's home. Environmental and personal samples were collected at the
participants homes and/or day care centers:

•      to identify the sources of exposures in the participants' environments,
•      to determine the important routes of exposure (inhalation, ingestion,  and dermal
       absorption) and,
•      to allow estimation of potential exposure and potential absorbed dose through multiple
       sample media

       The environmental samples collected in this study included indoor and outdoor air,
outdoor play area  soil, and indoor floor (carpet) dust, or if no carpet, hard floor surface wipes.  If
a pesticide had been applied in the home or day care center in the seven days prior to sampling,
transferable residues, hard floor surface wipes, and food preparation surface wipes were also
collected.  Personal samples collected in this study included drinking water,  duplicates of all
food and beverages that the participants ate or drank during the 48-h sampling period, hand
wipes, and urine.  In addition, approximately 10% of the children (26) in OH were videotaped
for about 2 h at their homes.  Note that the videotaped data are not presented in this report.
                                           1-4

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       The collected field samples and field and laboratory quality control samples were
extracted, then analyzed by gas chromatography/mass spectrometry for over 50 target
compounds1. These compounds included the following:

       two OP pesticides: chlorpyrifos and diazinon;
•      two OP metabolites: 2-isopropyl-6-methyl-4-pyrimidinol (IMP) and 3,5,6-trichloro-2-
       pyridinol (3,5,6-TCP);
•      ten OC pesticides: aldrin, a^/za-chlordane, gamma-chlordane, p.p '-DDE, p,p '-DDT,
       dieldrin, endrin, heptachlor, lindane, and pentachloronitrobenzene;
•      three pyrethroid pesticides: cyfluthrin and cis- and ^rara'-permethrin;
       one pyrethroid metabolite: 3-phenoxybenzoic acid (3-PBA);
       three acid herbicides: dicamba, 2,4-D, and 2,4,5-T;
       nine PAHs: benz[a]anthracene (BaA), benzo[a]pyrene (BaP), benzo[&]fluoranthene,
       benzo[e]pyrene, benzo[g/7/]perylene, benzo[£]fluoranthene, chrysene,
       dibenz[a,/z]anthracene, and indeno[l,2,3-c
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95th). The distributions of participant characteristics, activities, and locations that are important
for exposure were quantified, based on the questionnaire data. Potential exposures and potential
absorbed doses were estimated for selected target compounds, based on the percentage of
samples that had detectable levels of these compounds, the measured concentrations, the
participants' activity patterns, and assumed physiological parameters.  Statistical analyses were
performed on log-transformed data, using analysis of variance (ANOVA) models. The data
summaries presented in this report represent only the children and their primary caregivers in NC
and OH who participated in this study.

       This report summarizes the recruitment, field sampling, chemical analyses, data analyses,
and the study findings for both the NC and OH field studies.
                                            1-6

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                                      Chapter 2
                                     Conclusions
2.1    Overview
       The CTEPP study examined the aggregate exposures of 257 preschool children to
pollutants commonly found in their everyday environments. This study was conducted in six
counties each in North Carolina (NC) and Ohio (OH) which are in two different geographical
locations - the Southeast and the Midwest - of the United States. The overall goals of this study
were (1) to measure the concentrations of the target pollutants in multimedia samples collected at
the homes and at day care centers of 257 preschool children in six NC counties and six OH
counties, (2) to determine the distributions of child characteristics, activities, and locations that
contributed to their exposures, (3) to estimate the aggregate exposures of the preschool children
to these pollutants that they may encounter in their everyday environments, and (4) to apportion
the routes of exposure.  Participants were recruited randomly from selected homes and child day
care centers.  Monitoring was performed over a 48-h period at the children's homes and/or day
care centers.  Environmental (air, dust, and soil) and personal (hand wipes, diet, water, urine)
samples were collected.  In addition, surface wipe samples including hard floor wipes, food
preparation, and transferable residue (PUF) samples were collected from homes that had recent
pesticide applications. The samples were analyzed by gas chromatography/mass spectrometry
(GC/MS) for over 50 pollutants from such chemical classes as the organophosphate (OP)
pesticides, organochlorine (OC) pesticides, pyrethroid pesticides, acid herbicides, polycyclic
aromatic hydrocarbons (PAHs), phthalates, phenols, polychlorinated biphenyls (PCBs), and the
triazine pesticide atrazine.  The pollutants were selected because they had been commonly
detected in the past in indoor and outdoor environments and/or were potentially carcinogenic,
mutagenic, or endocrine disrupting chemicals in humans.

       The study showed that the participating NC and OH preschool children were potentially
exposed at their homes and day care centers to low levels of many of these pollutants from
several sources. In addition, these children were potentially exposed/dosed at low levels to some
of these pollutants  through several pathways and routes. The conclusions derived from the study
apply only to the children and their primary caregivers in NC and OH who participated in this
study and cannot be generalized to all preschool children in either state. Therefore, the
comparisons between results from NC and OH discussed below apply only to the results for
children in the selected NC and OH counties. In addition, this data report has only discussed the
potential exposures and potential absorbed doses of these preschool children and their primary
caregivers to pollutants in these environments, not possible health effects associated with these
exposures.
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2.2    Goal 1
       The CTEPP study's first goal was to measure the concentrations of the target pollutants
in multimedia samples collected at the homes and day care centers of 257 preschool children in
six NC and six OH counties.

2.2.1  Multimedia Sources of Potential Exposure

       Many of the pollutants were detected in several environmental, personal, and biological
media at the homes and day care centers of the participating NC and OH children.  Pollutants
that were detected in 50% or more of the samples in four or more types of environmental or
personal media were regarded as "frequently detected" pollutants. For both NC and OH portions
of the study, frequently detected pollutants included the following:

       OP pesticides and metabolite: chlorpyrifos, diazinon, and 3,5,6-TCP,
•      OC pesticides: a^/za-chlordane and gamma-chlordane,
•      Pyrethroid pesticides: c/'s-permethrin and /ram'-permethrin,
•      PAHs: benz[a]anthracene, benzo[&]fluoranthene, benzo[&]fluoranthene,
       benzo[g/z/]perylene, benzo[a]pyrene, benzo[e]pyrene, chrysene, indeno[l,2,3-cd]pyrene,
•      Phthalates: benzylbutylphthalate and di-w-butylphthalate, and
•      Phenols: bisphenol-A and pentachlorophenol.

In addition, PCB 52 and IMP (the metabolite of diazinon) were classified as "frequently
detected" pollutants within the OH portion of the study. PCB 52 was detected in more than 50%
of samples in four types of media in OH but in only two types of media in NC.  IMP was
analyzed only in OH samples.

       For pollutants that were frequently detected in indoor air, indoor floor dust, outdoor air,
dermal wipe, and  solid food samples, median concentrations within these media are given in
Table 2.2.1 for both NC and OH. In both states, these median concentrations were generally
higher for the indoor samples compared to the outdoor samples, although similar median values
were observed in both indoor and outdoor environments for several PAHs, particularly in NC.
Median PAH concentrations  in indoor and outdoor air were slightly higher for NC air samples
than for OH air samples. Both the NC and OH solid food samples contained only a few
pollutants at median levels above the method detection limit (MDL).  These pollutants were
chlorpyrifos (0.17 and 0.18 ng/g), 3,5,6-TCP (2.3 and 1.9 ng/g), and bisphenol-A (4.1 and 3.5
ng/g), where the numbers in parentheses correspond to median levels in NC and OH solid food
samples, respectively.  It is of interest to note that median levels of 3,5,6-TCP were about 15 and
10 times higher than the chlorpyrifos levels in solid food samples from NC and OH, respectively.
The break-down product of DDT,p,p '-DDE, was not classified as a frequently detected
pollutant, but it was detected in greater than 50% of solid food samples.  The median levels of
p,p '-DDE were 0.16 and 0.18 ng/g, respectively, in NC and OH solid food samples. In dust
samples, median concentrations of several PAHs were at least four times lower in homes and/or
day care centers of NC children compared to OH. In dermal wipe samples, median
concentrations of all PAHs were higher in OH than in NC. Lastly, median levels of bisphenol-A

                                           2-2

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were much higher in the dermal wipe samples in NC (5,900 ng/m2) and OH (4,600 ng/m2)
compared to the other frequently detected pollutants (< 530 ng/m2).

Table 2.2.1.   Median Levels of Pollutants Frequently Detected in Air, Dust, Dermal Wipe,
              and Solid Food Samples Collected at the Homes and Day Care Centers of
              Preschool Children in NC and OH
Pollutant/Metabolite
Chlorpyrifos
Diazinon
3,5,6-TCP
IMP
alpha-CUordane
gamma-Ch\ordane
cw-Permethrin
trans- Permethrin
Benz[a]anthracene
Benzo [b] fluoranthene
Benzo [k] fluoranthene
Benzo [gfe'Jperylene
Benzo [ajpyrene
Benzo [ejpyrene
Chrysene
Indeno[l ,2,3-oflpyrene
Bisphenol-A
Indoor Air,
ng/m3
NC OH
6.1
2.0
1.8
b
0.84
1.5
0.41
0.27
<
0.13
<
0.12
0.08
<
0.10
0.09
1.6
1.8
0.97
0.65
0.53
0.23
0.34
<
<
<
<
<
<
<
<
<
<
0.98
Dust,
ng/g
NC OH
140
21
92
-
24
36
800
730
130
350
110
190
200
190
180
180
<
62
25
42
15
11
13
500
390
640
1700
620
930
930
930
940
880
28
Outdoor Air,
ng/m3
NC OH
0.28
0.09
0.23
-
0.09
0.13
<
<
0.064
0.19
0.064
0.13
0.09
0.095
0.12
0.095
<
0.20
0.15
0.21
0.33
0.09
0.10
<
<
<
<
<
<
<
<
<
<
<
Dermal Wipe,
ng/m2
NC OH
160
33
130
-
34
42
530
300
<
<
<
<
<
<
<
<
5900
60

-------
wipe samples from NC.  In OH, median concentrations of benzylbutylphthalate and di-n-
butylphthalate were 19,000 and 6,400 ng/g in dust samples and were below the MDL within
dermal wipe samples.  Note that higher background levels were observed in OH dermal wipe
samples compared to NC samples. These background median levels of the MDL were 6,400 and
8,000 ng/m2 for benzylbutylphthalate, and 1,900 and 8,200 ng/m2 for di-w-butylphthalate, in NC
and OH dermal wipes, respectively.

       Liquid food and soil media types were not included in Table 2.2.1, because measured
concentrations of the frequently detected pollutants were typically low or below the MDL in
these media.  Only one pollutant, bisphenol-A, had median concentrations in liquid food samples
which were above the MDL (0.46 ng/mL in NC and 0.49 ng/mL in OH).  Generally, PAH
concentrations in soil samples were lower than the corresponding dust samples. Median levels
of the frequently detected PAHs ranged from 0.66 to 3.2 ng/g in NC soil and from 12 to 33 ng/g
in OH soil. The median level of di-w-butylphthalate was 44 ng/g in OH soil, but below the MDL
in NC soil.

       Table 2.2.2 presents median concentrations of pollutants that were frequently detected in
three types of surface samples that were collected after recent pesticide applications at homes in
NC and OH (hard floor surface wipe, food preparation surface wipe, and transferable residues
[PUF]). Median levels of chlorpyrifos and benzylbutylphthalate in the hard floor surface wipes,
along with benzylbutylphthalate in transferable residues, were more than four times greater in
samples collected from NC homes than those from OH homes.  In addition, median levels of di-
w-butylphthalate were slightly lower in all three surface sample types collected in NC homes
than those from OH homes. In NC, median levels of the pyrethroid pesticides (cis- and trans-
permethrin) ranged from 210 to 600 ng/m2 in these surface wipes and transferable residue
samples and were higher than those of the OP pesticides, while median levels of the pyrethroid
pesticides ranged from 31 to 65 ng/m2 for these sample types in OH homes.

       In summary, several pollutants, including chlorpyrifos, 3,5,6-TCP, c/s-permethrin, trans-
permethrin, benz[a]anthracene, benzo[&]fluoranthene, benzo[£]fluoranthene, benzo[g/z/]perylene,
benz[a]anthracene, benzo[&]fluoranthene benzo[&]fluoranthene, benzo[g/z/]perylene,
benzo[a]pyrene, benzo[e]pyrene, chrysene, indeno[l,2,3-cd]pyrene, benzylbutylphthalate, di-n-
butylphthalate, and bisphenol-A, were frequently detected in several environmental media such
as air, dust, and surface wipes, as well as in personal samples such as dermal wipes and foods,
collected at the homes and day care centers of participating children in both states. Therefore,
children could be potentially exposed to these pollutants in multiple environmental and personal
media through different exposure routes.
                                           2-4

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Table 2.2.2.  Median Levels of Pollutants Measured in Surface Samples Which Were
             Collected After Recent Pesticide Applications at Homes in NC and OH
Pollutant/Metabolite
Chlorpyrifos
Diazinon
cw-Permethrin
trans-Permethnn
Chrysene
Benzylbutylphthalate
Di-w -buty Iphthalate
Bisphenol-A
Hard Floor Surface Wipe,
ng/m2
NC OH
68
12
500
400
25
29,000
5,000
210
16
/7a-chlordane, gamma-chlordane,
c/5-permethrin, and frYms-permethrin in dust were 10.0, 11.1, 11.1, 5.6  and 6.3 times higher,
respectively, at day care centers than  at homes in NC. Loadings of several PAHs
(benz[a]anthracene, benzo[&]fluoranthene, benzo[£]fluoranthene, benzo[g/7/']perylene,
benzo[a]pyrene, benzo[e]pyrene, chrysene,  dibenz[a,/z]anthracene, andindeno[l,2,3-cJ]pyrene)
in dust ranged between 7.7 to 8.3 times higher at day care centers than at homes in NC. Loadings
of benzylbutylphthalate and di-w-butylphthalate were both 10 times higher,  and loadings of
pentachlorophenol were 4.2 times higher, in dust at day care centers compared to homes in NC.
In children's dermal wipe samples, bisphenol-A loadings were three times higher when collected
                                           2-5

-------
at day care centers versus homes in NC. However, highly significant differences between day
care and home environments occurred less frequently when levels in floor dust were expressed in
concentration units (ng/g). These results were partly due to the higher dust loadings measured in
carpets at day care centers compared to homes in NC. The mean value of fine dust particle
          loadings in NC day care centers was more than twice that in NC homes.
       Similar to NC, highly significant differences (p<0.01) were frequently observed among
the different pollutants and sample media in OH, with higher levels frequently found in day care
centers compared to homes, especially for dust when expressed as a loading. Loadings of
chlorpyrifos, diazinon, 3,5,6-TCP, cyfluthrin, c/s-permethrin, and trans-permGthrin were 7.1, 5.9,
3.4, 4.3, 5.0, and 5.3 times higher, respectively, at day care centers than at homes in OH.
Similarly, levels of PAHs (benz[a]anthracene, benzo[6]fluoranthene, benzo[g/z/]perylene,
benzo[a]pyrene, benzo[e]pyrene, chrysene, dibenz[a,/z]anthracene, andindeno[l,2,3-cJ]pyrene)
ranged between 5.6 and 6.7 times higher at day care centers than at homes in OH.  Loadings of
benzylbutylphthalate and di-w-butylphthalate were both 7.1 times higher in dust loadings at day
care centers compared to homes in OH. In addition, levels of bisphenol-A and PCB 52 were 3.0
and 4.2 times higher, respectively, at day care centers than at homes in OH.  However, like for
NC, highly significant differences between OH day care and home environments occurred less
frequently when levels in floor dust were expressed in concentration units (ng/g), partly due to the
amounts of dust at OH day care centers being generally higher (approximately three times) than
in OH homes.

       Comparisons between urban and rural environments: Only the acid herbicide 2,4-D had
dust concentrations (ng/g) which were highly significantly different (p<0.01) between urban and
rural locations for NC, with concentrations being 3.2 times higher in urban settings compared to
rural settings. In OH, there were several pollutants having concentrations in dust which were
highly  significantly different between urban and rural settings.  Concentrations  of PAHs
(benz[a]anthracene, benzo[&]fluoranthene, benzo[£]fluoranthene, benzo[g/7/']perylene,
benzo[a]pyrene, benzo[e]pyrene, chrysene, dibenz[a,/z]anthracene, andindeno[l,2,3-cJ]pyrene)
in OH dust samples ranged from 3.3 to 4.0 times higher in urban compared to rural environments.
When PAH levels in dust were expressed as loadings (ng/m2), the levels of benz [a] anthracene and
chrysene were 3.2 and 3.0 times higher in urban than rural environments.

       Comparisons between low-income and middle/high-income environments:  In NC,  several
pollutants and sample media had highly statistically significant (p<0.01) differences occurring for
children in the low-income compared to middle/high-income groups. Concentrations (ng/m3) of
diazinon, c/'s-permethrin, and trans-permethrin in indoor air samples were 3.6, 4.2, and 3.9 times
higher, respectively, for low-income households than middle/high-income households. Loadings
(ng/m2) of diazinon, 3,5,6-TCP, c/s-permethrin, and benzylbutylphthalate in NC dust samples
were 6.3, 3.4, 3.2, and 4.8 times higher, respectively, for low-income households than for
middle/high-income households. In contrast, concentrations of 2,4-D in dust samples (ng/g) were
4.5 times higher for middle/high-income households compared to low-income households.

       In OH, loadings of chlorpyrifos in dust samples (ng/m2) were 3.4 times higher in low-
income households compared to middle/high-income households. In contrast, concentrations of

                                           2-6

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2,4-D in dust samples (ng/g) were 4.2 times higher in middle/high-income households than in
low-income households.

       Summary: As determined from analyses performed on environmental and personal
sample media measurements, highly significant differences in floor dust loadings (ng/m2)
occurred between day care and home environments in both NC and OH for diazinon, the
pyrethroid pesticides, the nine PAHs, and the two phthalates, with loadings at homes averaging
less than one-third of the loadings observed in day care centers. These results were partly due to
the higher levels of dust in the carpets at day care centers compared to homes in both states. NC
preschool children were potentially exposed to higher levels of 2,4-D in dust samples (ng/g)
within an urban location compared to a rural setting, suggesting that 2,4-D may have been used as
a lawn herbicide for weed control more frequently in urban than in rural locations. OH children
were potentially exposed to higher levels of several PAHs in dust (ng/g and ng/m2) when in an
urban location compared to a rural setting; PAH concentrations (ng/g) tended to be at least two
times higher in urban dust samples than in rural dust samples in OH.  Through indoor air, NC
preschool children were potentially exposed to higher levels of diazinon, c/'s-permethrin, and
fraw^-permethrin when in low-income environments compared to middle/high-income
households. In addition, the NC preschool children were exposed to higher levels of diazinon,
3,5,6-TCP,  c/5-permethrin, and benzylbutylphthalate in dust (ng/m2) when in low-income
compared to middle/high-income households. However, concentrations of 2,4-D tended to be
higher in dust samples (ng/g) from middle/high-income than from low-income households. In
OH, levels  of chlorpyrifos in dust (ng/m2) were higher in low-income than in middle/high-income
households, while concentrations of 2,4-D in dust samples were higher in middle/high-income
households compared to low-income households.

2.3    Goal 2

       The second goal of the CTEPP study was to determine the distributions of child
characteristics, activities, and locations that contributed to their exposures.  The factors that were
considered  important for determining the children's and their primary caregiver's potential
exposures and potential absorbed doses to  pollutants were the following:

•      physical characteristics of the participant (body weight and hand surface area),
       children's activity patterns (frequency of placing toys and other objects in the mouth,
       pacifier use, teething, and frequency of washing hands),
•      locations where  children spent their time (indoor and outdoors at homes, at day care
       centers, or other locations)
•      volume of liquid and weight of solid food consumed by the participant over a 24-h period.
       These factors were used in the algorithms to estimate the children's exposures to
pollutants at homes and/or day care centers through the inhalation and ingestion (dietary and
indirect) routes of exposure. Exposures via the dermal route were not estimated for the children in
this study.
                                           2-7

-------
2.4    Goal 3

       The third goal of the CTEPP study was to estimate potential exposure level (ng/day) and
potential absorbed dose (ng/kg/day) of the pollutants that the study participants may encounter in
their everyday environments.  Potential exposure (ng/day) is defined as the total amount of a
pollutant that an individual comes in contact with over a 24-h period. Potential absorbed dose
(ng/kg/day) is defined as the total dose that could be absorbed in the body by the three routes of
exposure over a 24-h period, relative to the participant's body weight (kg). For each exposure
route, potential absorbed dose was estimated by assuming a 50% absorption rate for all pollutants
and participants. Aggregate potential exposure and aggregate potential absorbed dose were
defined as the sums of the estimated potential  exposure and potential absorbed dose, respectively,
across all three  exposure routes.
       These estimates were made for selected pollutants via up to three routes of exposure
(inhalation, dietary ingestion,  and indirect ingestion).  Then, for those pollutants having estimates
available for all three exposure routes, aggregated potential exposure level and aggregated
potential absorbed dose were calculated as the sum of the exposure/dose estimates across the
three routes.

       For each state, the following pollutants were considered for estimating potential  exposure
level and potential absorbed dose for the study participants:

•      OP pesticides/metabolite: chlorpyrifos, diazinon, and 3,5,6-TCP,
       OC pesticides: a//?/za-chlordane, gamma-chlordane, p,p '-DDE, and heptachlor (NC only),
•      Pyrethroid pesticides: cyfluthrin, c/s-permethrin, and fr'am'-permethrin,
       Acid herbicide: 2,4-D,
•      PAHs: benz[a]anthracene, benzo[&]fluoranthene, benzo[&]fluoranthene,
       benzo[g/z/]perylene, benzo[a]pyrene, benzo[e]pyrene, chrysene, dibenz[a,/z]anthracene,
       and indeno[l,2,3-cd]pyrene,
       Phthalates: benzylbutylphthalate and di-w-butylphthalate,
•      Phenols: bisphenol-A and pentachlorophenol, and
       PCBs: congeners 52, 95,  and 101.

       For most of these pollutants, potential  exposure level and potential  absorbed dose were
estimated under a given exposure route for the study participants in a given state only when at
least 45% of the samples collected in that state had detectable measurements for each media type
entering into the calculation of the estimates.

       For each state, aggregated potential exposure level and aggregated potential absorbed dose
was estimated for the following eight pollutants (based on availability of exposure/dose estimates
for each of the three exposure routes):
       OP pesticides/metabolite: chlorpyrifos, diazinon, and 3,5,6-TCP,
       Pyrethroid pesticides: c/'s-permethrin and ^ram'-permethrin,
       Acid herbicide: 2,4-D,

                                            2-8

-------
       Phthalate: di-w-butylphthalate, and
•      Phenol: bisphenol-A

2.4.1.  Estimated Potential Exposure Levels for NC and OH Preschool Children

       Potential exposure level (ng/day) was defined as the total amount of a pollutant that an
individual comes in contact with over a 24-h period. The estimated potential exposure levels of
the participating NC and OH preschool children were quantified by one or more routes of
exposure for each of the pollutants mentioned above.

       For the NC children, the estimated median potential exposure levels were highest for di-n-
butylphthalate (1,800 ng/day) through the inhalation route of exposure, followed by lower levels
of heptachlor (62 ng/day) and chlorpyrifos (47 ng/day).  Estimated exposures to other pollutants
via the inhalation route were less than 20 ng/day.  When considering the dietary ingestion route,
median potential exposure levels for NC children were highest for di-w-butylphthalate (39,000
ng/day), bisphenol-A (2,700 ng/day), and 3,5,6-TCP (1,200 ng/day), while exposures to other
pollutants were less than 200 ng/day. When considering the indirect ingestion route, median
potential exposure levels for NC children were highest for benzylbutylphthalate (920 ng/day) and
di-w-butylphthalate (350 ng/day), c/'s-permethrin (48 ng/day), and /ram'-permethrin (35 ng/day)
while estimated exposures to other pollutants were less than 10 ng/day.

       For the OH children, the estimated median potential exposure levels were highest for di-n-
butylphthalate (2,000 ng/day) through the inhalation route of exposure, followed by lower levels
of pentachlorophenol (18  ng/day) and chlorpyrifos (15 ng/day). Estimated exposures to other
pollutants via the inhalation route were less than  10 ng/day. When considering the dietary
ingestion route, median potential exposure levels  for OH children were highest for
benzylbutylphthalate (9,400 ng/day), bisphenol-A (1,700 ng/day), and 3,5,6-TCP (860 ng/day),
while exposures to other pollutants were less than 150 ng/day.  When considering the indirect
ingestion route, median potential exposure levels  for OH children were highest for
benzylbutylphthalate (630 ng/day) and di-w-butylphthalate (210 ng/day), while exposures to
PAHs except for dibenz[a,/z]anthracene (6.2 to 53 ng/day) and  to cis- and  fram'-permethrin (18
and 12 ng/day) were each greater than  10 ng/day, and estimated exposures to other pollutants
were less than 10 ng/day.  These results suggest that participating children had the highest
potential exposure levels to phthalates through all three routes  of exposure.

2.4.2.  Estimated Potential Absorbed Doses for NC and OH Preschool Children

       Potential absorbed dose (ng/kg/day) was defined as the total amount that could be
absorbed into the body over a 24-h period, relative to the child's body weight (kg). For each
exposure route, potential absorbed dose was estimated under the assumption that all pollutants
had a 50% absorption rate into the body for all exposure routes (17). The estimated potential
absorbed doses of the NC and OH preschool children were quantified by one or more routes of
exposure for each of the pollutants mentioned above.
                                            2-9

-------
       For the NC children, estimated median potential absorbed doses were highest for di-n-
butylphthalate (56 ng/kg/day) through the inhalation route of exposure, followed by much lower
concentrations for heptachlor (1.7 ng/kg/day) and chlorpyrifos (1.4 ng/kg/day). When considering
the dietary ingestion route, median potential absorbed doses for NC children were highest for di-
«-butylphthalate(l,100 ng/kg/day), followed by bisphenol-A (74 ng/kg/day).
Benzylbutylphthalate had the highest estimated median potential absorbed doses (26 ng/kg/day)
under the indirect ingestion route of exposure, followed by di-w-butylphthalate (9.7 ng/kg/day).

       For the OH children, estimated median potential absorbed doses were highest for di-n-
butylphthalate (57 ng/kg/day) through the inhalation route of exposure, while all other pollutants
had estimated median potential absorbed doses via the inhalation route of less than 0.6 ng/kg/day.
When considering the dietary ingestion route, median potential absorbed doses for OH children
were highest for benzylbutylphthalate (270 ng/kg/day), bisphenol-A (52 ng/kg/day) and 3,5,6-
TCP (25 ng/kg/day), while median estimated potential absorbed doses through the indirect
ingestion route were highest for benzylbutylphthalate (18 ng/kg/day), followed by di-n-
butylphthalate (5.7 ng/kg/day).  Like for potential exposure level, these results suggest that the
preschool children had the highest potential absorbed doses to the phthalates through all three
routes of exposure.

2.4.3.  Estimated Aggregated Potential Exposure Levels for NC and OH Preschool Children

       Aggregated potential exposure (ng/day) was defined as the sum of the estimated potential
exposure levels across all three exposure routes - inhalation, direct ingestion and indirect
ingestion - and was estimated for the eight pollutants mentioned earlier. Figure 2.4.1 presents
median values of the aggregated potential exposure levels for the study participants.

       NC children had the highest median aggregated potential exposure levels to di-n-
butylphthalate (42,900 ng/day),  followed by bisphenol-A (2,560 ng/day), and 3,5,6-TCP (1,230
ng/day), while the lowest median aggregated potential exposure level was observed for diazinon
                                           2-10

-------
                                  Figure A
            45000
            40000
            35000
            30000
            25000
            20000
            15000
            10000
              5000
                  0
                   &  A*  r*
&  <>^0V>*V
*  J  J>  £  «+
                                               
-------
(51.6 ng/day). OH children had the highest median aggregate potential exposure levels to di-w-
butylphthalate (8,310 ng/day), bisphenol-A (1,880 ng/day), and 3,5,6-TCP (930 ng/day), while
the lowest median aggregate potential exposure level was observed for diazinon (38.6 ng/day).
Thus, children in both states had the highest potential aggregate exposures to di-w-butylphthalate,
bisphenol-A, and 3,5,6-TCP in their everyday environments. However, NC children had five
times greater median aggregate potential exposure levels to di-w-butylphthalate than OH children.

2.4.4.  Estimated Aggregated Potential Absorbed Doses for NC and OH Preschool Children

       Aggregate potential absorbed dose (ng/kg/day) was defined as the sum of the estimated
potential absorbed dose across  all three exposure routes - inhalation, dietary ingestion, and
nondietary ingestion - and was estimated for the eight pollutants mentioned earlier.  Figure 2.4.2
presents median values of the aggregated potential  absorbed doses for the study participants.

       The NC and OH children had the highest median aggregated potential absorbed doses to
di-w-butylphthalate (1,250 and  262 ng/kg/day) and  bisphenol-A (71.4 and 60.8 ng/kg/day),
respectively. Both the NC and OH children had the lowest median aggregated potential doses to
diazinon (1.44 and 1.13 ng/kg/day), respectively.

       The results show that both the NC and OH children had the highest estimated aggregated
potential absorbed doses to di-w-butylphthalate in their everyday environments. However, the NC
children had over four times greater median aggregated potential absorbed doses of di-n-
butylphthalate than the OH children.

2.4.5  Urinary Biomarker Concentrations as a Indicator of Absorbed Dose

       Several acid pollutants and metabolites were measured in urine samples collected over the
48-h sampling period from each study participant.  Of these, 3,5,6-TCP, 2,4-D, and
pentachlorophenol were used as indicators of aggregated potential absorbed doses. For NC
children, median urinary concentrations were 5.3 ng/mL for 3,5,6-TCP (98% detected), 0.7
ng/mL for 2,4-D (94% detected), and 0.4 ng/mL for pentachlorophenol (89% detected).  Similar
median levels were observed for OH children:  5.1 ng/mL for 3,5,6-TCP  (100% detected), 1.0
ng/mL for 2,4-D (98% detected), and 0.8 ng/mL for pentachlorophenol (99% detected).

       In urine samples, NC and OH children had at least five times greater levels of 3,5,6-TCP
compared to 2,4-D and pentachlorophenol. Overall, NC and OH children were exposed to low
levels of these pollutants or their metabolites at their homes and/or day care centers over the 48-h
sampling period.

2.4.6.  Testing Important Hypothesis

       Analyses of estimated potential exposure levels, potential absorbed doses, aggregated
potential exposure levels, aggregated potential absorbed doses, and urinary concentrations of the
participating children were performed to address the first three of the seven hypotheses listed in
                                           2-12

-------
                                         Figure A
14UU-
1200
1000
| 800
|* 600
0)
= 400
200
n.






,__
\








itrt
                                          Figure B
Figure 2.4.2  Estimated Median Aggregate Potential Doses of NC and OH Preschool
              Children to Eight Pollutants in Their Everyday Environments

Legend: CPS = Chlorpyrifos; DZN = Diazinon; TCP = 3,5,6-Trichloro-2-pyridinol Cis-P and Trans-? = Cis- and
Traws-Permethrin; 2,4-D = 2,4-Dichlorophenoxyacetic acid; DBP = Di-w-butylphthalate; BPA = Bisphenol-A

Note: Figures A and B are equivalent, except Figure B excludes DBP.
                                             2-13

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Section 1.0. An analysis of variance approach was taken to determine whether these estimates
and concentrations differed significantly between 1) day care children and stay-at-home children,
2) children in urban and rural environments, and 3) children in low-income and middle/high-
income environments.

       The comparisons between the exposures of children and adults in the same households in
NC and OH are not discussed in this section. The results in chapter 9 showed that children were
generally exposed to significantly higher levels of pollutants than adults in the same household,
however, these results were likely due to differences in physiological factors (i.e., ventilation
rates and body weights), activity patterns (i.e., hand-to-mouth and object-to-mouth), or
consumption of different types of food.

       Comparisons between day care children and stay-at-home children:   For the nine PAHs
and for benzylbutylphthalate via the indirect ingestion route, OH day care children ranged up  to
3.3 times higher potential exposures and potential absorbed doses compared to stay-at-home
children, and these differences  were highly significant. For the dietary ingestion exposure route,
highly significant differences existed in potential exposure level and/or potential absorbed dose
between OH day care children  and stay-at-home children for cis- and ^raws-permethrin and for
benzylbutylphthalate, with day care children having approximately three times the levels, on
average, compared to stay-at-home children. For NC children, potential exposure level or
potential absorbed dose for one group (day care children or stay-at-home children) was always
less than three times the value of the second group, on average, across the pollutants and exposure
routes.

       Comparisons between children in urban and rural environments: NC children who lived
in urban counties had 3.4 times and 3.7 times higher potential exposures and potential absorbed
doses, respectively, to 2,4-D through the indirect ingestion route of exposure compared to rural
children, and these differences  were highly significant (p<0.01). Similarly, OH children living in
urban counties had 3.2 to 3.7 times higher potential exposures and potential absorbed doses of
each of the nine PAHs through the indirect ingestion route of exposure compared to rural
children, and these differences  were highly significant.

       Comparisons between children in low-income and middle/low- income environments:
Between low-income and middle/high-income children in both NC and OH, potential exposure
and potential absorbed dose estimates of 2,4-D were highly significantly different under the
indirect ingestion route,  with low-income children averaging 30% or less of the estimates of
middle/high-income children, on average.

       Summary: The largest differences between urban and rural children, between day care
and stay-at-home children, and between low-income and middle/high-income children in
potential exposure level  and potential absorbed dose, as well as the most frequent occurrences of
significant differences, occurred within the indirect ingestion exposure route for both states.
There were relatively few occurrences of highly significant differences between population strata
for either aggregated potential exposure levels or aggregated potential absorbed dose among the
eight pollutants for which these measures were calculated for the study participants, and no
                                           2-14

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difference deemed to be highly significant was at least three times larger, on average, for one
stratum versus another.  There were no highly significant differences in urinary concentrations of
3,5,6-TCP, 2,4-D or pentachlorophenol between any strata.

2.5    Goal 4

       The fourth goal of the CTEPP study was to apportion the aggregated potential exposure
levels and aggregated potential absorbed dose estimates for the NC and OH children across the
inhalation, dietary ingestion, and indirect ingestion routes of exposure. These aggregated potential
exposure levels and aggregated potential absorbed doses could be quantified through the three
routes of exposure for eight pollutants: chlorpyrifos, diazinon, 3,5,6-TCP, c/s-permethrin, trans-
permethrin 2,4-D, di-w-butylphthalate, and bisphenol-A.  Statistical analyses involved calculating
the proportions of the aggregate potential exposure levels and aggregate potential doses by each
route of exposure for each child, then fitting a logistic regression model to these proportions to
estimate mean proportions as a function of environmental type, urbanicity, and income status.

       Figures 2.5.1 and 2.5.2 illustrate the overall estimates of the mean proportions by route of
exposure for NC and OH children, respectively. The results show that for both states, the dietary
ingestion route was the primary route of exposure to all eight pollutants. Greater than 92% of the
aggregated potential exposure levels and aggregated potential absorbed doses of the children were
to bisphenol-A, 3,5,6-TCP, 2,4-D, and di-w-butylphthalate through the dietary ingestion route of
exposure. In addition, about 50% of the aggregated potential exposure levels and potential
absorbed doses of ^ram'-permethrin, c/s-permethrin, diazinon, and chlorpyrifos were through the
dietary ingestion route of exposure. The OP pesticides, chlorpyrifos and diazinon, contributed
most to the inhalation route of exposure for NC and OH children, while the pyrethroids, cis-
permethrin and fram'-permethrin, contributed most to the indirect ingestion route of exposure.
Therefore, children in both states were predominantly exposed to the eight chemicals through
ingestion, primarily dietary in nature.

       Mean proportions associated with each exposure route were also calculated by stratum
(urban children, rural children, low-income children, middle/high-income children, day care
children, stay-at-home children), and statistical analysis was performed to determine whether a
particular type of stratum (urbanicity, income level, day care attendance) had a significant effect
on the mean proportion for a given exposure route. Results of this analysis showed that there were
several highly statistically significant (p<0.01) differences in the exposures of NC or OH children
between pairs of strata.  However, these statistically significant differences between each strata
were frequently not realistically meaningful, except in some instances. For example, for
diazinon, mean proportions for the inhalation route of exposure differed significantly (p<0.01)
between low-income children (46%) and middle/high-income children (34%) for NC children.

       For the NC and OH children, Table 2.5.1 presents the relative importance of the children's
exposures to the eight target pollutants through the inhalation, dietary ingestion, and indirect
ingestion routes of exposure.
                                           2-15

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                                    39%
                      Chlorpyrifos
                                 -2%
                 38°/,
                                    8%
                        trans-P
                 93%
                                                  557
                                                                     40%
                                                 39%
              Diazinon
                   5%
                                                          cis-P
               2,4-D
                          DBF
                BPA
                        Inhalation
Dietary
Indirect
Figure 2.5.1  Estimated Mean Proportion of Aggregated Potential Exposure and Potential
              Absorbed Dose for NC Children, by Exposure Route

Legend: TCP = 3,5,6-Trichloro-2-pyridinol; Cis-P and Trans-P = Cis- and Traws-Permethrin; 2,4-D = 2,4-
Dichlorophenoxyacetic acid; DBP = Di-w-butylphthalate; BPA = Bisphenol-A.
                                            2-16

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                         Chlorpyrifos
                     37°/,
                          trans-?

                            2%
                         DBF
                                                   62P/o
          Diazinon
                                                  39%
                                                         cis-P
              2,4-D
                                                           BPA
                                                                   < 3%
                                                                     3%
                          Inhalation
Dietary
Indirect
Figure 2.5.2  Estimated Mean Proportion of Aggregated Potential Exposure and Potential
              Absorbed Dose for OH Children, by Exposure Route

Legend: TCP = 3,5,6-Trichloro-2-pyridinol; Cis-P and Trans-? = Cis- and Traras-Permethrin; 2,4-D = 2,4-
Dichlorophenoxyacetic acid; DBP = Di-w-butylphthalate; BPA = Bisphenol-A..
                                            2-17

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Table 2.5.1    The Relative Importance of the NC and OH Children's Exposures to the
              Eight Pollutants Through the Inhalation, Dietary Ingestion, and Indirect
              Ingestion Routes of Exposure.
Chemical
Class
OP
Pesticides
OP
Metabolite
Pyrethroid
Pesticides
Acid
Herbicide
Pollutant(s)
Chlorpyrifos
Diazinon
3,5,6-TCP
c/5-Permethrin
trans -Permethrin
2,4-D
Apportionment of Aggregated Exposure/Dose
JVC: dietary ingestion ~ inhalation > indirect ingestion
OH: dietary ingestion > inhalation > indirect ingestion
JVC: dietary ingestion > inhalation > indirect ingestion
OH: dietary ingestion > inhalation > indirect ingestion
JVC: dietary ingestion ~ indirect ingestion > inhalation
OH: dietary ingestion > indirect ingestion > inhalation
JVC: dietary ingestion > inhalation > indirect ingestion
OH: dietary ingestion > indirect ingestion ~ inhalation
 Phthalate     Di-w-butylphthalate
 Phenol
Bisphenol-A
JVC: dietary ingestion > inhalation > indirect ingestion
OH: dietary ingestion > inhalation > indirect ingestion

JVC: dietary ingestion > inhalation > indirect ingestion
OH: dietary ingestion > inhalation > indirect ingestion
       In summary, the NC and OH children had similar mean proportions of aggregated
potential exposure level and of aggregated potential absorbed dose for the eight pollutants across
the three routes of exposure considered in this study. The dominant route of exposure for these
children was through dietary ingestion for all eight pollutants. The OP pesticides, chlorpyrifos
and diazinon, contributed most to the inhalation route of exposure, while the pyrethroids, cis- and
^ram'-permethrin contributed most to the indirect ingestion route of exposure.
                                           2-18

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                                      Chapter 3
                                 Recommendations
       The CTEPP study has provided a wealth of data on young children's exposures to
pollutants in their everyday environments. The study findings indicate that the participating
children in NC and OH could have been potentially exposed and could have acquired potential
doses to low levels of many of the targeted pollutants from several sources, through several
pathways and routes.
       EPA will use these data in the future for the following:

       To estimate the dermal exposures of the NC and OH preschool children to the eight most
       prevalent pollutants, in order to estimate better their aggregate exposures to these
       pollutants in their everyday environments.

       To refine the algorithms that are currently used to determine children's potential
       exposures and potential absorbed  doses to these pollutants.

       To refine models and human health risk assessments, particularly for children.

       To compare the levels of potential exposure and potential absorbed doses with possible
       human health effects, particularly in children.
                                           3-1

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                                      Chapter 4
                  Sampling Design and Participant Recruitment
4.1    Sampling Design

       A population-based, stratified random sampling design (Figure 4.1.1) was developed to
collect the data needed to meet the objectives of the study. In each state, four urban and two
rural counties, representing three distinct geographical areas in the state, were randomly selected.
Within these counties, there were two sampling frames (components), which were designed to
allow testing of the study hypotheses, and in particular, to test whether the children's exposures
are significantly different at day care versus at home.  The first sampling component, the
telephone component, was composed of households that were selected randomly through list-
assisted telephone sampling.  The telephone component enrolled households with preschool
children who did not attend day care. The second sampling component, the day care component,
was composed of child day care centers that were randomly selected and enrolled households
with preschool children who did attend day care.  Within these components, the households and
child day care centers were stratified by income.

       In both North Carolina (NC) and Ohio (OH), six counties were selected using stratified
random sampling. Because of stratification, the samples represented different regions, urban and
rural areas, and low-income and middle/high-income areas of each state. The sample selection
process targeted counties with larger population and in particular, larger population in the low-
income groups, by selecting counties using probabilities proportional to size (PPS) within each
stratum.  The county population in the low-income segment was used as a measure of size. This
approach ensured greater representation of low-income families  than would have occurred
otherwise.  The locations of these counties in the two states are shown in Figure 4.1.2.  The
selected counties were in three distinct geographical areas in each state.  In NC, these
geographical areas were the coastal plain, the Piedmont, and the mountains.  In OH, the areas
were the northern, central, and southern regions.

       Within each of the two states, the samples were further stratified according to degree of
urban character (urbanicity) and family income.  The urbanicity  stratification was imposed at the
first stage of selection by classifying counties as predominantly urban or rural. A county was
considered urban if it was within or contained wholly or in part a Metropolitan Statistical Area
(MSA) as defined by the Office of Management and Budget (OMB Bulletin No. 99-04). Income
stratification was performed at subsequent stages of selection for the day care component and the
telephone component. This stratification was used to distinguish between low-income and
middle/high-income households and day care centers. Day care centers  were classified as low-
income if they received Federal assistance to serve low-income clients under the Head Start
                                          4-1

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                 Two State Sampling Plan (NC and OH)
                   Select Representative Counties - Six Per State
                                 (4 urban, 2 rural)

                     NC Regions:  Mountain, Coastal, Piedmont
                         OH Regions: South, Central, North
                       Two Sampling Frames in Each State
          Sample Component
         Telephone Screening
     Use List-Assisted Telephone
       Sampling Technique;
    Recruit Age-Eligible Children
       Stratify by Income Level;
       64 Participants per State
    Expected Response Rate = 75%
         Sample Component
         Day Care Centers
            1st Stage
   Select 16 Day Care Centers with
       Probability Sampling
  Expected Response Rate = 87.5%
           2nd Stage
Randomly Select Age-Eligible Children
      64 Participants per State
   Expected Response Rate = 85%
Figure 4.1.1  CTEPP Overall Sampling Design
                                          4-2

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                                   North Carolina
                                         B
                                                         A. Defiance
                                                         B. Cuyahoga
                                                         C.Fayette
                                                         D. Franklin
                                                         E. Licking
                                                         F. Hamilton
Figure 4.1.2  Six Counties in North Carolina (A) and Ohio (B) Selected by
             Stratified Random Sampling
                                         4-3

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program. Low-income families were classified according to the federal guidelines for assistance
eligibility under the Women, Infants, and Children program (WIC, 2000).  A household was
classified as low-income if its household income was below 185% of the federal poverty
guidelines (Federal Register, 2000).  In 2000, the WIC eligibility level for a family of two was
$20,813 and for a family of four was $31,534.

       In the day care component, all eligible child day care centers in the six selected counties
were identified. A child day care center was considered eligible if it was a commercial or not-
for-profit service provider, which provided child care services to seven or more preschool
children at a location other than the service provider's personal residence.  During the second-
stage sampling frame, these centers were divided into the two income strata. From these strata, a
random sample of targeted centers and a random sample of eligible children within each
participating center were selected. In the telephone component, a random sample of telephone
numbers  was selected, using list-assisted telephone sampling techniques in the six counties in
each state. The anticipated sample size was 128 children in each state, with half (64) from the
day care  center sample (children who attended day care) and the other half (64) from the
telephone sample (children who did not attend day care). This dual frame approach provided
maximum coverage for the target population.

4.2    Recruitment

4.2.1   Recruitment of the Day Care Center Component

       Recruitment of the day care center component was conducted in two stages, as diagramed
in Figure 4.2.1. In the first stage, master lists of all day care centers in NC and of all those in OH
were compiled. For the six target counties in each state, a complete list of day care centers in
each county was prepared and sorted by urbanicity and income. From these lists, approximately
16 centers were targeted for selection; of these at least four were Head Start centers,  which
served primarily low-income clients. The centers were contacted through telephone  calls and
mailings. In the second stage of the day care center component, eligible children who attended
the day care centers were selected randomly from up to two classrooms in each participating
center. Classroom information was requested from each of the centers. Parents or primary
caregivers were contacted through the centers, as discussed below, to obtain informed consent
for study participation.

       Because every eligible child day care center must be licensed to operate in its state, the
state licensing agencies were the main sources of comprehensive lists of centers in both NC and
OH.  Additionally, to ensure the completeness of the master lists of child day care centers, the
lists obtained from the state agencies were supplemented with information on centers from other
sources.  The most updated CD-ROM national telephone database (Pro-CD, 1999-2000,
infoUSA Inc.) was searched, and a list of eligible day care centers in the target counties was
prepared. In addition to the CD-ROM national telephone database, an Internet search was done.
Centers that appeared on the CD-ROM national telephone database and/or the Internet were
cross-checked against the lists provided by state licensing agencies. Centers that appeared on the

                                           4-4

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CD-ROM national telephone database and/or Internet, but did not appear on the list from state
licensing agencies, were called to determine the eligibility status of the center.  Additional
eligible centers were then added to the master list.
                                     First Stage
                                   Obtain complete list of
                                   daycare centers in the
                                      target counties
                                  Randomly select 16 day-
                                  care centers from the list
                                       in each state
                                 Call the selected day care
                                 centers to confirm address
                                   and name of director
                                Mail introductory letters to
                                  the directors of selected
                                     daycare centers
            Conduct follow-up
             calls or visits for
            refusing centers by
           study survey director
             in an attempt to
            reverse the refusal
Conduct follow-up calls
  and schedule visits
                                  Conduct follow-up visits
                                   and obtain informed
                                       consent or
                                 Optional: Obtain mail-back
                                         co nsent
Second
i
Stage
r
Collect daycare
information: number and
age ofeligible children
per class
                                                    Identify and list
                                                    eligible children
                                                   Randomly select 4-6
                                                   children in each day-
                                                       care center
                                                Send introductory letters
                                                   to the parents of
                                                   selected children
Conduct follow-up
calls or visits for
refusing parents by
study survey director
in an attempt to
reverse the refusal


•*-
*.
Conduct follow-up calls
  and schedule visits
                                                 Conduct follow-up visits.
                                                  Meet with the parents at
                                                    the daycare center,
                                                   explain the study, and
                                                  obtain informed consent
                                                           or
                                                Optional: Obtain mail-back
                                                         consent
Figure 4.2.1   Procedures for Recruiting Day Care Center Component
                                                     4-5

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       This sampling component was then stratified by county and by whether or not the center
received Federal assistance to serve low-income clients (Head Start centers). Within each
stratum, day care centers were selected, with probability proportional to the number of children
enrolled in the center. A total of 16 centers, including at least four Head Start centers, were
targeted for recruitment in each state. Further details on the day care center sample recruitment
can be found in the recruitment reports from NC and OH (Appendix B).

       Screening calls were conducted by the recruitment team, to confirm the addresses of the
selected centers and the names of the center directors. After confirmation, the recruitment team
sent an introductory letter, a study brochure, and a gift certificate (as incentive for the center to
participate) to each day care center director by overnight express mail.  Approximately three
days after the letters were mailed, the recruitment team made follow-up calls to each director.
To encourage participation of each center, the team made follow-up visits to the center director,
and the Battelle field team leader contacted the center as needed. The first stage recruitment
activities were completed by obtaining informed consent forms  from each day care  center.

       The second sampling stage of the day care component involved selecting a random
sample of eligible children from up to two classrooms in the selected centers.  Children in the
child day care center component were eligible if they were between the ages of 18 months and 5
years, toilet-trained or able to provide at least one urine sample, and not being breast-fed. In
addition, they had to attend a state-licensed child day care center, serving seven or more
children, on three consecutive days, for at least 25 h per week.

       The second stage recruitment activities began with the determination of the number of
age-eligible children in each classroom. Classroom Information sheets were sent to  and
completed by the day care director. These sheets requested the  following information for each
classroom: name of the classroom, total number of children in the classroom, and the initials and
ages of eligible children. Two classrooms and five children in each classroom were selected
randomly.  Following the selection of the  children, the recruitment team asked the day care
director to distribute the recruitment package,  which contained an introductory letter, a study
brochure, and a gift certificate (as incentive for the household to participate), to the  parents of
the  selected children. Parents were encouraged to call the project toll-free number to ask about
the  study. In consultation with the day care center director, the recruitment team also set up an
appropriate time, typically two or three days after the letters were sent, to meet with the parents
at the day care center.

       During the meeting with the parents, the recruitment team established rapport with the
parents and the child, and gave a small gift to the child, such as  a book or small toy. The
recruitment team emphasized the positive experiences that we and the participants had in our
previous pilot studies. An informed consent form was obtained from the parents, and they were
asked to complete the Recruitment Survey (Form #1; Table 5.2.2).  The recruitment team then
scheduled an initial sampling date with each family.
                                           4-6

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4.2.2.  Recruitment of the Telephone Sample Component

       The procedures for recruiting households by telephone sampling are diagramed in Figure
4.2.2.  A telephone sample list, which included addresses, was ordered from a commercial
survey sampling firm (Marketing Systems Group [MSG], Genesys Sampling System,
http://www.genesys-sampling.com). The sample design used for the telephone component was:
(1) to identify efficiently, through telephone contact, households having one or more children in
the eligible age range, that met the sampling targets in the household low-income or
middle/high-income domains, and (2) to provide coverage of households with unlisted telephone
numbers.

       The survey sampling firm used Census data, marketing research data, and other sources
to classify directory-listed households as having either one or more children in the age range of
18 months to 5 years, or having no children in that age group. The  same data were used to assign
the directory-listed households to an income range. All directory-listed households in each of the
six counties were assigned to one of the following four strata:

1.     Directory-listed households with income above $25,000 and having one or more children
       in the target age range
2.     Directory-listed households with income below or equal to  $25,000 and having one or
       more children in the target age range
3.     Directory-listed households with income above $25,000 and having no children in the
       target age range
4.     Directory-listed households with income below or equal to  $25,000 and having no
       children in the target age range

       In some  counties, as many as 30% of households could have unlisted telephone numbers.
To ensure inclusion of those households that did not appear in the directories, a Random Digit
Dialing (ROD) approach was used. To implement the ROD approach, the survey sampling firm
first identified all telephone exchanges in the selected county. Telephone exchanges having very
low percentages of directory-listed households, primarily nonresidential or business areas, in the
selected county  were deleted. From the remaining exchanges, a systematic random sample of all
numbers was drawn.  Some of these telephone numbers were residential, and some were
business or nonworking numbers.  To prevent a directory-listed telephone number from being
sampled in both the ROD frame and the directory-listed frame, the survey sampling firm selected
the ROD sample of telephone numbers first. The sampled telephone numbers were compared to
the database of directory-listed telephone numbers. Those telephone numbers that were
directory-listed were removed from the directory-listed frame, prior to the  stratification
described above. The list-assisted samples, corresponding to the four strata above, and the ROD
samples were combined in replicate files. This telephone sample selection did not include
households without home telephones; however, they were represented in the day care sample
component.
                                          4-7

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                            CTEPP Recruitment Protocol
                        Sample Component:  Telephone Sample
                                Purchase telephone sample list for the
                                          target counties
                                Send introductory letters to households
                                            on the list
                                  Conduct telephone screening calls
                                 — Screen for eligibility, using CATI
                                Conduct follow-up calls and schedule
                                              visits
                             Conduct follow-up calls for refusing parents
                                   in an attempt to reverse refusal
                                      Conduct follow-up visits.
                             M eet with the parents, explain the study, and
                                      obtain informed consent.

                                 Optional: Obtain mail-back consent
                                    Conduct random selection for
                                         final participants
Figure 4.2.2   Procedures for Recruiting Telephone Sample Component
                                               4-8

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       Introductory letters and a study brochure were sent to households in the telephone list
that had valid addresses. A Computer Assisted Telephone Interview (CATI) system was
developed to facilitate the screening process. All numbers in the files were called and screened
for eligible subjects.  Children were eligible for this telephone sample component if they were
between the ages of 18 months and 5 years, toilet-trained or able to provide at least one urine
sample, not being breast-fed, and not attending a day care center.  The final participants were
randomly selected from the eligible subjects. Staff visited those households that tentatively
agreed to participate in the study. At these visits, the staff explained the study further and
obtained informed consent.

4.3    Recruitment Results

4.3.1   North Carolina

       Recruitment of subjects for the NC field study was conducted in two phases. Recruitment
of Phase I participants began in four NC counties (Durham, Buncombe, Lee, and Mecklenburg)
in early February 2000, but was suspended on February 29 for four months due to the OMB
2000 Census requirement.  The OMB prohibited other federally-sponsored surveys from
occurring during the period from March to June 2000 while the 2000 U.S. Census was
conducted.). Recruitment of subjects in these counties resumed in July 2000 and continued
through December 2000. Phase I field sampling activities were completed with 48 households
in December 2000. Recruitment of Phase II subjects was conducted for the two eastern NC
counties affected by severe flooding from Hurricane Floyd (Edgecombe and Jones) from
February 26 through March 30, 2001. Twelve additional subjects and their adult caregivers from
the day care center sample  component were enrolled in Phase II. In Jones County, although one
day care center agreed to participate in the study, no parents were willing to participate, because
they were still dealing with the flooding problems from  the hurricane.

       A conservative approach was used to calculate the final response rate. During the
recruitment period, some people refused to be screened and some could not be reached. As a
result, their eligibility status was unknown. A calculated eligibility rate was used to estimate the
number of eligible subjects in this group of status-unknown subjects. This eligibility rate, which
was determined from the known responses, was calculated as the total number of eligibles
divided by the sum of the total number of eligibles and ineligibles. To calculate the final
response rate, the number of eligible subjects who agreed to participate was divided by the
estimated total number of eligible subjects - the total of those eligibles who responded plus the
estimated eligibles.  This approach tends to underestimate the final response rate, because it does
not include the number of status-unknown subjects who might be eligible and agree to
participate in the study but could not be reached.

       Table 4.3.1  summarizes the response rates for the NC study. Overall, 98% of the
recruitment target for day care participants in NC was achieved through enrollment of a total of
63 of 64 target households. Overall, 105% of the targeted number (67 of 64 targeted) of
telephone sample households in NC were enrolled in the CTEPP study. All recruitment
activities for NC were completed by March 30, 2001.
                                           4-9

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       Table 4.3.2 provides the overall recruitment results for NC  for the children who were
recruited at home or at day care.  The final recruitment results for the NC field study led to the
enrollment of 130 children, ranging in age from 20 to 64 months, and their primary adult
caregivers.

Table 4.3.1    Summary of CTEPP North Carolina Response Rates
Sampling Frame
Summary
Child Day Care Component: Child Day Care Centers
(A) Eligible and Recruited Child Day Care Centers
(B) Eligible Child Day Care Centers
(C) Ineligible Child Day Care Centers
(D) Unknown Eligibility
(E) Calculated Response Rate3
13
17
5
10
53%
Child Day Care Component: Day Care Parents
(A) Eligible and Recruited Day Care Parents
(B) Eligible Day Care Parents
(C) Ineligible Day Care Parents
(D) Unknown Eligibility
(E) Calculated Response Rate3
69
85
26
71
50%
Telephone Screening Component
(A) Eligible and Recruited Stay-at-Home Parents
(B) Eligible Stay-at-Home Parents
(C) Ineligible Stay-at-Home Parents
(D) Unknown Eligibility
(E) Calculated Response Rate 3
272
333
6547
2807
58%
         1 Calculated Response Rate, E = (A)/(B + (B/(B + C)) x D)
                                           4-10

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Table 4.3.2   Summary of CTEPP North Carolina Participant Characteristics
Final NC Results
Urban
Rural


Buncombe
Durham
Mecklenburg
Edgecombe
Total Urban
Lee
Jones
Total Rural
Total NC
% of Total
Telephone Sample
Unknown


3

3

1
1
4
6%
Low-income
6
5
2
1
14
4
3
7
21
31%
Mid-income
1
21
15
1
38
3
1
4
42
63%
Subtotal
7
26
20
2
55
7
5
12
67
100%
Day Care Sample
Unknown


1
1
2
1

1
3
5%
Low-income
6
5
11
11
33
5
0
5
38
60%
Mid-income
4
12
3
0
19
3
0
3
22
35%
Subtotal
10
17
15
12
54
9
0
9
63
100%

Total
17
43
35
14
109
16
5
21
130

                                                        4-11

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       Thirteen NC day care centers (eight regular day care and five Head Start) participated in
the study. Sixty-three day care children, day care teachers, and their caregivers successfully
completed the field activities of the study.  Sixty-six stay-at-home children and their caregivers,
successfully completed the field activities of the study. One stay-at-home participant did not
complete the study.  The distribution of low-income and middle/high-income of the NC families
in the telephone sample component was very close to the original sampling design.  However, in
the day care sample, low-income families were over-enrolled, with 60% of the day care sample
classified as low-income.  This over-enrollment of low-income families in the day care sample
occurred because many of the children in the regular day care centers, those not catering
specifically to low-income families through the Federally funded Head Start program, came from
families that were classified as low-income.  Further information on the NC field study can be
found in the NC Recruitment Report (Appendix B) and in our published paper on the CTEPP
sampling design and field methodology (11).

4.3.2   Ohio

       Recruitment of subjects for the OH field study began in January 2001 and was completed
in November 2001. Fifty-eight households were successfully recruited. Table 4.3.3 summarizes
the response rates for the OH study.  For the day care sample component, 91% of the recruitment
target for day care participants in OH was achieved through enrollment of a total of 58 of 64
target households. For the telephone sample component, a total of 165 potentially eligible
households were identified.  Overall, 108% of the target stay-at-home participants were recruited
through enrollment of a total of 69 of 64 target households. All recruitment for OH was
completed in November 2001.

       Table 4.3.4 provides the overall recruitment results for OH, for both the stay-at-home and
day care children. The final recruitment results for the OH field study led to the enrollment of
127 children, ranging in age from 20 to 65 months, and their primary adult caregivers.

       Sixteen OH day care centers (12 regular day care  and 4 Head Start) participated in the
study. Fifty-eight day care children and their caregivers, participated successfully in the field
activities of the study, with simultaneous sampling both at the centers and at the children's
homes. Sixty-nine households in which the children did not attend day care participated
successfully in the field activities of the study, with sampling for the children and their primary
caregivers at the children's homes. The distribution of low-income and middle/high-income
families in the OH telephone sample component is very close to the original sampling design,
with 26% of the stay-at-home participants classified as low-income. However, as in NC, the
low-income families were over-enrolled in the day care sample component, with 50% of the day
care participants classified as low-income. Further information on the OH field study can be
found in the OH Recruitment Report (Appendix B) and in our published paper on the CTEPP
sampling design and field methodology (11).
                                          4-12

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Table 4.3.3   Summary of CTEPP Ohio Participant Response Rates
Sampling Frame
Summary
Child Day Care Component: Child Day Care Centers
(A) Eligible and Recruited Child Day Care Centers
(B) Eligible Child Day Care Centers
(C) Ineligible Child Day Care Centers
(D) Unknown Eligibility
(E) Calculated Response Ratea
16
24
4
5
57%
Child Day Care Component: Day Care Parents
(A) Eligible and Recruited Day Care Parents
(B) Eligible Day Care Parents
(C) Ineligible Day Care Parents
(D) Unknown Eligibility
(E) Calculated Response Ratea
71
100
8
141
31%
Telephone Screening Component
(A) Eligible and Recruited Stay-at-Home Parents
(B) Eligible Stay-at-Home Parents
(C) Ineligible Stay-at-Home Parents
(D) Unknown Eligibility
(E) Calculated Response Rate a
165
191
4598
2449
57%
        1 Calculated Response Rate, E = (A)/(B + (B/(B + C)) x D)
                                         4-13

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Table 4.3.4   Summary of CTEPP Ohio Participant Characteristics
Final OH Results
Urban
Rural


Cuyahoga
Licking
Franklin
Hamilton
Total Urban
Defiance
Fayette
Total Rural
Total OH
% of Total
Telephone Sample
Unknown
1



1


0
1
1%
Low-income
4

7
2
13
2
3
5
18
26%
Mid-income
11
7
13
15
46
4

4
50
72%
Subtotal
16
7
20
17
60
6
3
9
69
100%
Daycare Sample
Unknown


2
1
3
2

2
5
9%
Low-income
10
4
6
9
29


0
29
50%
Mid-income
10

8
0
18
2
4
6
24
41%
Subtotal
20
4
16
10
50
4
4
8
58
100%

Total
36
11
36
27
110
10
7
17
127

                                                       4-14

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       In addition to the field sampling and data collection described above for both NC and
OH, 26 children in OH were videotaped for about two hours in their homes, in order to
supplement the information collected within activity diaries and other observations. Videotaping
started in OH in April 2001 and ended in October 2001. Sixty-nine percent of these 26 OH
children were stay-at-home children; 88% percent of them lived in urban counties; and 38%
percent of them were from low-income families. Fifty percent of the participants were female,
and the children's ages ranged from two to five years.

4.4    Evaluation

       Recruitment strategies included minimizing the burden on participants, ensuring
confidentiality, providing incentives for participation, and using carefully selected and trained
field staff.  Throughout the study, the staff were encouraged to be sensitive to participants'
concerns and to persevere in recruitment.

       The most frequent concern related to participant burden was the lack of center staff or
parent time. Day care teachers in particular were concerned about collection and storage of urine
samples. Several ways of reducing participant burden were used. These included providing
individual training to participants prior to the field sampling, providing assistance for urine
collection at the centers, offering flexible sampling schedules, and providing a project toll-free
telephone number to call for assistance. Additionally, actual contact time between staff and
participants during sampling was kept as short as possible.

       A major concern of some participants, especially of the directors and staff of child day
care centers, was whether individual data would be released to any regulatory agency or to
others. To allay this concern, a Certificate of Confidentiality for the study was obtained from the
National Institute of Mental Health. This Certificate provided legal protection of the privacy of
the individual data. Under this Certificate, the study researchers cannot and will not release any
individual data to anyone, including the courts, without written permission  of the individual.

       To encourage participation, both monetary and non-monetary incentives were offered to
participants. Participating families and child day care centers received $100 to cover their costs
of providing food and other samples. If the children were to be videotaped for about 2 h, an
additional incentive payment of $50 was furnished to the participating household; a $25 gift
certificate for a book or other appropriate item for the classroom was provided to child care
centers. At each visit to homes or centers, field staff brought small age-appropriate gifts for the
participating children. Field staff encouraged participants  to realize that they were performing
important research, and that their participation was valuable. Participants were given a project
T-shirt and pen. All participants received a framed certificate,  acknowledging their contributions,
at the conclusion of field sampling.

       To enhance response rates in the study, user-friendly materials and brochures were
developed. Letters and statements of endorsement were obtained from child care organizations,
such as the National Head Start Organization, and from past pilot study participants. Press

                                           4-15

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releases prepared by the U.S. EPA describing the study were used in the selected areas, and
EPA's principal investigator provided radio interviews. Prior to personal contact with centers
and parents, introductory letters and brochures were sent to them by overnight courier.  Multiple
follow-up calls and personal visits were made by study staff to potential participants.
Throughout, the study staff tried to develop a sense of a research partnership between centers,
teachers, parents, and researchers.

       For the initial telephone screening of potential participants, scripts were developed for
interviewers, so that the screening information could be entered directly into the computer.
Written consent forms for participation and for possible future contact were developed.

4.5    Recommendations

       Study recruitment required far more effort and time than  initially anticipated. In the
future, similar studies should allocate more time and staff resources to the recruitment of
participants.  Recruitment should begin at least four months prior to field sampling.  In addition,
the problem with participant recruitment was exacerbated by the requirement that no contact
could be made with subjects during the 2000 Census, which meant that some participant
recruiting had to occur during the field activity phase of the study.

       Overall, the recruitment methods worked well. However, several participants indicated
that they should receive greater compensation for performing data collection activities that they
found burdensome. In addition, increased monetary incentives should help to increase the
response rates and participant cooperation.

       Recommendations to improve  day care center participation in future studies of this type
include the following:

       Increase the compensation to day care centers, both to the center director and to the
       individual classroom teachers.
•      Prepare a special document that would contain information to ease the concerns of the
       center directors.  This information would address privacy issues and guarantees,
       compensation for time spent on the project activities, a description of day care
       recruitment procedures and study activities, and the assistance that would be provided by
       study staff.
       Design and implement a study web site that would explain the study and also provide a
       means for participants to ask questions.
•      Increase the staff and resources for the project recruitment team, so that more intensive
       recruitment activities, such as follow-up  visit to the day care centers, can be conducted.
•      Increase the compensation to day care parents.
•      Conduct additional in-depth  staff training on subject recruitment and data collection
       activities.
                                           4-16

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•      Have at least two or three staff members attend meetings with parents at the center. This
       would ensure full attention by the staff to all participants and minimize parents' waiting
       time.
       Minimize participant burden as much as possible.

       Although the telephone recruiting worked very well, the advance mailings were not very
effective, as about 65% of the mailed packages were returned as undeliverable.
Recommendations to improve participation for stay-at-home participants in future studies of this
type include the  following:

•      Increase the  compensation to the parents.
•      Mail the  study brochure and introductory letter to the potential participant immediately
       after their initial telephone screening is  completed.
       Minimize participant burden as much as possible.
                                           4-17

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                                      Chapter 5
                                  Field Monitoring
5.1    Overview
       The CTEPP study collected environmental and personal samples as well as supplemental
information to aid in the interpretation and assessment of the children's exposures to pollutants
at homes or day care centers. For children who stayed at home during the day with their primary
caregivers, field samples,  questionnaires, and time-activity/food diaries were collected at their
homes over a 48-h period. For children who attended day care, these above samples were
collected at both their day care centers and homes simultaneously over a 48-h period. Household
and center observation surveys, day care menus and other ancillary information were collected
before or immediately after sampling.

       Field staff collected samples of outdoor play area soil, indoor and outdoor air, indoor
floor dust, and drinking water at homes and child day care centers. The adult caregiver collected
duplicate diets, dermal (hand) wipes, and multiple spot urine samples for themselves and for
their child while at home.  The teachers collected the above samples for day care children while
at day care. If a pesticide application had occurred inside or outside the home or day care center
within the seven days preceding sampling or during the 48-h monitoring period, additional types
of field samples were collected. These additional samples consisted of transferable residues
(PUF roller samples), hard floor surface wipes, and food preparation surface wipes.
Supplemental information was collected through pre- and post-monitoring questionnaires,
house/building characteristic observation surveys, child/adult activity and food diaries, and day
care food menus.  In addition, 26 children were videotaped for about two hours in their homes in
Ohio (OH) to supplement the questionnaires and activity diaries.

       Field sampling started in North  Carolina (NC) in July 2000 and was completed by March
2001. It was completed in the mountain and Piedmont regions by December 2000.  However,
field sampling in the two coastal counties was delayed because of the severe hurricane flooding
that had occurred the previous year.  In this region, field sampling was completed by April 2001.
In OH, there were no significant delays in field sampling activities at participants' homes and/or
day care centers. Field sampling started in late April 2001 in urban counties, Franklin and
Licking, in central OH, because of their close proximity to Battelle's facility in Columbus, OH.
Field sampling was completed in the rest of central, northern and southern regions of the state by
November 2001. Overall, field samples were collected at a total of 130 homes and 13 day care
centers in NC, and at 127  homes and 16 day care centers in OH.
                                           5-1

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5.2    Field Data Collection

       Table 5.2.1 summarizes the field data collection procedures and sampling activities that
took place over a 48-h period at a participant's home and/or day care center.  This approach was
used for both the NC and OH field studies.  There were three field sampling teams (labeled as
teams A, B, and C), with two staff members in each team. Two field sampling teams, A and B,
collected the field data simultaneously at different homes or day care centers.  A third field
sampling team, C, served as a backup team and was responsible for field preparation and training
participants.

       Subjects were scheduled in the same cluster of locations within a county in the same
sampling week. The time needed to complete the field sampling work for each state was about
24 to 30 weeks, depending on the availability of the participants and the weather. One week
prior to each scheduled sampling date, the participants were trained to collect urine, hand wipe
and food samples, and were given instructions for filling out the Child Activity Diary. At that
time, they were given the opportunity to ask additional questions and voice any concerns they
had about their participation.

       For stay-at-home participants, field sampling activities took place at the households of
approximately eight children per week.  These activities occurred over a 48-h period for three
consecutive days.  Typical sampling schedules were: (1) Monday to Wednesday, (2) Tuesday to
Thursday, or (3) Wednesday to Friday. The initial sampling appointments generally ranged from
7 a.m. to 8 p.m; sampling began shortly thereafter and continued for the following 48 h.  In a
given week,  field sampling activities began at four households on Day 1, and each of two field
teams was responsible for the activities at four households per week.

       For day care participants, field sampling activities occurred at one day care center per
week, representing from four to six participating children. Sampling activities also occurred at
the households of these children during that week. Field sampling took place simultaneously
during a 48-h period at each child's day  care center and at her/his home. In a given week, field
sampling activities began at the day care center and at the households of two or three children on
Day 1, and each of two field teams was responsible for the activities at two or three households
per week.

5.2.1  Environmental and Personal Samples

       All field sampling procedures were conducted according to Standard Operating
Procedures (CTEPP-SOPs: 2.10 - 2.27). The list of all CTEPP SOPs is presented in Appendix
A. The multimedia samples that were collected at the children's homes and day care centers are
described below, in Sections 5.2.1.1 through 5.2.1.10.
                                           5-2

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Table 5.2.1    Summary of Field Data Collection Procedures and Sampling Activities over
               a 48-h Period at a Participant's Home and/or Day Care Center
 Sampling Day
Data Collection and Sampling Activity/Task
     Dayl
*•   Obtain signed consent form
*•   Conduct Pre-monitoring Interview
>•   Complete the House/Building Characteristic Observation Survey
>•   Provide instructions on food sample collection, give food containers and cooler,
    ask if it's OK to store the food samples in the participant's refrigerator
>•   Remind parent and teacher—no vacuuming during the 48-hour period (sweeping
    with a broom is OK)
>•   Review the instructions for collecting urine and hand wipe samples
>•   Give the sample collection supplies to the parent and teacher (e.g., urine and
    hand wipe)
*•   Review instructions for recording in the Child Activity Diary
>•   Set up indoor air monitor, mark the location on the sketch, record air log
*•   Set up outdoor air monitor, mark the location on the sketch,  record air log
>•   Take pictures of sampling activities.
Note: Each child's supplies (clean sample containers) are stored in a clean
container with name labeled on top).	
     Day 2
    Complete activities pending since Day 1, if any
    Check outdoor air monitor, record air log
    Check with the parent and teacher for questions about or problems with sampling
    activities
    Videotape child's activities, if applicable	
     Day 3
    Complete activities pending since Day 1, if any
    Unload indoor air samplers, record air log, remove air monitors
    Collect dust sample, vacuum the house (must unload the indoor air samplers first)
    Unload outdoor air samplers, record air log, remove air monitors
    Collect one soil sample (children's usual outdoor play area), mark the location on
    the sketch
    Collect hard floor surface wipe sample
    Collect food preparation surface wipe sample
    Collect PUF roller sample for transferable residues
    Pick up food samples, examine the samples, remove any non-edible materials
    Pick up urine and hand wipe samples
    Pick up the Child Activity Diary
    Conduct Post-monitoring Interview
    Present a Certificate of Appreciation to the parent and teacher
    Confirm the check mailing information with the parent and teacher
    Take pictures of sampling activities
    Videotape child's activities, if randomly selected	
                                              5-3

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5.2.1.1 Outdoor Play Area Soil

       Outdoor play area soil was sampled from the location identified by the teacher or the
primary caregiver as most often used by the children.  A scraping (putty) knife was used to
collect the soil from the top 0.5 cm of soil in a 1 ft2 (0.1 m2) area and placed into a glass jar. If a
play area did not have bare soil or dirt (e.g., grass, sand), the sample was collected near a
subject's sidewalk, driveway, or garden, reasonably close to the identified play area.

5.2.1.2 Indoor Floor Dust

       The high-volume small surface sampler (HVS3; Cascade Stack Sampling Systems, Bend,
Oregon) method was used to  collect floor dust from a 0.76 m2 area of carpet (12). The samples
were collected in the room the child used most often at the residence or day care center. The
initial sampled area was 0.76 m2.  Additional 0.76 m2  areas of the carpet were sampled until a
sufficient amount  of dust was collected for analysis (typically ~1.0 g) The dust sample was
transferred from the Teflon catch  bottle to a glass jar.  A hard floor surface wipe, described
below, replaced the floor dust sample when no carpeted areas were available.

5.2.1.3 Indoor and Outdoor Air

       Outdoor and indoor air was sampled over a 48-h period using filter and a backup XAD-2
trap to collect pollutants in air (8). Briefly, outdoor samples were collected using a Thomas
pump (Model 107CAB18A; Thomas Compressor and Vacuum Pumps, Sheboygan, MI). Indoor
samples were collected using an SKC pump (Model 224-PCXR8; SKC, Inc., Eightyfour, PA).
Flow rates for both pumps were set at a range of 3.9 to 4.1 L/min using a calibrated flow meter.
The inlet port of the sampling cartridge was placed approximately 75 cm above the floor or
ground, at the approximate breathing height of children in the participant age group.  The  URG-
2000 sampling cartridge (University Research Glassware Corp., Chapel Hill, NC) contained a
pre-cleaned quartz fiber filter and an XAD-2 cartridge, to collect the targeted pollutants both in
the vapor phase and condensed on particles < 10 j^m.  Outdoors, the sampling pump and controls
were placed in a Styrofoam cooler, which was housed in a large, plastic doghouse, furnished by
the field staff, to protect the equipment from inclement weather conditions. Indoors,  the
sampling equipment was placed in a Styrofoam cooler and housed in a child's playpen, also
furnished by the field staff, which was covered by a stroller net to protect it from curious
children or pets. Flow rates were recorded at the beginning and end of the sampling period.

5.2.1.4 Drinking Water

       For the day care center component, field staff collected one drinking water sample from
each participating child's home and one sample  from each participating day care center. For the
telephone component, only one drinking water sample was collected from each participating
child's home. These samples were collected in either 1-L or 0.5-L plastic jugs and refrigerated
until shipped to the laboratory.

                                          5-4

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5.2.1.5 Duplicate Plate Food and Beverages

       Duplicate plate samples of the solid and liquid food served to the children (7,8) were
collected for each child during the 48-h sampling period. At home, the adult caregiver provided
the same amount of the same food and beverages, excluding drinking water, consumed by their
child over the sampling period. The teachers provided duplicate servings of food and beverages
consumed by the participating children while at day care. Because all children in a given
classroom were served the same food on the same day, only one duplicate sample was provided
for each classroom on a given day. If a child brought his/her food from home, the home
caregiver was asked to provide a duplicate sample of that food. Composite solid and liquid food
samples were collected separately in 2 L glass containers.  These containers were placed in
provided coolers with blue ice until they were picked up by field staff.

5.2.1.6 Dermal Hand Wipes

       Adult caregivers and day care teachers collected dermal (hand) wipe samples from each
participating child during the 48-h sampling period (8).  Hand wipe samples were taken before
the participants washed their hands. The hand wipe consisted of a gauze pad (SOF-WICK, 10 x
10 cm - 3 ply;  Johnson & Johnson), which was pre-cleaned with dichloromethane (DCM), dried
and wetted with 2 mL of 75% isopropanol in distilled water, and stored in a glass jar. The adult
caregiver removed the pre-wetted gauze pad from the jar and wiped both hands of the child,
according to a  specified procedure (CTEPP-SOP-2.15), then put  the wipe back into the jar.  A
total of four hand wipe samples were collected for each child (two per day, one each before
lunch and dinner).  All hand wipe samples were refrigerated or placed in provided coolers with
blue ice until picked up by field staff.  Adult participants collected their own dermal wipe
samples according to these same procedures.

5.2.1.7 Transferable Residues

       The polyurethane foam roller  (PUF) method (13) was used to collect transferable
residues from indoor floor surfaces (e.g., carpet, vinyl), at homes or at day care centers that had
recent pesticide applications. Transferable residues were sampled at three locations where the
child spent most of their time inside the home or day care center; these locations were not the
same as those that were sampled for carpet dust with the HVS3. The PUF roller apparatus,
having a pre-cleaned, dry PUF sampling cylinder was rolled on the indoor floor surface at a rate
of approximately 10 cm/s for a 2 m distance (1 m up and back). This procedure was repeated,
using the same PUF cylinder, at the other two selected locations. On completion of sample
collection, the  PUF cylinder was wrapped in muffled aluminum foil and placed in a Ziplock bag.
                                          5-5

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5.2.1.8  Food Preparation Surface Wipe

       At homes and day care centers having recent pesticide applications, food surface
preparation wipes were collected from the kitchen counters where food was prepared. The wipe
consisted of a pre-cleaned, gauze pad (SOF-WICK, 10x10 cm - 3 ply; Johnson & Johnson),
which was cleaned with DCM, dried, and then wetted with 2 mL of 75% isopropanol and stored
in a glass jar. Masking tape was used to mark off a 38 x 38 cm (0.14 m2) area of the counter. The
sample was collected by wiping this part of the counter in one direction, folding the wipe in half
and wiping the surface again in the opposite direction, then returning it to the glass jar.

5.2.1.9  Hard Floor Surface Wipe

       At homes and day care centers either having recent pesticide applications or having little
or no carpeted floor surfaces for dust sampling, hard floor surface wipe samples were collected
on indoor floors  (i.e., tile, vinyl, hardwood floors) where the children spent most of their time
The wipe consisted of a gauze pad (SOF-WICK, 10 x 10 cm - 3 ply; Johnson & Johnson), which
was cleaned with DCM, dried, and wetted with 2 mL of 75% isopropanol and stored in a glass
jar. Masking tape was used to mark off a 38 x 38 cm (0.14 m2) area of the floor. The sample was
collected by wiping the designated area of the floor in one direction, then folding the wipe in
half, and wiping the surface again in the opposite direction, then returning the wipe to the jar.

5.2.1.10 Urine

       Spot urine samples were collected from each child over the 48-h monitoring period (8).
The child urinated into a plastic urine collector (bonnet) that was placed under the toilet seat.
The urine was then poured into a 120 mL plastic bottle by the adult. Adult caregivers, when at
home, collected three urine samples per day (first morning void, after lunch, and after dinner or
before bedtime) from their child. Day care teachers collected one urine sample from the child
each day after lunch. All urine samples were refrigerated or placed into provided coolers with
blue ice until picked up by field staff. Adult participants collected their own urine  samples at the
same frequency following similar procedures. Note: The spot urine samples for adults and
children were composited over the 48-h period, with the exception of those collected at homes
with recent pesticide applications, which were stored and analyzed separately.

5.2.2  Supplemental Information

       Supplemental information was collected to help assess the children's exposures to
pollutants in their everyday surroundings. Table 5.2.2 summarizes the types of collected
supplemental data. The same types of forms were used in both the NC and OH studies to collect
these data. The recruitment survey (Form #1) was used to collect the subject's eligibility
information.  This form was administered either by an interviewer, using Computer Assisted
Telephone Interviewing (CATI), or as a Self-Administered Questionnaire. The house/building
characteristics survey described the physical characteristics of the sampled house (Form #2) and

                                           5-6

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Table 5.2.2   Types of Questionnaires, Diaries, or Menus Collected from Participants
Supplemental information
Recruitment survey (Form #1)
House/building characteristics
observation survey (Form #2)
Day care center/building
characteristics survey (Form #3)
Parent pre-monitoring
questionnaire (Form #4)
Day care center pre-monitoring
interview (Form #5)
Parent post-monitoring
questionnaire (Form #6)
Day care center post-monitoring
questionnaire (Form #7)
Child activity diary and food
survey-home group (Forms
#8/AM and #8/PM)
Child activity diary and food
survey-day care group (Forms #9
and #10)
Day care center menus
Types of information
Identify potential participants in a household.
Document the physical characteristics of the house and
identify/inventory possible sources of pollutants.
Document the physical characteristics of the day care
center and identify and inventory possible sources of
pollutants.
Identify the individuals living in the home and describes
the sources and routes of potential exposure to pollutants.
Identify the individuals within the day care
center/classroom and describe the sources and routes of
potential exposure to pollutants.
Provide information on the child's activities and potential
exposure to pollutants over the 48-h sampling period.
Provide information on the child's activities and potential
exposure to pollutants over the 48-h sampling period.
Provide information on the child's activity patterns and
food consumption patterns at home.
Provide information on the child's activity patterns and
food consumption patterns at day care center.
Provide daily dietary menus up to three months prior to
field sampling at a day care center.
                                          5-7

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day care center (Form #3) and collected information for identifying possible sources of
pollutants.  These forms were filled out by the field staff.  Pre- and post-monitoring
questionnaires (Forms #4 to #7) collected general information on the households and day care
centers, as well as specific information on the possible sources of contamination in the children's
surrounding environments, on the usage of pesticides, and on the children's usual activities and
their activities during the 48-h sampling period. Child's activity and food diaries (Forms #8, #9,
#10) documented the information on the child's activities  and food consumption patterns over
the 48-h sampling period. Forms #4 through #10 were filled out by teachers and home
caregivers. Additionally, day care center food menus were collected; these provided information
on the food served at the centers a few weeks before field sampling occurred.

5.2.3   Sample Custody, Field Storage, Shipping, Laboratory Receipt, and Laboratory Storage

       The NC and OH field samples collected by participants during the 48-h sampling period
(food, hand wipe, and urine) were temporarily stored in the provided cooler with ice packs or in
the participant's home refrigerator until collected by the project staff at the end of the sampling
period.  Samples collected from NC were temporarily stored in freezers at or below -10°C at the
NC field office until shipped on dry ice to the Battelle laboratory in Columbus, OH on a weekly
basis. OH field samples were stored in freezers at or below -10°C in the analytical laboratories
until being prepared for analysis.

       Before field sampling, all sample containers were appropriately identified and labeled
with their purpose and with bar codes, then checked by the QC staff at the field office. Just prior
to leaving the field office for a sampling appointment, the field team conducted a sample and
equipment inventory and verified all sample ID labels again. During field sampling, the field
team collected samples  and noted sample conditions on the field sample/data check list. After
the samples were collected and brought back to the field office, they were processed immediately
by the receiving team.  Sample conditions and collection information were recorded into the
CTEPP Tracking System. All labels were checked and samples were transported and stored in
accordance with specifications described in the field sample handling SOPs (CTEPP SOPs 3.10 -
3.12 and 4.10-4.12).

       Strict sample custody procedures were followed throughout the collection and analysis
activities.  A sample chain of custody form was used to document all collection, shipment,
receipt, analysis, processing, and handling steps that each sample underwent as it passed from
one individual to the next.  This record was initiated in the field by the responsible field staff
member and captured the original field collection of the sample, as well as all subsequent
operations performed. Each sample custody record contained, at a minimum,  the following
information: participant identification code, sample ID, the operation performed on the sample
(e.g.,  collection, processing, shipment, receipt, storage, laboratory procedure,  disposal), initials
of the person performing the operation, date on which the operation was initiated, and any
relevant remarks or comments pertaining to the sample. The sample  custody  form was a
hand-written paper record. In addition, a computer-based tracking system was employed,  into
which the scanned information from the sample bar codes, as well as other pertinent information

                                           5-8

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for all collected samples, was entered. At the laboratory, the samples were stored in freezers at
or below -10°C until sample preparation and chemical analysis.

5.2.4   Quality Control

       Quality Assurance/Quality Control (QA/QC) procedures (including pre-field assessment
and field assessment) were implemented throughout the field data collection periods in NC and
OH.

       For pre-field assessment, the sampling equipment was calibrated and the sampling media
were prepared in the laboratory prior to shipment to the field.  Equipment was always tested
when it was set up and when it was removed, to ensure that it performed to specifications
defined in the relevant SOPs. All SOPs and field forms were field tested prior to project
implementation.  SOPs and field forms that were found to be inadequate were revised and
finalized prior to field implementation.

       For field assessment, field duplicates were collected for air samples. The dust, soil, food,
urine, and drinking water samples were bulk samples; different aliquots of the same samples
were used as field duplicates. Field blanks, which underwent the same handling and shipping
procedures as real field samples but did not go through the sample collection step, were
generated in the field to document any possible contamination that might have occurred in field
sample handling and shipping.  Field blanks were prepared and analyzed using the same methods
as field samples.

       Questionnaire results obtained during field visits were reviewed by technicians in the
field.  The final checks for completeness were performed by the QC team members at the field
office.

       Quality assurance orientation for CTEPP NC and OH field data team members included
an overview of program and facility QA requirements, QA requirement documents, field data
record keeping and quality assurance/quality control monitoring. The Battelle Quality
Assurance Officer (QAO) conducted field audits in both the NC and OH  field studies. Field
inspections performed by the Battelle QAO included facility preparation  and sample storage
areas in Durham NC, as well as Day-3 sampling activities.  The QAO also inspected the Battelle
Columbus OH laboratory facilities for adherence to sample  receipt, inspection, storage,
preparation and analysis procedures and oversaw sampling preparation and set-up, Day-1
sampling, and sample preparation performed in Columbus.  In addition, Battelle Field Team
Leaders conducted periodic internal field audits as described in CTEPP SOP 2.25. The  EPA
QAO and EPA Task Order Project Officer (TOPO)  also performed field audits in NC and OH.
There were no non-compliance findings observed during these audits. All recommendations
generated during internal and external audits, technical systems audits (TSAs) and surveillances
were formally documented in laboratory internal records  or in responses to EPA audit reports.
                                          5-9

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5.3    Results

       Results of the NC and OH field data collection activities are summarized in Sections
5.3.land 5.3.2.

5.3.1   North Carolina

       Tables 5.3.1 and 5.3.2 summarize the completeness associated with the collection of field
samples and supplemental information (questionnaires/diaries), respectively, from NC. Field
data collection activities in the NC study achieved greater than 99% completeness for field
samples, 100% for collected questionnaires/diaries, and greater than 99% for data collected on
the questionnaires/ diaries.

       The proposed samples were the ones that the field staff or participants planned to collect
at home or at day care. The  collected samples were the ones that were actually collected in the
field.  Empty liquid food containers were collected in some households, because the adult
caregivers claimed that they or the child participants drank only water. Thus, we did not count
the liquid food samples from these households. Completeness of field data collection was
expressed as a percentage of all samples collected in the field that had data generated in the
laboratory.

       Despite the fact that participants were paid ($25) sufficiently in advance to cover their
cost of duplicate food samples, some participants were still reluctant to provide us these samples.
Solid food samples with the smallest weights  (12.3 g of adult food and 7.76 g of child food) were
collected from the same low-income household.   The  adult caregiver in this household claimed
that they did not consume large amounts of food. Two day care centers provided only snacks
and the children brought their own lunches. Since these lunches were prepared at the children's
homes, the parents were asked to prepare duplicate lunches, which were provided as part of the
at-home food samples.  In one household, the adult participant withdrew from the study after the
Day-1 sampling event because the domestic partner did not want to continue the study.
Therefore, only partial field samples were collected and analyzed. However, a complete set of
questionnaires/ diaries was collected from this household.

       As shown in Table 5.3.2,  100 % of data forms were collected from the participating
households and day care centers, and more  than 99% of the data were collected from these
forms.  Data values labeled  as"incomplete" were treated as missing data, i.e., data that
participants failed to provide and/or which  could not be obtained by re-contacting the
participants. After all attempts were made  to  re-contact the participants in order to obtain
missing information, the any uncollected data were coded as "Missing". Responses of "Don't
Know" (as stated by the participant) or "Refused" were not treated as missing data items because
these were valid responses.
                                           5-10

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Table 5.3.1    Summary of the Completeness of the NC Sample Collection
Sample Description
Hand Wipe Adult
Hand Wipe Child
Drinking Water
Food Preparation Surface Wipe
Hard Floor Surface Wipe
Indoor Air Acid
Indoor Air Neutral
Floor Dust
Liquid Food Adult
Liquid Food Child
Outdoor Air Acid
Outdoor Air Neutral
Transferable Residues
Solid Food Adult
Solid Food Child
Outdoor Play Area Soil
Urine Adult
Urine Child
Proposed
198
284
155
18
46
151
151
154
130a
166a
154
154
18
130
166
143
618, 1901
744, 2831
Collected b
197C
283C
155
18
46
151
151
154
123e
164e
154
155h
18
130
166
143
615, 190h'
739, 2831
Reported
197
283
155
18
46
150d
151
154
122f
163g
154
154
18
130
166
143
615, 190
739, 283
Samples
Voided
0
0
0
0
0
1
0
0
1
1
0
1
0
0
0
0
0
0
Completeness
(%)
100
100
100
100
100
99.3
100
100
99.2
99.4
100
99.4
100
100
100
100
100
100
a Empty jars were collected for the liquid food samples because the participants claimed they drank only water.
 Samples collected include all field samples and field blanks but not laboratory generated QC samples.
c The participant withdrew from the study after day-1 sampling because the domestic partner refused to participate.
d One sample was voided due to pump malfunction (air volume sampled equaled zero).
e Count does not include the empty jars that were collected from households in which the adult and/or child only drank water.
f One sample was spilled during preparation.
g The field staff dropped one liquid food sample while loading the van.
h One extra outdoor air sample was collected to  replace one sample due to pump malfunction.
1 The first number is the number of individual collected urine samples, and the second number is the number of both composite
and non-composite samples.
                                                     5-11

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Table 5.3.2    Summary of the Completeness of the NC Questionnaire/Diary Collection
Form
Number
Form # 1
Form #2
Form # 3
Form #4
Form # 5
Form # 6
Form # 7
Form #8
Form #9
Form# 10
Proposed
130
130
13
130
13
130
63
67
63
63
Collected
130
130
13
130
13
130
63
67
63
63
Reported
130
130
13
130
13
130
63
67
63
63
Completeness for
Collected Forms
(%)
100
100
100
100
100
100
100
100
100
100
Completeness for
Collected Data3
(%)
99.6
99.8
99.8
99.9
99.8
99.3
99.9
99.0
99.7
99.6
a A SAS program was used to calculate the percentage of completeness for the data collected on each form using the
equation Completeness (%) = [(A-B)/A]*100
where   A = Count the total number of filled, valid data variables (not empty)
        B = Count the number of data variables coded as "missing"
                                               5-12

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5.3.2 Ohio

        Tables 5.3.3 and 5.3.4 summarize the completeness associated with the collection of field
samples and supplemental information (questionnaires/diaries), respectively, from OH. Field data
collection activities in the OH study achieved greater than 99% completeness for field samples,
100% for collected questionnaires/diaries, and greater than 94% completeness for the data
collected on the questionnaires/diaries.  In addition, all proposed children (26) were successfully
videotaped at their homes in OH; therefore, 100% completeness was achieved for the videotaping
activities.
Table 5.3.3   Summary of the Completeness of the OH Sample Collection
Sample Description
Hand Wipe Adult
Hand Wipe Child
Drinking Water
Food Preparation Surface
Wipe
Hard Floor Surface Wipe
Indoor Air Acid
Indoor Air Neutral
Floor Dust
Liquid Food Adult
Liquid Food Child
Outdoor Air Acid
Outdoor Air Neutral
Transferable Residues
Solid Food Adult
Solid Food Child
Outdoor Play Area Soil
Urine Adult
Urine Child
Proposed
196
283
157
16
38
150
150
157
127a
171a
156
156
18
127
170
143
634, 194e
756, 266e
Collected b
196
283
157
16
38
150
150
157
122C
170C
156
156
18
127
170
143
634, 194e
756, 266e
Reported
196
283
157
16
38
150
150
157
122
170
155
156
18
127
170
143
634, 194e
756, 266e
Samples
Voided
0
0
0
0
0
0
0
0
0
0
ld
0
0
0
0
0
0
0
Completeness
(%)
100
100
100
100
100
100
100
100
100
100
99.4
100
100
100
100
100
100
100
 Empty jars were collected for the liquid food samples because the participants claimed they drank only water.
b Samples collected include all field samples and field blanks but not laboratory generated QC samples.
c Count does not include the empty jars that were collected from households in which the adult and/or child only drank water.
d One sample was lost during laboratory extraction.
 The first number is the number of individual urine samples collected, and the second number is the number of both composite
and non-composite samples.
                                               5-13

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Table 5.3.4    Summary of the Completeness of the OH Questionnaire/Diary Collection
Form
Number
Form# 1
Form # 2
Form #3
Form #4
Form #5
Form # 6
Form #7
Form #8
Form #9
Form# 10
Proposed
127
127
16
127
16
127
58
69
58
58
Collected
127
127
16
127
16
127
58
69
58
58
Reported
127
127
16
127
16
127
58
69
58
58
Completeness for
Collected Forms
(%)
100
100
100
100
100
100
100
100
100
100
Completeness for
Collected Data3
(%)
98.8
100
99.8
99.9
99.4
99.9
99.6
99.9
95.1
94.0
a A SAS program was used to calculate the percentage of completeness for the data collected on each form using the
equation Completeness, (%) = (A-B)/A*100
where   A = Count the total number of filled, valid data variables (not empty)
        B = Count the number of data variables coded as "missing"
                                               5-14

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5.4    Evaluation

       Several problems were encountered during field sample collection. A frequent problem
encountered at the day care centers was the teachers' difficulty in recording the time-activity
diary for more than one child in a classroom. Although project field staff went over the recording
procedures carefully with the teachers before sampling, the detail required was overwhelming for
some of them. As a result, coverage of the time periods in the child activity diaries was
sometimes incomplete. In future studies, this information should be collected by a more
simplified method.

       Some day care teachers were reluctant to collect and store children's urine samples for
later pickup. Field staff,  therefore, assisted in urine sample collection at day care centers when
requested. Some parents had difficulty understanding the need  and procedures for duplicate plate
food sample collection and the time-activity diary recording procedures. Thorough pre-sampling
training of the adult participants by the field staff was necessary to communicate these
procedures.

       Training  of day care teachers and parents was conducted at the participating day care
centers in  each state. The project staff first consulted with the day care director to identify the best
time for the training (normally in the afternoon before the pickup time of the children). A flyer
about the upcoming CTEPP study meeting was then distributed to all selected parents and
classroom teachers a few days before the scheduled training date. The meeting was designed to
accomplished the following: (1) training of teachers in  the selected  classrooms (often best
accomplished when children were napping); (2) training of parents; (3) meeting with the day care
cook or kitchen staff to explain food collection; and (4) meeting with the day care director to
confirm sampling dates at the day care and to discuss the information needed for pre-monitoring
interview (e.g., day care floor plan and chemical use  information).

       Training  for teachers and parents included a brief study background discussion (e.g., what
the study was about, why it was important, what assistance was needed from them) and a step-by-
step demonstration of the procedures for completing  the child activity diary and  for collecting
urine, hand wipe, and duplicate food samples. Best results were achieved when two to three staff
members were available to train a small group of participants. The training emphasized hands-on
practice. Instruction sheets were handed out to participants after training for use  at home. In
addition to the training, the staff also reviewed the informed consent process with the parent and
asked the parent to complete the recruitment survey if informed consent had been obtained
earlier. After the training was completed, a project T-shirt was  presented to each participant.
Finally the staff confirmed the sampling schedule with  the parent and gave them a money order
for $25 to cover  their cost for providing duplicate food samples.  Similar training was conducted
for the telephone component participants at their homes. Once a subject was determined to be
eligible through the telephone screening process, an appointment was made to meet with the
subject at his/her house to go over the study procedures.
                                           5-15

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       Communication issues in the field were related to problems with directions, equipment
malfunctions, and scheduling changes. Participants were therefore encouraged to contact the field
staff by phone at any time necessary, and all field staff were provided with cellular phones to
facilitate communication with the participants and other staff members.

       In one household, the study was unable to collect outdoor air samples due to no available
electrical outlet for the air pump. In another household, a valid indoor air sample for acid
analysis could not be obtained because the air pump did not operate properly. In one household,
the participant refused to continue the study after Day-1, resulting in incomplete sets of dermal
hand wipes and the child liquid food sample.  The urine samples from three households were
combined incorrectly by the laboratory staff, requiring the collection and processing of make-up
urine samples from these households. One liquid food sample was dropped while field staff were
loading the van.

5.5    Recommendations

       Despite efforts to enhance participant cooperation in collecting food samples (i.e., training
and pre-paying for food samples provided by the participants), there were still some missing food
samples due to participants' reluctance to collect duplicate food samples. This was particularly
problematic when the participants  ate in a restaurant. In some situations, the project staff was able
to purchase the missing food samples from the same restaurant. We recommend an increase in
participant compensation or a decrease in the participant burden (i.e., collecting 24-h instead of
48-h food samples) to improve the participants' cooperation in future studies.

       Some air sampling problems were caused by severe storms or an unreliable power supply
at the sampling site. For future similar studies, we recommend self-powered (i.e., battery-
powered) air pumps for air sampling. A battery backup  system is also a good alternative;
however, such systems can only provide temporary power for approximately 18 h.
                                           5-16

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                                      Chapter 6
                            Sample Analysis Procedures
6.1    Overview
       In the CTEPP study, more than 50 compounds were measured in 11 different types of
sample matrices. Target compounds included two organophosphate (OP) pesticides, two OP
metabolites, three pyrethroid pesticides, one pyrethroid metabolite, 10 organochlorine (OC)
pesticides, three acid herbicides, nine polycyclic aromatic hydrocarbons (PAHs), two phthalates,
three phenols, 17 polychlorinated biphenyls (PCBs), seven PAH metabolites, and one triazine.
(Note that two carbamates, propoxur and bendicarb were originally included on the list of target
pollutants but were later removed due to the study's analytical methods being incompatible for
these pollutants.)  The target pollutants and their metabolites were divided into two groups,
neutral and acidic, based on their chemical properties. According to sample media, various
extraction and cleanup methods were employed for these pollutants/metabolites in each group.
The neutral and acidic pollutants and OP metabolites that were measured in the environmental
and personal samples, except urine, are listed in Tables 6.1.1 and 6.1.2, respectively1. The target
acidic pollutants/metabolites that were measured in urine are listed in Table 6.1.3. With the
exception of creatinine in urine samples, Battelle performed all analyses of CTEPP field
samples. No cross-checks by independent laboratories were used to confirm measured levels in
some samples.

       Both neutral and acidic pollutants as well as OP metabolites were measured in air, indoor
floor dust, soil, hand wipe, hard floor surface wipe, food preparation surface wipe, transferable
residue (PUF), and child food samples.  Adult food samples were analyzed only for acidic
pollutants and OP metabolites. Child food samples from North Carolina (NC) were analyzed for
all neutral and acidic pollutants as well as one OP metabolite.  Child food samples from Ohio
(OH) were analyzed for all the target pollutants and two OP metabolites, except for the PCBs.
Note that one OP metabolite, 3,5,6-trichloro-2-pyridinol (3,5,6-TCP), was measured in the NC
samples and two OP metabolites, 3,5,6-TCP and 2-isopropyl-6-methyl-4-pyrimidinol (IMP),
were measured in the OH samples.  Drinking water samples were analyzed only for atrazine.
Floor surface wipe  samples, when collected to replace floor dust samples from homes without
carpet, were analyzed for neutrals and acids. Additionally, food preparation surface wipe, hard
floor surface wipe,  and transferable residue samples were collected in homes where pesticides
had been applied recently (within seven days of field sampling or during the 48-h monitoring
period).  In NC  and OH, recent pesticide applications were only reported at homes and none at
day care centers. The pesticides applied to the NC homes were all neutral pollutants, therefore,
'Participants were still able to purchase and apply both chlorpyrifos and diazinon at their residences or day care centers in NC
and OH during the study.
                                           6-1

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Table 6.1.1   Neutral Target Pollutants for the CTEPP Study
                                                Target Pollutants
 OP Pesticides

 Chlorpyrifos

 Diazinon

 OC Pesticides

 Aldrin

 alpha-Chlovdane

 gamma-Chlovdane

 p,p '-DDE

 p,p '-DDT

 Dieldrin

 Endrin

 Heptachlor

 Lindane

 Pentachloronitrobenzene

 Pyrethroid Pesticides

 Cyfluthrin

 c/s-Permethrin
trans-Permethrin

PAHs

B enz [a] anthr ac ene

Benzo[a]pyrene

Benzo[&]fluoranthene

Benzo[e]pyrene

Benzo[g/7/']perylene

B enzo [k] fluoranthene

Chrysene

Dibenz[a, /zjanthracene

Indeno [1,2,3 -c J]pyrene

Phthalates

Benzylbutylphthalate

Di-w-butylphthalate

Phenols

Bisphenol-A

Nonylphenol
PCBsa

PCB 44 (2,2',3,5'-tetrachlorobiphenyl)

PCB 52 (2,2',5,5'-tetrachlorobiphenyl)

PCB 70 (2,3',4',5-tetrachlorobiphenyl)

PCB 77 (3,3',4,4'-tetrachlorobiphenyl)

PCB 95 (2,2',3,5',6-pentachlorobiphenyl)

PCB 101 (2,2',4,5,5'-pentachlorobiphenyl)

PCB 105 (2,3,3',4, 4'-pentachlorobiphenyl)

PCB 110 (2,3,3',4',6-pentachlorobiphenyl)

PCB 118 (2,3',4,4',5-pentachlorobiphenyl)

PCB 138 (2,2',3,4,4',5'-pentachlorobuphenyl)

PCB 153 (2,2',4,4',5,5'-hexachlorobiphenyl)

PCB 180 (2,2',3,4,4',5,5'-heptachlorobiphenyl)

Triazine

Atrazine
 Data were reported for 12 PCBs, but not for PCBs 10, 15, 28, 126, and 169. The data for the five PCBs were excluded because the presence of the volatile PCBs 10, 15, and 28
with the presence of closely eluted interference peaks could not provide useful information for Aroclor patterns and none of the PCBs 126 and 169 were detected in the samples.

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Table 6.1.2   Acidic Target Pollutants and Metabolites for the CTEPP Study
 Target Pollutants and Metabolites
 OP Metabolites



 2-Isopropyl-6-methyl-4-pyrimidinol (IMP)a



 3,5,6-Trichloro-2-pyridinol(3,5,6-TCP)



 Acid Herbicides



 Dicamba



 2,4-Dichlorophenoxyacetic acid (2,4-D)



 2,4,5-Trichlorophenoxyacetic acid (2,4,5-T)



 Phenols



 Pentachlorophenol (PCP)
a IMP was measured only in the OH samples.
Table 6.1.3   Target Pollutants and Metabolites Measured in The CTEPP Urine Samples
 Target Pollutants and Metabolites
 OP Metabolites



 2-Isopropyl-6-methyl-4-pyrimidinol (IMP)



 3,5,6-Trichloro-2-pyridinol(3,5,6-TCP)



 Pyrethroid Metabolite



 3-Phenoxybenzoic acid (3-PBA)3



 Acid Herbicides



 2,4-Dichlorophenoxyacetic acid (2,4-D)



 PAH Metabolites



 1 -Hydroxybenz[a]anthracene
3-Hydroxybenz[a]anthracene a



3 -Hydroxybenzo [a]pyrenea



3 -Hydroxychrysene



6-Hydroxychrysenea



6-Hydroxyindeno[ 1,2,3-cd]pyrenea



1-Hydroxypyrene a



Phenols



Pentachlorophenol (PCP)
 These metabolites were measured only in the OH samples.
                                          6-3

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 the wipe and transferable residue samples were only analyzed for neutral pollutants. The
 pesticides applied to the OH homes were either neutral or acidic pollutants.  Therefore, these OH
 samples were analyzed for either neutral or acidic pollutants/metabolites depending upon the
 type of pesticides that had been applied.

        Environmental samples were solvent-extracted using Soxhlet extraction, sonication,
 accelerated solvent extraction (ASE), or refluxing techniques. Most samples required cleanup to
 remove potential interferences. Acidic compounds were derivatized using silylation or
 methylation, depending upon the compound. The specific gravity and creatinine concentrations
 of the urine samples were measured. Urine samples were then hydrolyzed under acidic
 conditions, extracted, derivatized, and cleaned up prior to analysis. Concentrated extracts of all
 samples were analyzed by gas  chromatography/mass spectrometry (GC/MS) in the selected ion
 monitoring mode. Thirty different SOPs, as listed in Appendix A, were used due to the large
 variety of chemicals and matrices that were considered for extraction and analysis. Flow charts
 of the sample preparation and analysis methods used for all the target pollutants/metabolites in
 each sample media are given in Appendix C.

        Quality control (QC) samples were analyzed to assess the overall quality of the analytical
 results. These QC samples included:  (1) field and laboratory duplicates, (2) duplicate GC/MS
 analyses of sample extracts, (3) matrix spike samples (MSSs), and (4) field and laboratory
 blanks. Surrogate recovery standards  (SRSs) were used to assess recovery in every sample.

 6.2    Procedures for North Carolina and Ohio samples

        The same sample analysis procedures were used to determine target pollutants and
 metabolites in environmental and personal samples collected in both NC and OH. As noted in
 Tables 6.1.2 and 6.1.3, a few additional acidic pollutants/metabolites were measured in the OH
 samples, along with the target compounds analyzed in the NC samples.

 6.2.1   Extraction

       Several types of samples required processing prior to extraction.  Dust samples were
sieved, and only the fine dust samples (<150 |^m) were extracted. Any visible small rocks were
removed from the soil samples, and then the sample was mixed with a glass rod before an aliquot
was taken for extraction. Liquid food samples were thawed for 2 to 5 days in a refrigerator prior
to extraction. Solid food samples were thawed (-2-5 days), homogenized with dry ice using a
food processor (Hobart Food Chopper, 33"xl9"x9.5"); and stored in glass jars at < -10°C  for
subsequent extraction. Urine samples were composited for each child and adult over the 48-h
period  at homes, except from homes with recent pesticide applications. The urine samples from
the homes with recent pesticide applications were extracted individually.  If the child attended
day care, the urine samples collected from the day care center were not combined with the urine
samples collected from the child's home. All other samples were processed as received from the
field. Table 6.2.1 summarizes the SRSs and internal standards (ISs) used in the different  types of
samples. The SRSs were added to each sample prior to extraction,  and the ISs were added to the
concentrated sample extracts prior to GC/MS analysis. Table 6.2.2 summarizes the sample

                                           6-4

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preparation methods employed for each type of samples. Detailed preparation and extraction
methods are described in CTEPP SOPs 5.12-5.23 and 5.27-5.29. Typically, all samples were
extracted within 14 days of receipt.
Table 6.2.1    Surrogate Recovery Standards and Internal Standards for Chemical Analysis
Compound Class
Surrogate Recovery Standards
Internal Standards
Neutral Pollutants
OP Pesticide
OC Pesticide
Pyrethroid Pesticide
PAH
Phthalate
Phenol
PCB
Triazine a
p,p'-DDE-d4
p,p'-DDE-d4
p,p'-DDE-d4
Dibenz[a,/z]anthracene-d14
Benzylbutylphthalate-d4
Bisphenol-A-d6
2,2,4,5,5'-Pentachlorobiphenyl-C13
NAb
Diazinon-d10
Phenanthrene-d10,
p,p'-Dibromobiphenyl
p,p'-Dibromobiphenyl
p,p'-Dibromobiphenyl,
Benzo[e]pyrene-d12
p,p'-Dibromobiphenyl
p,p'-Dibromobiphenyl
Phenanthrene-d10
Atrazine-d5
Acidic Pollutants/Metabolites
OP Metabolite
Acid Herbicide
Phenol
NAb
2,4-D-C13
2,4-D-C13
TCP-C13N15
Dicamba-d3
Dicamba-d3, TCP-C13N15
Acidic Pollutants/Metabolites in Urine
OP Metabolite
Pyrethroid Metabolite
Acid Herbicide
PAH Metabolite
Phenol
NAb
2,4-D-C13
2,4-D-C13
2,4-D-C13
2,4-D-C13
TCP-C13N15
Dicamba-d3
Dicamba-d3
Dicamba-d3
Dicamba-d3
 a Atrazine was measured only in drinking water samples.
 bNA denotes not available.
                                           6-5

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Table 6.2.2    Summary of Sample Extraction Methods
   Medium
    Target Chemicals
               Summary of Method
 Air
Neutral pollutants
Soxhlet extract overnight (~14 h) with 80 mL
dichloromethane (DCM); concentrate with Kuderna-Danish
concentrator (KD); if cleanup is needed, solvent exchange to
hexane; Florisil solid phase extraction (SPE) clean up with 18
mL of 15% ethyl ether (EE) in hexane; concentrate with KD.
                 Acidic pollutants/metabolites
                             Soxhlet extract overnight (~14 h) with 80 mL acetonitrile
                             (ACN); concentrate with KD; split sample extract for
                             silylation and methylation. Silylate with 100 ^L MTBSTFA
                             at 70°C for 1 h. Methylate in 50 ^L methanol with etheral
                             diazomethane (diazald, carbitol, 37%  aqueous KOH).
 Dust/Soil
Neutral pollutants
0.5 g of dust or 1-2 g of soil, sonicate for 15 min with 2x10
mL of 10% diethyl ether in hexane; concentrate with KD; if
cleanup is needed, Florisil SPE clean-up with 12 mL of 15%
EE in hexane and 6 mL DCM; concentrate with KD.
                 Acidic pollutants/metabolites
                             0.5 g of dust or 5 g of soil, accelerated solvent extraction
                             (ASE) with acetone at 120° C and 2000 psi for 3 cycles of 10
                             min; concentrate with KD; split sample extract for silylation
                             and methylation. Silylate with 100 ^L MTBSTFA at 70°C
                             for 1 h.  Methylate in 50 ^L methanol with etheral
                             diazomethane; solvent exchange into isooctane; Florisil SPE
                             clean up with 12 mL of 15% EE in hexane and 6 mL DCM;
                             concentrate with KD.
 Drinking
 Water
Atrazine
100 mL of drinking water, CIS SPE with 12 mL of 50%
DCM in hexane; dry with sodium sulfate; filter through
quartz fiber filter; concentrate with KD.
 Solid Food
Neutral pollutants
12 g of solid food, ASE with DCM at 100° C and 2000 psi for
2 cycles of 5 min; dry with sodium sulfate; concentrate with
KD; GPC clean-up with DCM; collect fractions Fl and F2
separately. Concentrate F2 with KD; Fl: solvent exchange
into ACN; ENVI-Carb clean up with 48 mL ACN;
concentrate with KD or TurboVap
                 Acidic pollutants/metabolites
                             8 g of solid food, ASE with methanol at 110°C and 2000 psi
                             for 2 cycles of 5 min; concentrate with KD; extract with 15
                             mL MilliQ water; adjust to pH>12 with 40% KOH; extract
                             with 3x20 mL hexane; discard hexane; acidify to pH<2 with
                             cone. HC1; extract with 3x20 mL DCM; dry with sodium
                             sulfate; concentrate with KD; split extract for silylation and
                             methylation. Silylate with 100 ^L MTBSTFA at 70°C for 1
                             h. Methylate in 50 ^L methanol with etheral diazomethane.
                                                  6-6

-------
Table 6.2.2    Summary of Sample Extraction Methods (cont.)
   Medium
    Target Chemicals
               Summary of Method
 Liquid Food
Neutral pollutants
30 mL of liquid food, reflux in 60 mL DCM for 1.5 h, filter,
extract with 2x20 mL DCM, dry with sodium sulfate, filter,
concentrate with KD, filter extract on micron acrodisc PTFE
filter, GPC clean-up with DCM, collect fractions Fl and F2
separately. Concentrate F2 with KD. Fl: solvent exchange
into ACN; ENVI-Carb clean up with 48 mL ACN;
concentrate with KD or TurboVap
                 Acidic pollutants/metabolites
                              10 mL of liquid food, extraction method 1 or 2:
                             Method 1 for non-clear liquid food: ASE with methanol at
                              110°C and 2000 psi for 2 cycles of 5 min; concentrate with
                             KD for subsequent liquid-liquid partitioning as method 2.
                             Method 2 for clear liquid food: liquid-liquid partitioning with
                              10 mL milliQ water and 10 mL sample, filter through quartz
                             filter; add up to 15 mL MilliQ water to resulting extract from
                             either method 1 or 2; adjust to pH>12 with 40% KOH;
                             extract with 3x20 mL hexane; discard hexane; acidify to
                             pH<2 with concentrated HC1; extract with 3x20 mL DCM;
                             dry with sodium sulfate; concentrate with KD; split extract
                             for silylation and methylation. Silylate with 100 ^L
                             MTBSTFA at 70°C for 1 h.  Methylate in 50 ^L methanol
                             with etheral diazomethane.
 Dermal, Floor
 Surface,
 Food
 Preparation
 Wipes
Neutral pollutants
Soxhlet extract overnight (-14 h) with 300 mL DCM; filter
on quartz fiber filter; concentrate with KD, if needed, Florisil
SPE clean-up with 18 mL of 15% EE in hexane; concentrate
with KD.
                 Acidic pollutants/metabolites
                             ASE with acetonitrile (ACN) at 120° C and 2000 psi for 3
                             cycles of 5 min; concentrate with KD; split sample extract for
                             silylation and methylation. Silylate with 100 ^L MTBSTFA
                             at 70°C for 1 h. Methylate in 50 ^L methanol with etheral
                             diazomethane. If needed, Florisil SPE clean-up with 18 mL
                             of 15% EE in hexane; concentrate with KD.
 Urine
Acidic pollutants/metabolites
1 mL urine: hydrolysis with 100 ^L cone. HC1 at 80 °C for 1
h; add 1 mL of 20% NaCl solution,  1 mL chlorobutane (CB),
and 10 nL of internal standard; mix and centrifuge; remove
800 nL of the extract and silylate with 100 ^L MTBSTFA at
70°C for 1 h; transferred to GC vial.
10 mL urine: hydrolysis with 500 uL cone. HC1 and 1 mL of
CB at 80°C for 1 h; add 10 mL of 20% NaCl solution and
extract with 3x10 mL DCM; concentrate with KD; methylate
in 50 |^L methanol with etheral diazomethane.
                                                  6-7

-------
Prior to GC/MS analysis, two different derivatization methods, methylation and silylation, were
used for the acidic compounds. Dicamba, 2,4-D, 2,4,5-T, 3-PBA, and hydroxy-PAHs were
methylated using diazomethane. 3,5,6-TCP and IMP were silylated using
N-(t-butyldimethylsilyl)-N-methyl-trifluoroacetamide (MTBSTFA). Pentachlorophenol (PCP)
could be derivatized by methylation or silylation, and in early analyses the silylated derivative
was used.  However,
interferences were seen in some dust samples. Therefore, PCP was analyzed in most samples as
the methyl derivative. After cleanup and derivatization, sample extracts were concentrated to 1
mL and spiked with internal standards, as shown in Table 6.2.2. Extracts were stored in a freezer
at < -10 °C until analysis. Typically, all samples were analyzed within 14 days of extraction.

6.2.2  Sample Analysis

       All concentrated sample extracts and standard solutions were analyzed by 70 eV electron
impact (El) GC/MS.  The Hewlett-Packard GC/MS was operated in the selected ion monitoring
mode. Data acquisition and processing were performed with a ChemStation data system. The
GC column was a DB-5  fused silica capillary (60 m x 0.32 mm, 0.25 |^m film thickness). Helium
was used as the GC carrier gas. The GC/MS operation  conditions used for different types of
samples are summarized in  Table 6.2.3. Peaks monitored were the molecular ion peaks and their
associated characteristic fragment ion peaks.  Identification of the target compounds was based on
their GC retention times relative to their internal standard and relative abundance of the
monitored ions. Quantification of target compounds was based on comparisons of the integrated
ion current response of the target ions to those of the respective internal standards using average
response factors for the target compounds, generated from standard calibrations.  The response
factor was calculated using  the following equation:

       Rf=(As/Als)x(Cls/Cs)
where
       As = area of quantification ion for target pollutant in the standard solution
       Ais = area of quantification ion for internal standard in the standard solution
       Cis = concentration of internal standard in the standard solution
       Cs = concentration of target pollutant in the standard solution
       Rf = response factor of target pollutant

The target pollutant concentration in the sample was calculated using the following equation:

       Cs = (As/Als)x(Cls/Rfavg)
where
       As = area of quantification ion for target pollutant in the sample extract
       Ais = area of quantification ion for internal standard in the sample extract
       Cis = concentration of internal standard in the sample extract
       Cs = concentration of target pollutant in the sample extract
       Rfavg= average response factor of target pollutant
                                           6-8

-------
Table 6.2.3   Summary of GC/MS Operating Conditions
   Medium
         Target Chemicals
         Summary of Method
 Air, Dust,
 Soil, Solid
 Food, Liquid
 Food, Dermal
 Wipes, Floor
 Surface
 Wipes, Food
 Preparation
 Wipes,
 Transferable
 Residue
OP and OC pesticides, pyrethroid pesticides,
PAHs, phthalates, and phenols
Injection volume: 1 ^L
Solvent delay: 7 min
Inlet: 290 °C
Oven: 70°C (2 min hold), 15°C/minto 150°C,
 6°C/minto290°C
Transfer line: 290 °C
PCBs
Injection volume: 1 ^L
Solvent delay: 7 min
Inlet: 290 °C
Oven: 70°C (2 min hold), 20°C/min to 150°C,
4°C/min to 290 °C (4 min hold)
Transfer line: 290 °C
                Acid herbicides and PCP
                                        Injection volume: 1 ^L
                                        Solvent delay: 7 min
                                        Inlet: 290 °C
                                        Oven: 90 °C, 8°C/minto 290 °C
                                        Transfer line: 290 °C
                OP metabolites (3,5,6-TCP and IMP), and
                PCP
                                        Injection volume: 1 ^L
                                        Solvent delay: 7 min
                                        Inlet: 290 °C
                                        Oven: 90 °C, 8°C/minto 290 °C
                                        Transfer line: 290°C
 Drinking
 Water
Triazine (atrazine)
Injection volume: 1 \\L
Solvent delay: 7 min
Inlet: 290 °C
Oven: 70 °C, 20°C/minto 190°C, 4°C/minto
215°C, 27°C/minto290°C
Transfer line: 290°C
 Urine
Pyrethroid metabolite (3-PBA), 2,4-D, PAH
metabolites, and PCP
Injection volume: 1 ^L
Solvent delay: 7 min
Inlet: 290 °C
Oven: 90 °C, 8°C/minto 290 °C (5 min)
Transfer line: 290 °C
                OP metabolites (3,5,6-TCP, IMP)
                                        Injection volume: 1 ^L
                                        Solvent delay: 7 min
                                        Inlet: 290 °C
                                        Oven: 90 °C, 8°C/minto 290 °C
                                        Transfer line: 290 °C
                                                5-9

-------
6.2.3   Supplemental Measurements on Urine Samples

       Creatinine concentration and specific gravity were measured in the urine samples so that
comparisons of urine metabolite concentrations could be made from sample to sample on a
common basis, considering that the dilution level of individual urine samples can vary greatly
depending on the individuals' muscle activity, kidney efficiency, and the amount of water that
they ingest. Creatinine is a byproduct of the breakdown of creatine and phosphocreatine, an
energy storage compound in muscle. The more active the person, the greater the amount of
creatinine excreted in the urine. The specific gravity is the weight of a known amount of urine
compared to the weight of an equal amount of water.  Specific gravity measures the kidney's
ability to concentrate or dilute urine in relation to plasma.  Because urine is a solution of minerals,
salts, and compounds dissolved in water, the specific gravity of urine is greater than 1.  Urine
specific gravity increases as the urine becomes more concentrated.

       Aliquots (10 mL each) of composited urine samples were removed for creatinine analysis.
The non-composited urine samples were not analyzed for creatinine, because of the small sample
size per void and the need to analyze the urine samples for parent compounds or metabolites.  The
urine sample aliquots were sent to the Ohio State University Clinical Laboratory for creatinine
analysis. The method employed was the Jaffee Picric Acid, colorimetric method.  Specific
gravity measurements were performed on all composited and non-composited urine samples,
using reagent strips purchased from Lab Essentials Inc.  (Monroe,  GA), Urine Reagent Strips
(9-parameter). The reagent end of the strip was dipped into the urine sample. After one minute,
the color of the test strip was compared to the standard color chart, and the specific gravity value
was recorded.

6.2.4   Method Evaluation

6.2.4.1  Instrument Performance

       The GC/MS system was calibrated with perfluorotributylamine according to the
manufacturer's instructions, to  verify that acceptable performance criteria were achieved, before
analyzing any standard solutions and/or samples. A multi-point calibration curve (typically five
points) was constructed with calibration standards for each sample set. An average response
factor (Rf) of each target pollutant was generated from the multi-point calibration curve.  The
percent relative standard deviation (% RSD) of the calculated Rf values in all the calibration
solutions was required to be within ± 25%.  The calculated values of the standard solutions were
checked to ensure that the relative percent difference (%RPD) was within ± 30% of the expected
values.  If the % RSD values of some compounds were greater than ± 25%, the GC/MS system
was checked to determine the sources of this variation.  Appropriate corrective  actions (i.e.,
cleaning the source) were taken. The calibration standard solutions and the sample set were then
re-analyzed, and another multi-point calibration curve was generated for quantification.
                                           6-10

-------
6.2.4.2 Method Performance

6.2.4.2.1  North Carolina Method precision was evaluated based on the results from duplicate
samples and duplicate GC/MS analyses. One field duplicate air sample for neutral analysis, and
one for acid analysis, were collected in the NC study.  Duplicate NC samples for dust, soil, food
and urine were duplicate aliquots of these samples. Duplicate wipe and transferable residue
samples were not obtained because it was not feasible to obtain true duplicate samples for these
sample media. For example, once a surface has been wiped or sampled with a PUF roller, there is
no other equivalent surface from which a duplicate sample can be obtained. A summary of the
mean and standard deviation (SD) values of the %RPD of the duplicate NC samples are given in
Tables 6.2.4 through  6.2.6.  For neutral pollutants in the multimedia samples, the mean %RPD
ranged from 0 to 26%, except for PCB 52 for which the mean %RPD ranged from 0 to 36%. The
mean %RPD for acidic pollutants/metabolites ranged from 0 to 16%. Duplicate GC/MS analyses
were performed on randomly selected sample extracts for all sample media (the same sample
extract was analyzed twice by GC/MS).  Results of the mean and SD for the %RPD of the
duplicate GC/MS analyses are summarized in Tables 6.2.7 to 6.2.9. The mean %RPD ranged
from 0 to 9% for all neutral and acidic pollutants/metabolites.

      Overall method accuracy was evaluated by measuring the recoveries of the MSSs and
SRSs that had been spiked onto all field samples. Recoveries of the MSSs for dust, soil, liquid
food, solid food, and urine samples were obtained from different aliquots of the corresponding
spiked and non-spiked samples. Recoveries of the MSSs of air, wipe, and PUF samples were
obtained from the spiked blank sample media. The mean and SD values of the recovery data
from the NC matrix spike samples are summarized in Tables 6.2.10 to 6.2.12. Typical spiking
levels of MSSs and SRSs by matrix are shown in these Tables. With few exceptions, satisfactory
recoveries were obtained for most target pollutants/metabolites in all types of samples. Mean
recoveries ranged from 54±6.5 to 130±6.5% for neutral pollutants. Mean recoveries ranged from
64±16 to  99±23% for acidic pollutants/metabolites. High background levels of the two  phthalates
were found in the non-spiked blank sample media as well as in the field samples. Consequently,
the spiked levels of the two phthalates were not high enough in most of the matrix spike samples
to provide satisfactory recovery data. For the same reason, satisfactory recoveries for target OP
pesticides and PAHs could not be obtained in a few dust and soil samples. Interference  peaks
were observed for bisphenol-A, cyfluthrin, and c/'s-permethrin. Recovery data for these samples
were not included in calculating the mean and SD as noted in Table 6.2.10. A ^ram'-permethrin
standard was not available at the early stage of the NC field study, thus some of the matrix spike
samples did not contain this compound.

      Recovery data of SRSs are summarized in Tables 6.2.13 to 6.2.15.  Quantitative
recoveries for the SRSs includingp,p '-DDE-d4, dibenz[a,/z]anthracene-d14, PCB101-C13, and 2,4-
D-C13 were obtained in most NC field samples.  Recoveries for SRSs ranged from 56±9.5  to
120±18% for neutral pollutants and from 75±11 to 91±18%for acidic pollutant, 2,4-D-C13.
Interference peaks were observed for benzylbutylphthalate-d4 and bisphenol-A-d6, in some air,
dust, soil, and wipe samples. Therefore, satisfactory recoveries were not obtained.

      Field blanks and laboratory method blanks were used to assess background contamination
from field sample handling and laboratory sample processing. Results  of the neutral and acidic

                                          6-11

-------
pollutants/metabolites in field blanks and laboratory blanks from NC are summarized in Tables
6.2.16 to 6.2.17.  Typically, field blanks were taken every other week during the sampling periods
in each state.  Field blanks for air, wipe, and PUF samples were unspiked sampling cartridges,
precleaned wipes, and precleaned PUFs respectively. These cartridges, wipes, and PUFs were
taken to the field and treated the same way as field samples, but were not exposed.  Field blanks
for dust/soil and liquid/solid food were empty containers that were used for collecting the
respective samples and went through the same field handling procedures as field samples.
Because the same kind of wipes was used for dermal wipes, floor surface wipes, and food
preparation wipes, all the wipe samples shared the same field blanks.  Dust and soil  samples
shared the same field blanks, because the same type of containers was used for these samples.

       The reported median and SD values in Tables 6.2.16 and 6.2.17 were generated from the
combined field blanks and laboratory blanks data.  These tables do not include the
pollutants/metabolites that were not detected in the blanks from all sample media. If the target
pollutant/metabolite was detected in some of the blanks, the non-detected blank results were
replaced by the method detection limit (MDL) divided by the square root of two for all media,
except liquid food, in the determination of the median and SD values. Non-detected results for
liquid food blanks were replaced by the MDL divided by ten. With few exceptions, most target
pollutants/metabolites were not detected in the field blanks  and laboratory method blanks.  The
median values of these pollutants/metabolites were below or close to the method detection limits
in these blanks.  Measurable amounts of bisphenol-A in wipe samples, and of the two phthalates
in all sample media, were found in the field blanks and laboratory method blanks in NC.
Therefore, background correction was performed for these samples, before the data were used for
the statistical analysis discussed in Chapter 8 of this report.  Two PUF method blanks (11% of all
PUF samples) were analyzed for neutrals; one did not contain any detectable target pollutants
except for the two phthalates. The other PUF blank contained few PCBs; visible particles were
observed in this blank PUF, which were probably due to contamination in the laboratory.  There
were 29 (6.1% of total urine samples) method blanks, and 12 (2.5% of total urine samples) field
blanks, which were collected and analyzed for target pollutants/metabolites in urine. None of the
urine blanks had any detectable target compounds.

       Only one target pollutant,  atrazine, was measured in the drinking water samples, thus all
QC data for the drinking water samples are  summarized in Table 6.2.18.  There was no  SRS for
the water samples, because atrazine-d5 was used as an internal standard.  Overall method
precision was very good; the mean of the %RPD of duplicate water samples was 2.2 ± 3.5%, and
a similar result was obtained from the duplicate GC/MS analyses.  Average recovery of the matrix
spike samples was 84 ± 20%. Trace amounts of atrazine were found in some of the  blank
samples.
                                          6-12

-------
Table 6.2.4    Results for Duplicate Samples for Neutral Pollutants - North Carolina
Pollutant Air Dust/Soil Liquid Food Solid Food
Number of QC samples
Percent of field samples
2
0.7
30
10
10
6.1
6
3.6
Relative Percent Difference, %
OP Pesticides
Chlorpyrifos
Diazinon
OC Pesticides
Aldrin
a/p/?a-Chlordane
gamma-Chlordane
p,p'-DDE
p,p'-DDT
Dieldrin
Endrin
Heptachlor
Lindane
Pentachloronitrobenzene
Pyrethroid Pesticides
Cyfluthrin
CM-Permethrin
frara-Permethrin
PAHs
Benz[a]anthracene
Benzo[a]pyrene
Benzo[fe]fluoranthene
Benzo[e]pyrene
Benzo [gfe ]perylene
Benzo[£]fluoranthene
Chrysene
Dibenz[a, /7]anthracene
Indeno [1,2,3 -crf|pyrene
Phthalates
Benzylbutylphthalate
di-«-Butylphthalate
Phenols
Bisphenol-A
Nonylphenol
PCBs
PCB44
PCB52
PCB70
PCB77
PCB95
PCB 101
PCB 105
PCB 110
PCB 118
PCB 138
PCB 153
PCB 180
mean*
24
b

-
1.3
9.3
-
-
-
-
4.2
7.4
-

-
-
-

-
-
-
-
-
-
-
-
-

6.0
13

-
-

-
36
-
-
7.8
7.6
-
-
-
-
-
-
SD
NA
-

-
NA°
NA
-
-
-
-
NA
NA
-

-
-
-

-
-
-
-
-
-
-
-
-

NA
NA

-
-

-
NA
-
-
NA
NA
-
-
-
-
-
-
mean
14
5.4

1.2
4.2
4.3
1.7
2.8
3.0
0.22
1.5
-
-

0.63
3.1
4.6

21
14
14
17
16
9.9
15
9.6
13

23
20

2.3
1.1

0.04
1.5
0.67
-
1.8
1.9
1.2
0.71
1.2
0.04
0.51
0.76
SD
27
8.9

3.1
5.6
5.9
4.2
7.6
9.3
0.85
3.3
-
-

1.59
4.9
6.1

23
12
11
14
15
8.0
15
12
11

25
26

4.6
4.2

0.15
3.4
2.2
-
6.9
6.4
4.5
1.8
2.5
0.14
1.5
2.9
mean
-
-

-
-
-
-
-
-
-
-
-
-

-
1.3
5.2

0.76
-
-
-
-
-
0.19
-
-

23
18

2.8
1.4

-
-
-
-
-
-
-
-
-
-
-
-
SD
-
-

-
-
-
-
-
-
-
-
-
-

-
2.4
9.7

1.7
-
-
-
-
-
0.42
-
-

23
9.4

3.2
3.1

-
-
-
-
-
-
-
-
-
-
-
-
mean
-
-

-
-
-
4.4
0.25
-
-
-
2.9
-

-
2.5
8.9

4.5
3.6
5.3
1.9
-
0.59
3.2
-
-

26
18

2.9
-

-
-
-
-
-
-
-
-
-
-
-
-
SD
-
-

-
-
-
6.9
0.44
-
-
-
5.0
-

-
3.4
15

4.0
1.8
0.45
0.95
-
0.51
1.7
-
-

26
11

2.5
-

-
-
-
-
-
-
-
-
-
-
-
-
 * Only one duplicate air sample was collected
 b - denotes that the target pollutant was below
 0 NA denotes not applicable.
for neutral pollutants; the reported mean value of RPD is the RPD value of the duplicate samples.
detection limit in all duplicate samples.
                                                      6-13

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Table 6.2.5   Results for Duplicate Samples for Acidic Pollutants/Metabolites -
                North Carolina
Pollutant
Number of QC samples
Percent of field samples
Air
2
0.7
Dust/Soil
20
6.7
Liquid Food
28
9.8
Solid Food
44
15
Relative Percent Difference, %
OP Metabolites
3,5,6-TCP
Acid Herbicides
Dicamba
2,4-D
2,4,5-T
Phenols
PCP
mean*
16

b
-
-

0.69
SD
NA°

-
-
-

NA
mean
8.0

-
2.6
-

4.8
SD
8.9

-
5.6
-

4.4
mean
5.8

-
0.33
-

-
SD
7.0

-
1.2
-

-
mean
7.7

-
4.7
0.47

1.3
SD
6.5

-
7.7
2.1

3.5
* Only one air duplicate sample was collected for acidic pollutants; the reported mean value of RPD is the RPD for the duplicate samples.
b - denotes that the target pollutant was below detection limit in all duplicate samples.
° NA denotes not applicable.
Table 6.2.6    Results for Duplicate Samples for Urine Analysis - North Carolina
Pollutant
Number of QC samples
Percent of field samples
Urine |
26
5.5
Relative Percent Difference, %
OP Metabolites
IMP
3,5,6-TCP
Acid Herbicides
2,4-D
PAH Metabolites
l-Hydroxybenz[a]anthracene
3-Hydroxychrysene
Phenols
PCP
mean
_a
7.9

2.5

4.0
-

8.2
SD
-
7.3

3.2

14
-

8.5
* - denotes that the target pollutant was below detection limit in all duplicate samples.
                                                   6-14

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Table 6.2.7  Results for Duplicate Analyses of the Same Sample Extract for Neutral Pollutants - North Carolina
Pollutant
Number of QC samples
Percent of field samples
Air
PCB
24
7.9
Others
28
9.2
Dust/Soil
PCB
38
13
Others
34
11
Wipes
PCB
36
12
Others
42
15
Liquid Food
PCB
34
21
Others
34
21
Solid Food
PCB
30
18
Others
26
16
PUF
PCB
-
0.0
Others
2
11
Relative Percent Difference, %
OP Pesticides
Chlorpyrifos
Diazinon
OC Pesticides
Aldrin
a/pfcz-Chlordane
gamma-Chlordane
p,p'-DDE
p,p'-DDT
Dieldrin
Endrin
Heptachlor
Lindane
Pentachloronitrobenzene
Pyrethroid Pesticides
Cyfluthrin
cu-Permethrin
fram-Permethrin
PAHs
Benz[a]anthracene
Benzo [a]pyrene
Benzo[fe]fluoranthene
Benzo [e]pyrene
Benzo [gfe]perylene
Benzo [£]fluoranthene
Chrysene
Dibenz[a,/7]anthracene
Indeno [ 1 , 2, 3 -c
-------
Table  6.2.7   Results for Duplicate Analyses of the Same Sample Extract for Neutral Pollutants - North Carolina (cont.)
Pollutant
Phthalates
Benzylbutylphthalate
di -«-Butylphthalate
Phenols
Bisphenol-A
Nonylphenol
PCBs
PCB44
PCB52
PCB70
PCB77
PCB95
PCB 101
PCB 105
PCB 110
PCB 118
PCB 138
PCB 153
PCB 180
Air
mean
7.6
3.9

6.5
0.71

0.47
4.6
0.86
•
2.2
1.4

1.7
0.79
-
0.45
0.10
SD
10
6.4

8.9
2.7

1.6
6.2
2.6
•
3.8
2.6
-
3.1
2.8
-
1.6
0.35
Dust/Soil
mean
8.9
4.7

1.2
2.7

0.54
1.2
-

0.69
0.99
-
1.7
2.4
1.3
2.1
1.3
SD
11
4.1

2.7
8.5

2.3
3.1

-
2.5
2.5

3.4
5.3
3.4
6.1
3.7
Wipes
mean
7.3
3.1

8.6
1.3

0.46
1.3
0.24
•
0.59
0.35

0.60
0.18
0.13
1.4
0.25
SD
8.0
3.2

7.7
4.4

2.0
4.4
1.0

1.7
1.5
-
1.9
0.64
0.56
3.9
0.93
Liquid Food
mean
2.0
3.3

3.1
0.14

-
-

-
-
-

-
-
-

-
SD
1.6
5.7

3.3
0.59

-
-

•
-
-

•
-
-

-
Solid Food
mean
5.8
3.6

4.1
0.1

.
-
-
-
0.03

-
-
-

-
-
SD
7.4
6.8

2.6
0.34

-
-

-
0.12
-

-
-
-
-
-
PUF
mean
3.1
4.4

5.4


-
-

•
-
-

•
-
-

-
SD
NA
NA

NA
NA

-

-
-
-

-
-
-

-
-
" Only one duplicate GC/MS analysis for OC, OP, PAH, PE, Phenols, and PY performed on the PUF sample; the reported mean value of RPD is the RPD of the duplicate GC/MS analyses.
b NA denotes not applicable.
° - denotes that the target pollutant was below detection limit in all duplicate GC/MS analyses.
                                                                       6-16

-------
Table 6.2.8   Results for Duplicate Analyses of the Same Sample Extract for Acidic
              Pollutants/Metabolites - North Carolina
Pollutant
Number of QC
samples
Percent of field
CQmpl^c
Air
silylate
22
7.3
methylate
20
6.6
Dust/Soil
silylate
40
13
methylate
32
11
Wipes
silylate
21
8.2
methylate
22
8.6
Liquid Food
silylate
16
5.6
methylate
22
7.7
Solid Food
silylate
34
12
methylate
38
13
Relative Percent Difference, %
OP Metabolites
3,5,6-TCP
Acid Herbicides
Dicamba
2,4-D
2,4,5-T
Phenols
PCP
mean
5.7

."
2.4
0.12

7.9
SD
6.0

-
7.0
0.37

6.2
mean
4.1

2.3
1.6
-

5.3
SD
4.5

7.0
2.7
-

4.7
mean
5.5

-
0.89
-

1.5
SD
4.3

-
2.9
-

2.7
mean
1.5

-
-
-

-
SD
1.7

-
-
-

-
mean
3.1

0.99
2.8
-

0.15
SD
3.6

2.1
4.0
-

0.64
* - denotes that the target pollutant was below detection limit in all duplicate GC/MS analyses.
Table 6.2.9   Results for Duplicate Analyses of the Same Sample Extract for Urine
              North Carolina
 Pollutant
                                                  Urine
Number of QC samples
Percent of field samples
54
11
Relative Percent Difference, %
OP Metabolites
IMP
3,5,6-TCP
Acid Herbicides
2,4-D
PAH Metabolites
l-Hydroxybenz[a]anthracene
3-Hydroxychrysene
Phenols
PCP
mean
1.1
3.9

4.6

1.3
0.44

3.7
SD
3.9
2.8

5.4

2.7
1.4

3.7
                                           6-17

-------
Table 6.2.10  Results for Matrix Spike Samples for Neutral Pollutants - North Carolina
 Pollutant
                           Air
                                           Dust/Soil
                                                             Wipes
Liquid Food
                                                                                                 Solid Food
                                                                                                                     PUF
Typical spike level, ng
Number of QC samples
Percent of field samples
50
15
4.9
20
19
6.4
20
21
7.3
50
10
6.1
50
8
4.8
50
2
11
Percent Recovery, %
OP Pesticides
Chlorpyrifos *
Diazinon b
OC Pesticides
Aldrin
a/pfcz-Chlordane
gamma-Chlordane
p,p'-DDE
p,p'-DDT
Dieldrin
Endrin °
Heptachlor
Lindane
Pentachloronitrobenzene
Pyrethroid Pesticides
Cyfluthrind
cw-Permethrin e
frara-Permethrin f
PAHs
Benz[a]anthracene
Benzo [a]pyrene
Benzo[fe]fluoranthene
Benzo [e]pyrene
Benzo [gfe]perylene
Benzo [£]fluoranthene
Chrysene
Dibenz[a,/7]anthracene
Indeno [1,2,3 -c
-------
Table 6.2.10  Results for Matrix Spike  Samples for Neutral Pollutants - North Carolina (cont.)
Pollutant
Phthalates
Benzylbutylphthalate E
di-«-Butylphthalateh
Phenols
Bisphenol-A '
Nonylphenol'
PCBs
PCB44
PCB52
PCB70
PCB77
PCB95
PCB 101
PCB 105
PCB 110
PCB 118
PCB 138
PCB 153
PCB 180
Air
mean

-

91
100

92
91
93
100
89
92
100
97
99
100
97
110
SD
-
•

17
16

14
14
11
12
13
13
13
14
13
16
13
16
Dust/Soil
mean
110
100

69
89

79
81
80
88
74
78
87
81
86
86
85
89
SD
28
29

12
22

13
16
13
15
12
12
18
17
17
17
16
21
Wipes
mean

-

110
120

100
100
110
110
100
100
120
110
120
110
120
120
SD
-.
•

27
16

16
16
17
19
17
17
22
19
23
22
21
27
Liquid Food
mean
74
61

130
130

90
88
95
100
86
91
99
100
100
96
96
97
SD
24
25

10
9.5

13
11
12
16
13
14
18
12
16
18
17
19
Solid Food
mean
67
61

100
125

74
75
81
89
78
79
82
77
86
73
74
78
SD
13
1.7

17
14

12
13
18
8.7
23
18
9.7
12
20
9.4
8.8
16
PUF
mean

-

80
85

86
87
91
98
81
91
100
97
97
100
97
110
SD
-
•

30
31

7.8
5.5
8.4
24
12
8.7
23
15
23
25
25
19
* Data for two dust/soil samples were excluded because of low spike level.
b Data for one dust/soil sample was excluded because of low spike level.
0 Data for one PUF sample was excluded because of matrix effect.
d Data for seven dust/soil, two wipe, six liquid food, and one solid food were excluded because of low spike level, or interference.
e Data for 12 dust/soil and five wipe samples were excluded because of low spike level or matrix effect.
f Trans-permethrin standard was included in the matrix spike solution in part of NC field study.
E Data for all air, wipe, and PUF as well as 15 dust/soil, seven liquid food, and six solid samples were excluded because of low spike level or interference.
h Data for all air, wipe, and PUF as well as 12 dust/soil, seven liquid food and six solid food samples were excluded because of low spike level or interference.
1 Data for 12 dust/soil, 13 wipe, and two liquid food samples were excluded because of low spike level, or matrix effect.
' Data for four dust/soil, five wipe, and three liquid food samples were excluded because of matrix effect.
                                                                                    6-19

-------
Table 6.2.11  Results for Matrix Spike Samples for Acidic Pollutants/Metabolites - North Carolina
 Pollutant
                               Air
                                                 Dust/Soil
                                                                      Wipes
Liquid Food
                                                                                                           Solid Food
Typical spike level, ng
Number of QC samples
Percent of field samples
50
20
6.6
50
19
6.4
50
12
4.7
50
14
4.9
50
21
7.1
Percent Recovery, %
OP Metabolites
3,5,6-TCP
Acid Herbicides
Dicamba
2,4-D '
2,4,5-T
Phenols
PCP
mean
80

64
67
69

99
SD
11

16
18
15

23
mean
8

72
76
78

78
SD
18

16
23
19

26
mean
80

75
77
74

69
SD
8.2

13
15
15

11
mean
69

74
80
80

67
SD
14

14
15
14

14
mean
80

88
92
99

78
SD
7.8

13
15
14

14
* Data for four dust/soil samples were excluded because of low spike level or matrix effect.
Table 6.2.12  Results for Matrix Spike Samples for Urine Analysis - North Carolina
 Pollutant
                                                                         Urine
Typical spike level, ng/sample
Number of QC samples
Percent of field samples
25
32
6.8
Percent Recovery, %
OP Metabolites
IMP"
3,5,6-TCP
Acid Herbicides
2,4-D
PAH Metabolites
l-Hydroxybenz[a]anthracene b
3-Hydroxychrysene b
Phenols
PCP
mean
7.2
99

98

92
95

79
SD
3.2
11

12

22
18

10
* Low recoveries were obtained for IMP because the analytical method used was developed for 3,5,6-TCP, not IMP.
b Data for three urine samples were excluded because of matrix effect or interference.
                                                                       6-20

-------
Table 6.2.13   Results for Surrogate Recovery Standards for Neutral Pollutants - North Carolina
 Pollutant
                                     Air
                                                       Dust/Soil
                                                                            Wipes
Liquid Food
                                                                                                                   Solid Food
                                                                                                                                         PUF
Typical spike level, ng
Number of QC samples
Percent of field samples
50
351
110
50
371
120
20
346
120
50
202
120
50
197
120
50
23
130
Percent Recovery, %

Benzylbutylphthalate-d4 *
Bisphenol-A-d6 b
Dibenz[a,/?]anthracene-d14 °
p,p'-DDE-d4
PCB101-C13
mean
120
110
110
97
98
SD
18
21
18
14
14
mean
110
73
87
84
86
SD
21
22
19
19
18
mean
120
110
99
100
110
SD
15
19
19
18
17
mean
74
110
110
89
90
SD
25
21
22
22
21
mean
56
100
88
73
69
SD
9.5
21
21
15
10
mean
110
55
87
97
95
SD
16
19
11
14
11
* Data for 231 air, 83 dust/soil, and 126 wipe samples were excluded because of interference or matrix effect.
b Data for 97 air, 210 dust/soil. 147 wipe, 36 liquid food, and 36 solid food samples were excluded because of interference or matrix effect.
0 Data for 24 dust/soil and 39 solid food samples were excluded because of matrix effect or interference.
Table 6.2.14   Results for Surrogate Recovery Standards for Acidic Pollutants - North Carolina
 Pollutant
                                     Air
                                                       Dust/Soil
                                                                            Wipes
Liquid Food
                                                                                                                  Solid Food
Typical spike level, ng
Number of QC samples
Percent of field samples
50
355
120
50
359
120
50
290
110
50
332
110
50
379
130
Percent Recovery, %

2,4-D-C13"
mean
79
SD
15
mean
79
SD
14
mean
75
SD
11
mean
75
SD
14
mean
91
SD
16
* Data for 11 air samples were excluded because of matrix effect.
                                                                         6-21

-------
Table 6.2.15  Results for Surrogate Recovery Standards for Urine Analysis - North Carolina
   Pollutant
                                                             Urine
Typical spike level, ng
Number of QC samples
Percent of field samples
20
564
120
Percent Recovery, %

2,4-D-C13
mean
91
SD
18
Table 6.2.16  Results for Blank Samples Having Detectable Neutral Pollutants - North Carolina
Pollutant

Number of QC samples
Ppr^pnt nf fioM camplpc
Air
MR
17
s fi
PR
12
1 0
Dust/Soil
MR
23
7 7
PR
12
An
Wipes
MR 1 PR
15
S 9
13
A S
Liquid Food
MR
8
40
PR
12
7 A
Solid Food
MR
7
49
PR
12
7 9
PUF
MR
2
1 1
PR
0
Q
Concentration

OP Pesticides
Chlorpyrifos
Pyrethroid Pesticides
cw-Permethrin
frara-Permethrin
Phthalates
Benzylbutylphthalate
di-«-Butylphthalate
Phenols
Bisphenol-A
ng/m3
median
0.06

0.06
_

28
24

-
SD
0.01

0.03
_

78
21

-
ng/g
median
-"


_

41
38

-
SD
•


_

96
59

-
ng/sample
median
-

-
_

360
300

7.1
SD
-


_

490
500

15
ng/mL
median
-

0.003
0.003

9.8
42

-
SD
-

0.03
0.07

43
46

-
ng/g
median
•

-
_

36
94

-
SD
-

-.
_

86
130

-
ng/m2
median
•

-
_

7000
9000

-
SD
•

-
_

1500
8800

-
a. - denotes not detected in all blanks.
                                                            6-22

-------
Table 6.2.17  Results for Blank Samples Having Detectable Acidic Pollutants/Metabolites
             North Carolina
Pollutant

Number of QC samples
Percent of field samples
Air
MB
19
6.3
FB
12
4.0
Dust/Soil
MB
15
5.1
FB
12
4.0
Wipes
MB
12
4.7
FB
11
4.3
Liquid Food
MB
7
2.5
FB
12
4.2
Solid Food
MB
17
5.7
FB
12
4.0
Concentration


OP Metabolites
3,5,6-TCP
Phenols
PCP
ng/m3
median

0.06

0.06
SD

0.01

1.1
ng/g
median

1.4

. a
SD

0.56

-
ng/sample
median

0.71

-
SD

0.88

-
ng/mL
median

-

-
SD

-

-
ng/g
median

0.09

-
SD

0.03

-
a. - denotes not detected in all blanks.
Table 6.2.18  Results for Water Samples - North Carolina
Pollutant
Number of QC
Percent of field


Atrazine
Drinking Water Samples
Duplicate
28
18
Relative Percent
Difference, %
mean
2.2
SD
3.5
Analytical Duplicate
28
18
Relative Percent
Difference, %
mean
2.3
SD
5.1
MSS
16
10
Percent Recovery,
%
mean
84
SD
20
Blank
MB
15
9.7
FB
13
8.4
Concentration,
ng/mL
median
0.01
SD
0.02
                                          6-23

-------
6.2.4.2.2 Ohio For the OH study, results of the %RPD of duplicate samples for neutral pollutants,
acidic pollutants/metabolites, and pollutants/metabolites in urine are summarized in Tables
6.2.19, 6.2.20, and 6.2.21, respectively. The mean of the %RPD was between 0% and 18% for all
duplicate samples, except for the two phthalates.  The mean of the %RPD for the two phthalates
ranged from 7.1% to 38%. Results of the %RPD of duplicate GC/MS analyses are summarized in
Tables 6.2.22 to 6.2.24. As expected, %RPD values from the duplicate GC/MS analyses were
smaller than those from the duplicate samples.

       Recovery data for the OH matrix spike samples are summarized in Tables 6.2.25 to 6.2.27'.
Recovery data of SRSs are summarized in Tables 6.2.28 to 6.2.30.  With few exceptions,
quantitative matrix spike and SRS recoveries were obtained for the target compounds in all
sample media. Mean recoveries ranged from 70±16% to 130±23% for neutral pollutants, from
71±8.2% to 100±11% for acidic pollutants/metabolites. Because of the high background levels
found in the nonspiked blank sample media as well as the high levels found in field samples, the
spiked levels of the two phthalates were not high enough in most of the matrix spike samples. As
a result, satisfactory recoveries could not be obtained.  For the same reason, satisfactory
recoveries for diazinon, PAHs, and frvms'-permethrin could not be obtained in one matrix spike
sample. Interference peaks were observed for bisphenol-A, cyfluthrin, and c/'s-permethrin in
some samples. Recovery of IMP was not acceptable (<50%) in liquid food, solid food, and urine
samples.  This was mainly because the analytical method developed for the other OP metabolite,
3,5,6-TCP, was also used to measure IMP, but was found to be inadequate to measure IMP in
some matrices. Different analytical methods need to be developed and evaluated for quantitative
determination of IMP in these sample media.

       Quantitative recoveries for the SRSs including p,p'-DDE-d4, dibenz[a,/z]anthracene-d14,
PCB101-C13, and 2,4-D-C13 were  obtained in most OH field samples. Interference  peaks were
observed for the benzylbutylphthalate-d4 and bisphenol-A-d6, in some air, dust, soil, and wipe
samples; satisfactory recoveries for these SRSs were not obtained.

       Results of the OH field blanks and laboratory blanks are summarized in Tables 6.2.31 to
6.2.33. Note that the reported median and SD values were from the combined field blanks and
laboratory method blanks.  The median concentrations of the target pollutants/metabolites were
below or close to the method detection limits.  Measurable amounts of the two phthalates were
found in the field blanks and laboratory method blanks in all media, and cis- and trans-permethrin
were found in air blanks. Therefore, background-corrected data for these samples were used for
the statistical analysis discussed in Chapter 8 of this report.
                                           5-24

-------
Table 6.2.19   Results for Duplicate Samples for Neutral Pollutants - Ohio
p ,, , , n,,vtiv™i T :„„:,! w™.,i «,jsj w,.™i
Number of QC samples
Percent of field samples
22
7.2
8
4.8
10
5.9
Relative Percent Difference, %
OP Pesticides
Chlorpyrifos
Diazinon
OC Pesticides
Aldrin
a/p/?a-Chlordane
gamma-Chlordane
p,p'-DDE
p,p'-DDT
Dieldrin
Endrin
Heptachlor
Lindane
Pentachloronitrobenzene
Pyrethroid Pesticides
Cyfluthrin
cw-Permethrin
frara-Permethrin
PAHs
Benz \a\ anthracene
Benzo[alpyrene
Benzo[fe]fluoranthene
Benzo[e]pyrene
Benzo [g/7! ]perylene
Benzo[£lfluoranthene
Chrysene
Dibenz[a,/7]anthracene
Indeno [1,2,3 -crf]pyrene
Phthalates
Benzylbutylphthalate
di-«-Butylphthalate
Phenols
Bisphenol-A
Nonylphenol
PCBs
PCB44
PCB52
PCB70
PCB77
PCB95
PCB 101
PCB 105
PCB 110
PCB 118
PCB 138
PCB 153
PCB 180
mean
4.8
7.8

-
3.9
4.2
3.8
1.9
3.1
0.18
-
-
-

3.7
3.3
2.8

18
13
8.3
13
11
5.8
14
10
11

22
15

2.3
_

0.79
1.4
1.1
-
4.1
2.1
0.55
2.3
1.1
1.2
3.3
0.73
SD
8.9
10

-
5.6
5.2
7.7
4.4
6.9
0.60
-
-
-

6.3
4.0
3.5

14
12
7.7
9.4
8.5
5.3
10
8.9
7.0

34
11

3.9
_

1.7
2.4
2.9
-
6.5
3.2
1.8
4.3
1.6
3.4
5.4
2.4
mean
0.79
.«

-
-
-
_
_
-
-
-
-
-

_
_
_

-
-
-
-
-
_
-
-
_

29
38

4.7
_

NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
SD
1.6
_

-
-
-
_
_
-
-
-
-
-

_
_
_

-
-
-
-
-
_
-
-
_

28
17

9.3
_

-
-
-
-
-
-
-
-
-
-
-
-
mean
9.6
1.6

-
-
-
4.8
_
-
-
-
-
-

_
2.3
3.9

0.37
0.63
3.7
-
-
0.36
2.5
-
_

30
7.1

9.6
_

-
-
-
-
-
-
-
-
-
-
-
-
SD
5
2.5

-
-
-
4.2
_
-
-
-
-
-

_
2.4
4.2

0.84
1.4
6.6
-
-
0.50
3.5
-
_

28
2.8

12
_

-
-
-
-
-
-
-
-
-
-
-
-
* - denotes not detected in all duplicate samples.
b NM denoted that PCBs were not measured in liquid food samples.
                                                 6-25

-------
Table 6.2.20  Results for Duplicate Samples for Acidic Pollutants/Metabolites - Ohio
Pollutant
Number of QC samples
Percent of field samples
Dust/Soil
20
6.7
Liquid Food
22
7.6
Solid Food
16
5.4
Relative Percent Difference, %
OP Metabolites
IMP
3,5,6-TCP
Acid Herbicides
dicamba
2,4-D
2,4,5-T
Phenols
PCP
mean
3.5
5.0

1.3
5.2
0.66

4.2
SD
5.3
3.4

2.8
7.8
2.1

4.4
mean
1.5
2.1

.<>
-
_

-
SD
5.0
2.4

_
-
_

-
mean
7.1
6.3

2.0
1.9
_

0.33
SD
5.3
5.6

5.6
3.0
_

0.93
a. - denotes not detected in all duplicate samples.
Table 6.2.21  Results for Duplicate Samples for Urine Analysis - Ohio
Pollutant
Number of QC samples
Percent of field samples
Urine |
26
5.7
Relative Percent Difference, %
OP Metabolites
IMP
3,5,6-TCP
Acid Herbicides
2,4-D
PAH Metabolites
1 -Hydroxybenz[alanthracene
3 -Hydroxychry sene
Phenols
PCP
mean
_>
4.8

4.1

0.18
_

4.9
SD
-
6.1

4.0

0.44
_

3.4
a. - denotes not detected in all duplicate samples.
                                              6-26

-------
Table 6.2.22  Results for Duplicate Analyses of the Same Sample Extract for Neutral Pollutants - Ohio
Pollutant
Number of QC samples
Percent of field samples
Air
PCB
32
10
Others
34
11
Dust/Soil
PCB
44
15
Others
30
10
Wipes
PCB
54
19
Others
38
14
Liquid Food
PCB
NM"
-
Others
18
11
Solid Food
PCB
28
16
Others
24
14
PUF
PCB
4
29
Others
4
29
Relative Percent Difference, %
OP Pesticides
Chlorpyrifos
Diazinon
OC Pesticides
Aldrin
a/p/?a-Chlordane
gamma-Chlordane
p,p'-DDE
p,p'-DDT
Dieldrin
Endrin
Heptachlor
Lindane
Pentachloronitrobenzene
Pyrethroid Pesticides
Cyfluthrin
cw-Permethrin
frara-Permethrin
PAHs
Benz[alanthracene
Benzo[a]pyrene
Benzo[felfluoranthene
Benzo[e]pyrene
Benzo |#fe Iperylene
Benzo[£]fluoranthene
Chrysene
Dibenz[a, /7]anthracene
Indeno [1,2,3 -crf|pyrene
mean
2.0
3.7

0.05
3.0
4.1
_
-
0.18
0.11
1.2
-
0.80

_
3.5
1.6

2.0
0.31
1.2
2.2
1.5
0.88
1.8
-
0.83
SD
2.6
5.3

0.20
3.7
4.0
_
-
0.74
0.30
2.7
-
3.0

_
4.1
2.4

3.7
0.71
2.6
3.7
3.5
1.8
2.6
-
1.6
mean
2.3
3.7

0.11
3.4
3.5
2.7
2.7
0.57
0.04
0.54
0.40
_

2.3
3.6
2.4

2.6
2.3
3.7
2.8
3.6
3.3
2.8
4.9
4.3
SD
3.4
4.4

0.42
2.9
3.6
3.2
4.6
1.6
0.15
1.5
1.6
_

4.0
3.6
1.9

1.9
1.8
2.7
2.2
2.7
3.5
3.2
4.1
4.0
mean
2.3
1.4

b
1.8
1.8
_
0.10
-
-
_
-
_

0.19
2.3
4.3

2.0
1.7
2.5
2.9
2.6
3.3
2.4
3.4
3.7
SD
2.8
2.9

-
4.2
3.2
_
0.43
-
-
_
-
_

0.57
3.4
4.9

2.4
2.1
3.6
3.3
2.3
3.3
2.2
6.3
3.5
mean
-
-

-
-
-
_
-
-
-
_
-
_

_
-
_

_
-
-
-
_
-
-
-
-
SD
-
-

-
-
-
_
-
-
-
_
-
_

_
-
_

_
-
-
-
_
-
-
-
-
mean
2.5
0.23

-
0.66
0.66
1.5
-
0.35
-
0.06
-
_

_
-
_

0.30
0.07
2.2
0.66
_
0.12
0.85
-
-
SD
3.7
0.57

-
2.3
2.3
1.8
-
1.2
-
0.21
-
_

_
-
_

0.81
0.23
4.8
2.0
_
0.42
2.5
-
-
mean
5.7
1.3

-
-
-
_
-
9.0
-
_
-
_

_
2.4
3.4

3.4
6.7
3.6
4.6
4.2
2.8
1.7
-
2.2
SD
8.1
1.9

-
-
-
_
-
13
-
_
-
_

_
1.7
0.50

4.4
2.2
4.2
4.5
0.34
0.98
1.0
-
0.44
                                                       6-27

-------
Table 6.2.22  Results for Duplicate Analyses of the Same Sample Extract for Neutral Pollutants - Ohio (cont.)
Pollutant
Phthalates
Benzylbutylphthalate
di-«-Butylphthalate
Phenols
Bisphenol-A
Nonylphenol
PCBs
PCB44
PCB52
PCB70
PCB77
PCB95
PCB 101
PCB 105
PCB 110
PCB 118
PCB 138
PCB 153
PCB 180
Air
mean
11
9.1

3.5
-

0.26
4.7
0.71
_
1.7
0.78
-
0.27
-
-
-
-
SD
21
26

4.1
-

1.0
5.4
1.5
_
2.8
2.7
-
1.1
-
-
-
-
Dust/Soil
mean
6.1
7.5

2.1
-

0.51
1.5
0.72
_
1.9
0.83
0.29
1.4
0.89
0.67
1.7
0.72
SD
9.8
13

3.6
-

1.7
2.4
1.5
_
3.6
1.4
1.3
2.5
1.8
1.6
3.6
1.8
Wi
mean
2.6
1.6

3.4
-

0.41
0.67
1.2
_
0.57
0.43
0.11
0.25
0.25
-
-
-
pes
SD
3.1
2.7

3.8
-

1.5
1.8
3.4
_
2.6
1.6
0.58
0.84
0.98
-
-
-
Liquid Fond
mean
3.8
3.3

2.6
-

NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
SD
4.6
4.0

3.2
-

-
-
-
_
-
-
-
_
-
-
-
-
Solid Fond
mean
2.4
1.2

3.8
-

-
0.23
-
_
-
-
-
_
-
-
-
-
SD
1.8
0.95

1.9
-

-
0.87
-
_
-
-
-
_
-
-
-
-
PIIF
mean
1.3
0.87

2.9
-

-
8.5
0.62
_
-
3.9
-
4.3
-
-
-
-
SD
0.79
0.42

0.58
-

-
4.0
0.87
_
-
5.4
-
4.8
-
-
-
-
"NM denotes that PCBs were not measured in liquid food samples.
b - denotes not detected in all duplicate GC/MS analyses.
                                                                 6-28

-------
Table 6.2.23  Results for Duplicate Analyses of the Same Sample Extract for Acidic Pollutants/Metabolites - Ohio
Pollutant
Number of QC samples
Percent of field samples
Air
silylate
28
9.2
methylate
26
8.5
Dust/Soil
silylate
28
9.3
methylate
42
14
Wipes
silylate
30
12
methylate
20
7.9
Liquid Food
silylate
24
8.3
methylate
30
10
Solid Food
silylate
16
5.4
methylate
16
5.4
Relative Percent Difference, %
OP Metabolites
IMP
3,5,6-TCP
Acid Herbicides
Dicamba
2,4-D
2,4,5-T
Phenols
PCP
mean
3.1
5.0

0.03
2.7
.<>

2.9
SD
3.10
6.5

0.10
5.7
_

4.2
mean
1.9
1.1

1.1
2.6
_

1.8
SD
2.8
1.3

2.4
4.2
0.01

1.7
mean
1.5
3.6

0.05
1.2
_

1.6
SD
2.8
2.9

0.14
1.7
_

2.3
mean
0.68
0.85

-
-
_

0.38
SD
1.7
1.5

-
-
_

1.5
mean
4.1
2.9

0.19
0.32
_

0.06
SD
5.1
2.3

0.53
0.52
_

0.16
' - denotes not detected in all duplicate GC/MS analyses.
Table 6.2.24  Results for Duplicate Analyses of the Same Sample Extract for Urine - Ohio
Pollutant
Number of QC samples
Percent of field samples
Urine
56
12
Relative Percent Difference, %
OP Metabolites
IMP
3,5,6-TCP
Acid Herbicides
2,4-D
PAH Metabolites
l-Hydroxybenz[alanthracene
3-Hydroxychrysene
Phenols
PCP
mean
0.05
1.8

3.1

.<>
_

4.9
SD
0.21
1.6

2.8

_
_

3.8
 ' - denotes not detected in all duplicate GC/MS analyses.
                                                             6-29

-------
Table 6.2.25  Results for Matrix Spike Samples for Neutral Pollutants - Ohio
Pollutant
Typical spike level, ng
Number of QC samples
Percent of field samples
Air
50
19
6.2
Dust/Soil
20
11
3.7
Wipes
20
7
2.5
Liquid Food
25
6
3.6
Solid Food
50
7
4.1
Percent Recovery, %
OP Pesticides
Chlorpyrifos
Diazinon *
OC Pesticides
Aldrin
a/p/?a-Chlordane
£amma-Chlordane
p,p'-DDE
p,p'-DDT
Dieldrin
Endrin
Heptachlor
Lindane
Pentachloronitrobenzene
Pyrethroid Pesticides
Cyfluthrinb
cw-Permethrin0
frara-Permethrin d
PAHse
Benz[alanthracene
Benzo[alpyrene
Benzo[felfluoranthene
Benzo[elpyrene
Benzo fe/7! Iperylene
Benzo[£lfluoranthene
Chrysene
Dibenz[a, /?lanthracene
Indeno [1,2,3 -crf|pyrene
mean
97
77

84
91
91
95
96
87
94
90
86
87

97
100
88

89
76
88
75
72
84
85
74
70
SD
13
13

9.8
12
11
12
23
12
12
15
9.1
11

19
17
11

17
18
16
12
12
19
14
15
16
mean
81
77

81
72
75
76
88
92
82
95
81
82

100
110
86

87
90
95
82
90
86
90
79
87
SD
6.8
7.8

12
4.0
7.3
5.7
13
15
8.5
13
11
16

14
30
7.1

21
15
24
14
15
8.8
18
6.1
13
mean
110
95

91
95
96
93
110
93
110
100
120
110

100
99
97

95
95
97
92
88
93
91
92
91
SD
12
120

14
12
15
15
15
15
10
16
7.3
10

15
12.
1.8

16
19
17
17
17
15
15
16
19
mean
89
72

90
73
72
81
89
90
90
83
87
100

71
87
68

91
91
96
81
89
99
78
100
100
SD
11
13

8.4
9.3
9.4
11
12
6.0
10
13
12
16

18
19
27

16
13
12
7.8
14
7.9
12
16
18
mean
100
78

93
78
76
77
110
93
100
100
110
120

110
110
85

100
100
92
82
100
96
83
100
100
SD
17
12

14
8.3
6.7
13
17
13
9.8
7.2
12
14

16
27
17

24
13
13
11
17
17
17
20
16
                                                          6-30

-------
Table 6.2.25   Results for Matrix Spike Samples for Neutral Pollutants - Ohio (cont.)
Pollutant
Phthalates
Benzylbutylphthalate f
di-«-Butylphthalateg
Phenols
Bisphenol-Ah
Nonylphenol
PCBs1
PCB44
PCB52
PCB70
PCB77
PCB95
PCB 101
PCB 105
PCB 110
PCB 118
PCB 138
PCB 153
PCB 180
Air
mean
-
-

78
86

89
88
93
92
87
90
99
93
97
94
93
99
SD
-
-

10
12

13
11
14
15
14
12
14
12
13
12
12
15
Dust/Soil
mean
80
91

567
76

75
78
76
83
72
73
79
73
74
78
76
78
SD
12
11

4.2
20

5.1
9.5
6.0
14
7.2
7.7
7.4
7.1
6.3
8.4
7.5
8.3
Wipes
mean
-
-

110
100

80
87
87
90
81
87
88
88
87
86
86
85
SD
-
-

13
12

14
8.7
8.3
17
11
8.6
11
9.0
13
10
11
12
Liquid Food
mean
-
-

97
100

_
-
-
-
_
-
-
-
_
-
-
-
SD
-
-

24
19

_
-
-
-
_
-
-
-
_
-
-
-
Solid Food
mean
120
76

130
130

84
86
90
100
78
86
100
91
98
94
95
98
SD
15
5.8

23
12

12
11
11
13
12
12
19
13
15
14
15
17
* Data for diazinon in one dust/soil sample was excluded because of low spike level.
b Data for two dust/soil samples were excluded because of interference.
0 Data for eight dust/soil samples were excluded because of interference or low spike level.
d Data for one dust/soil sample was excluded because of low spike level.
e Data for all target PAHs in one dust/soil sample was excluded because of low spike level.
f Data for air, wipe, and liquid food can not be obtained because of low spike level; data for seven dust/soil, six liquid food, and five solid food samples were excluded because of low spike level or matrix
effect.
E Data for air, wipe, and liquid food can not be obtained because of low spike level; data for eight dust/soil, six liquid food, and five solid food samples were excluded because of low spike level or matrix
effect.
h Data for two air samples, eight dust/soil samples were excluded because of matrix effect.
'PCBs were not measured in liquid food samples.
                                                                                    6-31

-------
Table 6.2.26   Results for Matrix Spike Samples for Acidic Pollutants/Metabolites - Ohio
Pollutant
Typical spike level, ng
Number of QC samples
Percent of field samples
Air
50
14
4.6
Dust/Soil
50
8
2.7
Wipes
50
9
3.5
Liquid Food
50
11
3.8
Solid Food
50
9
3.0
PUF
50
1
25
Percent Recovery, %
OP Metabolites
IMP
3,5,6-TCP
Acid Herbicides
Dicamba
2,4-D
2,4,5-T
Phenols
PCP
mean
93
86

77
80
85

77
SD
12
12

10
9.3
8.8

7.0
mean
63
82

72
71
81

86
SD
35
8.7

11
8.2
12

12
mean
79
86

79
82
83

79
SD
13
14

15
9.9
11

5.9
mean
6.6
79

82
83
84

84
SD
4.6
13

9.9
11
6.4

18
mean
10
86

78
85
86

84
SD
5.9
17

6.0
8.2
9.1

10
mean*
59
56

26
51
51

75
SD
NA
NA

NA
NA
NAb

NA
* The reported mean value for the PUF sample was the recovery data of the one matrix spike PUF sample analyzed.
' NA denotes not applicable.
Table 6.2.27   Results for Matrix Spike for Urine Analysis - Ohio
Pollutant
Typical spike level, ng
Number of QC samples
Percent of field samples
Urine
25
14
3.0
Percent Recovery, %
OP Metabolites
IMP"
3,5,6-TCP
Acid Herbicides
2,4-D
PAH Metabolites
1 -Hydroxybenz[a]anthracene
3 -Hydroxy chry sene
Phenols
PCP
mean
5.0
96

98

95
100

96
SD
2.3
10

20

16
11

18
"Low recoveries were obtained for IMP because the analytical method used was developed for 3,5,6-TCP, not IMP.
                                                                     6-32

-------
Table 6.2.28  Results for Surrogate Recovery Standards for Neutral Pollutants - Ohio
Pollutant
Typical spike level, ng
Number of QC samples
Percent of field samples
Air
50
360
120
Dust/Soil
20
347
120
Wipes
20
317
110
Liquid Food
25
192
110
Solid Food
50
198
120
PUF
20
17
120
Percent Recovery, %

Benzylbutylphthalate-d4 *
Bisphenol-A-d6b
Dibenz[a,/?]anthracene-d14
p,p'-DDE-d4
PCB101-C13
mean
120
92
80
98
94
SD
38
25
18
18
16
mean
100
65
75
82
78
SD
28
14
16
31
11
mean
110
100
92
94
89
SD
28
13
16
15
11
mean
61
97
98
80
NM°
SD
12
19
19
18
-
mean
63
120
100
75
93
SD
15
20
21
12
19
mean
110
65
75
100
95
SD
8.9
6.5
12
14
8.5
* Data for 85 liquid food and 119 solid food were excluded because of matrix effect.
b Data for 256 dust/soil, 75 wipe, 22 solid food, and 14 PUF were excluded because of interference or matrix effect.
° NM denotes that PCBs were not measured in liquid food samples.
Table 6.2.29  Results for Surrogate Recovery Standards for Acidic Pollutants - Ohio
Pollutant
Typical spike level, ng
Number of QC samples
Percent of field samples
Air
50
357
120
Dust/Soil
50
350
120
Wipes
50
281
110
Liquid Food
50
336
120
Solid Food
50
333
110
PUF
70
5
120
Percent Recovery, %

2,4-D-Cn
mean
80
SD
15
mean
81
SD
11
mean
82
SD
10
mean
90
SD
13
mean SD
88 12
mean
53
SD
1.8
Table 6.2.30  Results for Surrogate Recovery Standards for Urine Analysis - Ohio
Pollutant
Typical spike level, ng
Number of QC samples
Percent of field samples
Urine
20
518
110
Percent Recovery, %

2,4-D-Cn
mean
95
SD
20
                                                                  6-33

-------
Table 6.2.31   Results for Blank Samples with Detectable Neutral Pollutants - Ohio
Pollutant

Number of QC samples
Percent of field samples
Air
MB
18
5.9
FB
14
4.6
Dust/Soil
MB
11
3.7
FB
14
4.7
Wipes
MB
12
4.3
FB
14
5.0
Liquid Food
MB
5
3.0
FB
14
8.3
Solid Food
MB
4
2.3
FB
14
8.2
PUF
MB
1
7.1
FB
1
7.1
Concentration

OP Pesticides
Chlorpyrifos
OC Pesticides
p,p'-DDT
Pyrethroid Pesticides
Cyfluthrin
cw-Permethrin
frara-Permethrin
PAHs
Benz \a\ anthracene
Chrysene
Phthalates
Benzylbutylphthalate
di-«-Butylphthalate
Phenols
Bisphenol-A
PCBs
PCB44
PCB52
PCB70
PCB110
ng/m3
median
0.06

_«

0.62
0.06
0.06

0.06
0.06

27
44

0.62

0.03
0.03
0.03
0.03
SD
0.01

_

0.08
0.52
0.44

0.02
0.01

50
43

0.55

0.02
0.02
0.03
0.01
ng/g
median
_

_

_
-
_

_
_

66
130

_

-
_
_
-
SD
_

_

_
-
_

_
_

47
170

_

-
_
_

ng/sample
median
_

_

_
-
_

_
_

360
760

7.1

-
0.71
0.71
0.71
SD
_

_

_
-
_

_
_

1400
1800

11

-
0.83
0.83
0.83
ng/mL
median
_

0.003

_
0.003
0.003

_
_

14
25

0.03

-
_
_
-
SD
_

0.03

_
0.21
0.22

_
_

12
7.2

0.67

-
_
_
-
ng/g
median
_

_

_
-
_

_
_

10
66

_

-
_
_
-
SD
_

_

_
-
_

_
_

12
41

_

-
_
_
-
ng/m2
median
_

_

_
-
_

_
_

4100
18000

388

-
_
_
-
SD
_

_

_
-
_

_
_

4800
23000

510

-
_
_
-
" - denotes that the pollutant was not detected in all the blanks.
                                                                 6-34

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Table 6.2.32  Results for Blank Samples with Detectable Acidic Pollutants/Metabolites - Ohio
Pollutant

Number of QC samples
Percent of field samples
Air
MB
21
6.9
FB
14
4.6
Dust/Soil
MB
11
3.7
FB
14
4.7
Wipes
MB
9
3.2
FB
14
5.0
Liquid Food
MB
8
2.8
FB
14
4.8
Solid Food
MB
9
3.0
FB
14
4.7
PUF
MB
-
-
FB
1
25
Concentration

OP Metabolites
IMP
3,5,6-TCP
Acid Herbicides
2,4-D
Phenols
PCP
ng/m3
median
0.06
0.06

0.12

0.12
SD
0.01
0.03

0.03

0.27
ng/g
median
_
_

_•

-
SD
_
_

_

-
ng/sample
median
_
0.71

1.4

-
SD
_
0.89

1.7

-
ng/mL
median
_
_

_

-
SD
_
_

_

-
ng/g
median
_
0.09

_

-
SD
_
0.05

_

-
ng/m2
median
_
_

_

-
SD
_
_

_

-
" - denotes that the pollutant was not detected in all the blanks.
Table 6.2.33  Results for Blank Samples with Detectable Urine Pollutants - Ohio
Pollutant

Number of QC samples
Percent of field samples

OP Metabolites
3,5,6-TCP
Urine
MB
16
3.5
FB
14
3.0
Concentration, ng/mL
median

0.71
SD

0.18
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       The QC data for the OH water samples are summarized in Table 6.2.34. The overall
method precision was very good. The mean of the RPD of duplicate water samples was 2.1 ±
3.4%; similar results were obtained from the duplicate GC/MS analyses.  The average recovery of
the matrix spike samples was 79 ± 4.7%. Trace amounts of atrazine were found in some of the
blank samples.
Table 6.2.34  Results of Analysis of Water Samples - Ohio
Pollutant

Number of QC samples
Percent of fielH samples


Atrazine
Drinking Water Samples
Duplicate
8
5 1
Relative Percent
Difference, %
mean SD
2.1 3.4
Analytical Duplicate
26
17
Relative Percent
Difference, %
mean
2.3
SD
1.8
MSS


5
3
7
Percent Recovery,
%
mean
79
SD
4.7
Blank
MB
5
3 7
FB
14
80
Concentration,
ng/mL
median
0.01
SD
0.001
6.3    Evaluation

       Due to budget constraints, different analytical methods could not be used for each
compound class. Instead, the OP and OC pesticides, pyrethroid pesticides, PAHs, phthalates,
phenols except for PCP, PCBs, and triazine were grouped as neutral pollutants, and the acid
herbicides, PCP and metabolites for OP pesticides, pyrethroid pesticides, and PAHs were grouped
as acid pollutants/metabolites.

       Two carbamate pollutants, propoxur and bendiocarb, were not included in the day care
pilot studies, and were added later to the CTEPP study design at the suggestion of the EPA Office
of Pesticide Programs, in hopes that the CTEPP methods might be able to detect these compounds
(7-10). However, the analytical methods used in the CTEPP study were not tested  for these two
compounds. Unfortunately, these two pollutants decompose partially on the GC column and
interference compounds co-eluted with both propoxur and bendiocarb. Therefore, useful data were
not obtained for these two compounds.

       Atrazine could be measured accurately in water samples, but there were interference
problems in other sample media.  For air, dust, soil, and wipe samples, there was an interference
compound that eluted at the same retention time as atrazine on the GC column, and which also had
the same ion ratio of the monitored ions as those observed for atrazine. This was initially observed
in the air samples, when extremely high concentrations (>1000 ng/mL) were detected for what was
believed to be atrazine.  The sample extracts were re-analyzed using GC/MS in full mass scan
mode in an attempt to confirm the presence of atrazine in these sample extracts. The full mass
scan results showed that an interference compound, which was an unsaturated aliphatic
hydrocarbon, eluted at the same retention time and had the same monitored ion ratio as did
atrazine. Therefore, atrazine was  measured only in drinking water samples.
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       Interference peaks were also observed for cyfluthrin, c/'s-permethrin, bisphenol-A-d6, and
benzylbutylphthalate-d4 in some samples. These interference peaks affected only the
quantification of the SRSs, benzylbutylphthalate-d4 and bisphenol-A-d6, and did not affect the
quantification of the native chemicals benzylbutylphthalate and bisphenol-A. If the interference
components were not completely resolved from the peaks of target pollutants, estimated values
were obtained and reported.  These data were coded with "INT" in the database to show the
presence of the interferences. Note that the interference peak for c/s-permethrin became
insignificant when the concentrations of this  compound exceeded 100 to 500 ng/mL, depending
upon the sample. In these cases, the INT codes were not reported in the database. In some
samples, interferences were observed for one of the surrogate recovery standard (SRS), bisphenol-
A-d6, but not for the native compound bisphenol-A. Similar interferences were observed for
benzylbutylphthalate-d6, but not for benzylbutylphthalate.

       It is not surprising that phthalates were found in field blanks and laboratory blanks.
Background levels varied greatly among different sample matrices. Phthalates were present in the
analytical-grade solvents that were used for extracting samples and cleaning up sample extracts.
Plastic-related materials were used in the disposal pipette holders and in the pre-packed solid
phase extraction (SPE) columns that were used to clean up sample extracts.  Depending upon the
sample media, types of solvent used,  and cleanup method employed, the background levels of
phthalates varied.  In general, the phthalate contamination increased with sample handling and
number of cleanup steps.  Also, in food samples, the elution band of the phthalates on the GPC
column included many fatty acids and fatty acid esters that hindered low-level detection of
pyrethroids such as cyfluthrin.  The GPC fractions had to be cleaned up further, using ENVI-Carb
columns for the food samples, in order to measure cyfluthrin.

       The determination of a diazinon metabolite, IMP, in the environmental and personal
samples was added late in the OH field study. We used the same analytical methods for TCP to
measure IMP in these samples.  Results of the matrix spike  samples showed that IMP were
quantatively measured in air, dust, soil, wipe but not in urine, solid food and liquid food samples.
We have identified that IMP was lost during  the liquid-liquid partitioning step. The overall
recoveries of IMP in these samples were less than 10%, no statistical analyses were performed on
these data.

6.4    Recommendations

       We recommend evaluation of cleanup methods  and/or different detection methods such as
liquid chromatography (LC)/MS to determine carbamates in multimedia samples for future studies.
In an on-going Battelle study for US  EPA, we developed an analytical method for the
determination of carbamates in water samples.  This method consists of SPE extraction of water
samples into acetonitrile (ACN) and LC/MS  analysis of the ACN extracts.

       We recommend evaluation of cleanup methods  such as  use of a C18 SPE column or an
immunoaffinity (IA) purification column to determine atrazine in multimedia samples.  In an on-
going Battelle study for US EPA, we developed an IA column  for atrazine, established the elution

                                           6-37

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profile of atrazine for the IA column.  Preliminary results suggest that the IA column is an
effective cleanup method for analysis of atrazine in dust and soil samples.

       Different SRSs should be evaluated for phthalates and bisphenol-A to minimize the
interference peaks observed in multimedia samples for future studies.

       In a recent Battelle internal research and development study, we developed an analytical
method that can provide quantitative recoveries of IMP from urine samples.  We therefore
recommend that this new analytical method be evaluated and refined as necessary for determining
IMP in multimedia samples in future studies.

       As noted earlier, phthalates were found in the field blanks and in the laboratory blanks.  In
this study, the phthalate contamination increased with increased sample handling and with the
number of cleanup steps. For future studies, we recommend a different approach to measurement
of phthalates in multimedia samples.  Since phthalates are typically present at much higher
concentrations than the other target pollutants in multimedia samples, we would conduct GC/MS
analysis of the phthalates in dilute sample extracts prior to any cleanup steps for the neutral
compound analyses, as a separate analysis. This approach would eliminate much of the exacting
and time-consuming sample preparation work associated with limiting phthalate contamination
from sample handling.  The GC/MS analysis of the phthalates would include both the m/z 149 ion
for quantification of low concentration pollutants, and the molecular ion for quantification of
pollutants at higher levels.
                                           6-38

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                                     Chapter 7
                                 CTEPP Database
7.1    Overview

       The CTEPP database was configured similarly to the database developed in the
National Human Exposure Assessment Survey (NHEXAS)-Arizona study (14). The database
followed the general format that was used in EPA's exposure database that was current at the
start of the CTEPP study. The database, which comprises the two databases for the North
Carolina (NC) and the Ohio (OH) field studies, contains the questionnaire data, the analytical
data, and metadata. Sufficient detail was provided so that the data can be understood by a
diverse set of users.

       The CTEPP database is one of the largest current databases containing information on the
environmental exposures of preschool children. The study's documentation,  which includes the
study design, Standard Operating Procedures, and Quality System Implementation Plan, will be
placed in EPA's Environmental Information Management System (EIMS;
http://oaspub.epa.gov/edr/eimsS.startup). In addition, the metadata, which include abstracts,
acronyms, keywords, and related entries will be placed in EIMS. The CTEPP data will be stored
in the Human Exposure Database System (HEPS: http://www.epa.gov/heds/). The CTEPP
database will be made available to interested federal agencies, state and local agencies, non-
governmental organizations, academia, and the general public.

7.2    Quality Assurance Procedures for the Database

       Quality assurance and quality control(QA/QC) procedures were implemented within both
the NC and OH databases. The QA/QC summaries are given in Appendix D. The following
subsections provide information on the types of QA/QC procedures associated with the
questionnaire data, analytical data, and metadata collected in this study.

7.2.1   Questionnaire Data

       A comprehensive QA/QC plan was implemented to ensure data quality in all phases of
questionnaire data collection. During the pre-data collection phase, each hard copy data form
was tested by trained project staff for consistency and accuracy. Mock interviews and field data
collection simulations were conducted to evaluate the effectiveness of the data forms. Once
revisions were made to the data forms based on the outcome of these activities, final drafts were
sent to EPA for review and approval. The data forms were further updated after receiving EPA's
comments.  The updated forms were reviewed and approved by the Battelle Institutional Review
Board, the U.S. EPA Human Subjects Research Protection Official, and the U.S. Office of
Management and Budget.

                                          7-1

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       After final approval of the data forms, software components were programmed for use in
the recruitment telephone survey and to allow double entry of the data.  Standardized
programming methods were used which inserted QC checks in all of these programs, including
range checks, consistency checks, and skip pattern rules.  These programs enforced the rules
upon data entry.  Before the programs were approved for actual data entry, they went through
strict QA/QC checks for programming errors.

       Before data collection began, telephone interviewers and field staff were trained in the
study procedures, according to the SOPs, to ensure high data quality. Telephone interviewers
were required to be certified for the study by passing a series of tests before they could initiate
any contact with the study subjects.  Training for the field data collection team members
included a 40-h training session which incorporated at least one day of actual supervised field
sample collection experience. Field staff were allotted additional time to practice their field data
collection techniques.

       After data collection began, data collection activities were monitored routinely.  These
efforts included the use of computer software and phone monitoring systems to monitor
telephone recruitment data, and periodic internal field audits to ensure high quality of data
collected in the field.  In addition, external  field audits were conducted by an EPA auditor and
the EPA Task Order Project Officer (TOPO).

       During field data collection, the field staff also reviewed the collected information while
at the sampling site, to identify missing data items or questionable information. Any identified
issues or problems were resolved at the sampling site before the field data collection team
returned to Battelle. A Daily Activity Check List was also used to assist the field staff in
conducting data collection activities and field edits.

       After a data collection event at a sampling site was completed and the data forms were
returned to Battelle, the receiving team conducted QC checks on each participant's data  forms
and study materials.  The team used a Participant Data QC Check List to verify a standard list of
important items. All data forms were then  entered twice and verified, using the CTEPP Double
Data Entry Program.  Two data entry teams performed the data entry work and entered the data
into two separate databases. These separate databases were compared for consistency, corrected
if necessary, and combined into one database. As mentioned above, these data entry programs
included range checks, consistency checks, and skip pattern rules.

       Finally, after completing all the data collection tasks, the project staff conducted final
QA/QC checks by reviewing data frequency reports and verifying randomly selected participant
files. Data items in the database were checked against the data documentation manual and the
actual participant data in the original data form. Personal identifiers were removed from the
database to ensure participant confidentiality.
                                           7-2

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7.2.2   Analytical Data

       Analytical data were electronically imported into the database according to CTEPP SOP
4.12.  The analytical raw data (QUAN report) were generated from each instrument by a
qualified analyst.  The QUAN report was then reviewed by the Task Order Leader (TOL) for all
the identified pollutants. The QUAN report was then electronically transferred into a custom
report and saved as a "crd" file.  The "crd" file was then electronically parsed into an Excel
spreadsheet template. Data such as sample extraction weight and quality assurance codes were
manually entered and saved as an Excel file with an extension of .xls by the first data reviewer.
The TOL reviewed all the Excel files before they were imported into the analytical database. If
any anomalous results were observed in the data, every effort was made to identify any problems
in the sample collection, sample preparation, and/or analysis, which could have contributed to
the anomaly. Data dictionaries and code sets for core analytical data, QA/QC data, and ancillary
data were developed for the analytical database.  The completed Excel spreadsheets were then
electronically imported into the analytical database by the database staff.

       Database queries were developed to perform QA/QC checks on the NC and OH
analytical databases.  These included (1) sample ID checks, (2) missing data checks, (3)
duplicate data checks, (4) out-of-range checks, and (5) upper- and lower- concentrations checks.

       The sample ID checks were performed to verify that all Sample IDs with reported data
were valid Sample IDs, that is, that they were logged as being received from the field.  If invalid
sample IDs were detected, the database staff traced back to the original raw data, including
laboratory record books and GC/MS logbooks, to identify the transcription error and to make the
corrections accordingly. All  corrections were documented in the database importing log book.

       Missing data checks were performed to verify that all Sample IDs received from the field
had a complete set of analytical data reported.  Those samples that were received but did not
have a complete set of analytical data and/or ancillary data for a stated reason in the electronic
Chain of Custody  (CoC) data were identified, and either the analytical data for these samples
were found and imported into the database, or the samples were located, processed, analyzed,
and reviewed, and the analytical data were imported into the database.

       Duplicate data checks were performed to verify that the same analytical data were not
imported into the database twice for a given sample. The database staff traced the sample results
back to the laboratory record books, the GC/MS sequence logs, and/or the QUAN reports to
confirm that duplicate data were the result of a double import, and not a QA/QC re-analysis (e.g.
duplicate sample or duplicate injection). Once the duplicate data were identified as a double
import, the set of results for the sample having the oldest sample import date were eliminated
from the analytical database.  If the duplicate data were identified as a QA/QC re-analysis, the
proper QC code was added to the QC_Code data field, and the data for the first duplicate (only)
remained in the Core_Analytical_Results table, and the data for the first and second duplicates
were reported in the QA_QC_Results table.
                                           7-3

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       Out-of-range checks were performed to verify that all data for data fields limited to a
code set did not violate that code set. For data fields that were limited to a code set of values,
queries were performed to identify data within those fields that did not belong to, or "violated",
the code set. Once identified, the database staff traced the sample results back to  the laboratory
record books to identify the transcription error. The data in the database were corrected, and
these corrections were documented.

       Upper- and lower-level concentrations checks were performed on all results that were
greater than plus or minus three standard deviations from the mean. Database queries were
performed to identify those calculated results (Resultl and Result2) that were greater than or less
than three standard deviations from the domain mean.  Five percent of these data were reviewed
again by the data reviewer.  The data reviewer checked the QUAN report, all the parameters
used for the results calculation, and the result calculation itself to make sure that identification
and quantification were performed correctly. If the data reviewers detected any mis-
identification and/or mis-quantification, corrections were made accordingly.  The TOL approved
the corrected data, and the database manager made the changes in the database. All activities
were documented in the laboratory record books and database importing log.

       After all checks were completed, the final calculation of results was performed within the
database. A random subset (approximately 5%) of calculated results were recalculated using an
independent calculation source (Excel) for validation.  In addition, hand calculations were
performed on one data set for each sample matrix using a calculator.

7.2.3   Metadata

       Metadata were prepared in the format described in the "User Guide and Data
Administration Guidelines for the USEPA's Environmental Information Management System
(EIMS)," Version 1.3, Oct. 2001, including abstracts, related entries, key words,  and acronyms,
at the study, data table, and document level.

7.3    EPA Review

       EPA conducted several independent QA/QC reviews of the early draft versions of the NC
and OH databases.  The EPA performed visual range checks. The data were normalized before
identifying potential outliers. Outliers were identified based on whether they exceeded six
standard deviations from the mean. For a randomly selected set of variables (about 5%), more
extensive checks were performed including range checks, consistency, and skip pattern checks.
When the EPA Database Manager or the EPA TOPO identified problems or errors (i.e., missing
samples, duplicate samples, linkage problems) in the database, the EPA TOPO had Battelle
verify that the  data were correct and make  any necessary changes to the data in the database.

       After the draft final NC and OH databases were delivered to EPA, EPA conducted a
more thorough QA/QC review of the databases. EPA repeated the extensive checks performed
on the randomly selected variables. In addition, a new set of randomly selected variables

                                          7-4

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(additional 5%) were thoroughly checked. Furthermore, comparisons were made between earlier
versions and the latest version of the database to assure that no unexplained changes had
occurred. Any errors identified by EPA in the database were corrected by Battelle.

       After EPA received the final versions of the NC and OH databases, EPA assigned data
quality values to each sample in the Core_Analytical_Results table. The QA/QC protocol (SAS
program) used to assess the quality of each sample is found in Appendix E. Each sample result
was assigned one of the following data quality (QC_Flag code) values:

       1 = good quality data
       2 = questionable, but still acceptable data
       3 = unusable data

       Only sample results that had assigned QC_Flag code values of 1 or 2 were used in the
statistical analyses discussed in Chapters 8 and 9.  In addition, the data associated with one NC
adult participant (PID972072) and accompanying child (PID972071) who withdrew from the
study after Day 1 were excluded from the statistical analyses.

7.4    Evaluation

       Within each record of the CTEPP database, the Participant Identification code (PID) was
designed to be the key linking field that allows database users access to all of a given subject's
study data, including questionnaire data and measured environmental  and biological target
compound levels.  The PID was designed as a  6-digit composite data field.  The first two digits
contained  the day care code (indicating whether or not the study participant attended day care,
the specific day care, participant or non-day care participantand the state of origin).  The next
three digits were a unique participant identification number. The sixth digit contained the
participant type code, which identified the sample as collected from a child or from an adult at
home, or from a child at day care. Although the information contained within the PID was
important, the first step database users had to do before querying the environmental, personal, or
questionnaire data was to query the PID to separate it into its different pieces of information.

7.5    Recommendations

       Based upon lessons learned from designing the CTEPP database, recommendations for
designing  large exposure databases  on future studies are as follows:

(1)    Avoid Composite Data Fields
       Data fields should not be designed as a composite data field that contains several distinct
pieces of data. If a piece of information is significant, it should be stored as its own separate
data field. For example, the PID should actually have been separated into three separate data
fields: 1) Day care ID, 2) Participant ID, and 3) Participant Type. Avoiding composite data
fields would eliminate the need to write queries that separate out the bits of information
contained  within such fields, resulting in a more streamlined data extraction process.

                                           7-5

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(2)    Design and Test Key Linking Fields
       The key linking fields that allow a user access to all of the questionnaire, environmental,
and personal data for a given subject should be planned and tested for a small pilot study prior to
implementing them into a large study database.

(3)    Add Link Tables for User Friendliness
       Due to the complex nature of the CTEPP study design, it was not possible to have just
one key field that linked all of the collected and calculated data for a given subject.  As a result,
several fields needed to be considered when bringing data together across all samples collected
for a given subject.  In the case of a study that has several "many-to-many" tables within its
database (e.g., a single water sample is collected at a day care center, yet the analytical result for
this sample is applicable to all study subjects attending the day care center, while conversely, a
single study subject is associated with multiple samples such as urine, hand wipes, and food), an
additional link table should be added to make the database more user-friendly. Designing a
database containing many-to-many tables further complicates the relationships required to link
the environmental and biological data with the questionnaire  data.  These relationships are not
readily understood by those not intimately familiar with the study design.  Link tables provide a
user-friendly way of making use  of the key linking fields without requiring the user to
understand the relationships between those fields. An example of a useful link table is a table
that lists all  of the Sample IDs that are applicable for a given  participant and makes the
construction of the database queries that link environmental, biological, and questionnaire data
much simpler.

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                                       Chapter 8
                                  Statistical Analyses
8.1    Overview of Data Analysis

       Data for a variety of parameters were available for statistical analysis. These data
included the following:

•      Concentrations of target pollutants in environmental samples collected at homes and day
       care centers. Environmental samples included indoor and outdoor air (ng/m3), soil
       (ng/g), indoor floor dust collected via HVS3 vacuum (ng/m2 and ng/g), and drinking
       water (ng/mL; atrazine only). For homes with recent pesticide applications,
       concentration data were  available for dust collected via wipes from hard floors and food
       preparation surfaces (ng/m2) and for transferable residues collected from floors via PUF
       roller (ng/m2).  Concentration data in dust collected via wipes from hard floors were also
       available for some locations that did not have carpeted floors from which dust could be
       collected via HVS3 vacuum.
       Concentrations of target pollutants in personal samples collected from children and
       adults. Personal samples included duplicate diet solid food samples (ng/g), duplicate diet
       liquid food samples (ng/mL), and hand wipes (ng/m2).  Adult food samples were
       analyzed only for selected acid pollutants.
•      Information on characteristics, time spent at various locations, and activity patterns
       associated with the participating children and adults during the sampling period.
•      Concentrations of selected acid pollutants and metabolites in urine samples collected
       from the participating children and adults (ng/mL and (imoles/mole creatinine). For both
       North Carolina (NC) and Ohio (OH), these pollutants and metabolites included 2,4-D,
       l-hydroxybenz[a]anthracene, 3-hydroxychrysene, pentachlorophenol, and  3,5,6-TCP.
       For OH, seven additional metabolites were measured: 3-hydroxybenz[a]anthracene,
       3-hydroxybenzo[a]pyrene, 6-hydroxychrysene, 6-hydroxyindeno[l,2,3-cJ]pyrene,
       1-hydroxypyrene, IMP, and 3-phenoxybenzoic acid.

       Pollutant concentrations in multimedia samples (e.g., air, dust, soil, food) were combined
with information on activity patterns and physiological parameters to estimate daily  potential
exposure and absorbed dose for each participant by each of three exposure routes:  inhalation,
dietary ingestion, and indirect ingestion.1 Potential exposure, expressed in ng/day and
pmoles/day, is defined as the total amount of a pollutant that an individual comes in  contact with
over a 24-h period. Potential exposure is a route-specific parameter that was calculated from the
       1  Potential exposure and absorbed dose were not estimated for the dermal exposure route due to the
limited availability of adequate methods and sufficient background data in the literature.
                                           8-1

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measured concentrations in those exposure media (multimedia samples) that were relevant to the
given exposure route, along with the estimated contact rates with those media. Potential
absorbed dose, expressed in ng/kg/day and pmoles/kg/day, is defined as the total dose that could
be absorbed into the body over a 24-h period, relative to the participant's body weight. For each
exposure route, potential absorbed dose was estimated by assuming a 50% absorption rate for all
pollutants and participants (17). This was a conservative approach and was adopted due to the
lack of sufficient information available in the scientific literature for most CTEPP target
pollutants on the nature of their absorption into the body. Future research may allow these
results to be updated be performed on these data when more detailed and accurate absorption
rate information becomes available for certain pollutants. For a given study participant,
pollutant, and exposure route, potential exposure and potential absorbed dose were calculated if
the criteria  specified in Section 8.4 were achieved. Section 8.4 provides the detailed formulas
that were used to calculate potential exposure and potential absorbed dose.

      Aggregate potential exposure and aggregate potential absorbed dose were defined as
the sums of the estimated potential exposure and potential absorbed dose, respectively, across all
three exposure routes. Aggregate potential exposure and absorbed dose were calculated for the
following eight pollutants and metabolites that were frequently detected (at or above 50%) in
several types of multimedia:  bisphenol-A, chlorpyrifos, diazinon, di-w-butylphthalate, 2,4-D,
c/s-permethrin, frYms-permethrin, and 3,5,6-TCP.

       The concentrations of several parent compounds or their metabolites (specified above)
were measured in the urine of children and adults over the 48-h sampling period. Urine samples
were combined spot samples rather than total void samples. This was done primarily to prevent
placing undue burden on the participants if total void samples were to be collected across the 48-
h sampling period.  While using spot urine samples rather than total void samples has some
limitations  (e.g.,  not allowing for total volume over the 48-h period to be known), a steady-state
assumption was made which implied that exposures were chronic in nature.  This assumption
was reasonable given that information on individual half-lives of the pollutants were unknown,
pesticide applications were infrequent, and measured exposures tended to be low. The estimated
aggregate potential exposures and absorbed doses of the children were compared with the
concentrations of these pollutants in their urine.

       Monitoring data were available from a probability sample of 129 children and  129 adults
in North Carolina (NC) and a probability sample of 127 children and 127 adults in OH.  It is
important to note that the study design only permits the outcome of the statistical analyses to be
used to characterize the subpopulation of children who reside in the selected counties and who
participated in the CTEPP study. The results should not be used to make inferences on larger
populations of children, such as all children "in NC, OH, or in the United States," "in low-
income and middle/high-income families,"or "in day care centers."  Neither can the study
design permit results to be used to test hypotheses such as whether exposures differ significantly
between all NC children and all OH children. For this report, the statistical summaries and
analysis did not consider sample weights assigned to the study participants that would have
allowed the results to represent larger populations of children. Future analyses could be

-------
performed which calculate and take into account sampling weights, from which inferences could
be drawn for the populations from which the participants were randomly recruited, namely,
preschool children and their caregivers in the randomly-selected counties in NC and OH.

       Statistical analyses were conducted to meet each of the four goals detailed in Table 8.1.1.
Sub-goals are provided for three of the four goals.  Table 8.1.1 also provides an overview of the
types of statistical analyses used to address each goal or sub-goal. Details on the statistical
analysis approaches are given in Section  8.5.

8.2    Preparation for Statistical Analysis

       To prepare for the statistical analyses, several preliminary operations were performed on
the collected study data:

•      Because high and variable concentrations of selected pollutants were observed in some of
       the blank samples, it was necessary to apply a background correction to the measured
       concentrations for these pollutants in some matrices. Background correction to measured
       concentrations were performed in the following instances:

              for benzylbutylphthalate and di-w-butylphthalate in all sample media collected in
              both  states,
       -      for bisphenol-A in dust wipe samples collected in  NC, and
       -      for cis- and /rara'-permethrin in air samples collected in OH.

       The following procedure was used to correct for background contamination. For a given
       pollutant and matrix,  a t-test was applied to the blank data to determine if the mean blank
       value was significantly different from zero.  The mean blank value and an upper 95%
       confidence bound on  the mean were calculated. Then, background-corrected results were
       calculated by subtracting the mean value adjusted for sample volume, amount, or area
       (whichever is relevant for the given sample media).
•      Sample results labeled as "not detected" were replaced by the method detection limit
       (MDL) divided by the square root of two for all media except liquid food samples. The
       pollutant concentrations detected  in the liquid food samples were generally very low.
       When pollutants were detected in liquid food samples at levels close to the MDL, the
       signal-to-noise ratios  for the chromatograms were greater than three.  Therefore, not-
       detected results for the liquid food samples were replaced by the MDL divided by ten.

•      In the database, the concentrations of pollutants in dermal wipes were given in
       ng/sample. Prior to statistical analyses, this value was converted to a loading (ng/m2 of
       skin wiped).  For each study participant, a tracing of one hand was taken on a sheet of
       paper, and this tracing was cut out and weighed (in grams).  The following equation was
       then used to  calculate the dermal wipe loading (ng/m2):

-------
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calculated for each exposure route and analyzed using a logistic regression model
that contained effects for income status, urbanicity, and day care status and that
accounted for correlation between children attending the same day care center. (St
Section 8.5.2.3, analysis #1.)
Sub-goal 4.2: Wald chi-sauare tests were performed within the logistic regression
to test for significance of the effects in the regression model for a given exposure
route to determine whether the proportions differ significantly between two
specified groups of children. Estimates of the average proportion within each groi
and corresponding 95% confidence intervals were reported. (See Section 8.5.2.3,
analysis #1.)
Sub-goal 4.3 : Each study participant was represented by a three-dimensional vect<
of log-transformed potential exposure estimates for the inhalation, dietary, and
indirect routes, and a multivariate mixed-model ANOVA was performed on these
vectors. This model included fixed effects of income status, urbanicity, and day
care status and took into account correlation in measurements for children attendin
the same day care center, as well as correlation between a participant's three
exposure routes. A statistical test performed within this model fit determined
whether significant differences existed in the log-transformed exposure or dose
estimates among the three routes. (See Section 8.5.2.3, analysis #2.)
Sub-goals 4.4 and 4.5: Within the multivariate mixed-model ANOVA, pairwise

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                                T   ,.      A*D
                                Loading  =  	
       where A corresponds to the analytical measurement (ng), D equals the density of the
       paper on which the hand tracing was made (-80 g/m2), and W corresponds to the weight
       of the hand tracing (g). Since the hand wipe involved wiping the front and back of both
       hands, the reported weight of the hand tracing (W) was multiplied by four within this
       equation. Note that if a study participant had multiple wipe samples taken at home
       and/or day care over the 48-h period, the value of A for that participant at a particular
       location corresponded to the geometric mean of the multiple measurements taken at that
       location. If fFwas not reported for a given participant (one in NC, four in OH), then the
       average value for fFwas calculated from other participants within the same state and sex
       category and that were similar in age to the participant, and this average was used to
       calculate the participant's wipe loading.

•      Occasionally, such as when homes did  not have carpeted floors or when homes had
       recent pesticide applications, multiple hard floor surface wipes were collected in the
       same home. For each of these homes, the geometric mean of these  multiple wipe sample
       results was calculated (after replacing "not detected" values as mentioned above) and
       used in the statistical analysis. The geometric mean was labeled as "not detected" only
       when all results used in its calculation were labeled as "not detected."

•      A study participant may have had multiple urine samples taken due to recent pesticide
       application, or a child attending day care may have had urine samples taken both at home
       and at day care. In these situations, the geometric mean of a participant's urine sample
       results was calculated and used in the analyses. This geometric mean was labeled as "not
       detected" only when all results used in  its calculation were labeled as "not detected."

•      Urine sample concentrations  (in both ng/mL and pmoles/mL) were adjusted in two ways:
       1) by dividing by the sample's specific gravity, and 2) by dividing by the sample's
       creatinine level.  Creatinine-adjusted urine concentration was expressed in both ng/mg
       creatinine and (imoles/mole creatinine.  Descriptive statistics and statistical analyses were
       performed on unadjusted and adjusted urine concentrations, for both types of
       adjustments.

Data labeled as "unusable" by the study's quality control process were not used in statistical
summaries and analyses.  Measured concentrations were not adjusted based on the recoveries of
QC samples (e.g., surrogate recovery samples) prior to including them in summaries or analyses.
                                           8-7

-------
8.3    Strata Considered in the Statistical Analysis

       The study goals required the statistical analysis to make comparisons between different
strata that were determined according to urbanicity, the income status of the participating
families or day care centers, and the type of environment where samples were collected. The
different types of statistical analyses required that multimedia sample locations and study
participants be stratified.  The strata that were considered in the statistical analyses, along with
the criteria for placing sampling locations and study participants into strata, were as follows.

•      Urban and rural strata: Sampling locations and study participants were placed in the
       "urban" or "rural" stratum based on the county in which they were located or resided:
       •      NC locations and participants were placed in the "urban" stratum if they
              originated from Buncombe, Durham, Edgecombe, or Mecklenburg counties.
       •      OH locations and participants were placed in the "urban" stratum if they
              originated from Cuyahoga, Franklin, Hamilton, or Licking counties.
       •      NC locations and participants were placed in the "rural" stratum if they originated
              from Jones  or Lee counties.
       •      OH locations and participants were placed in the "rural" stratum if they originated
              from Defiance or Fayette counties.

       A county was classified as urban if it contained part of, or was contained within, a
       Metropolitan Statistical Area (MSA) as defined by the Office of Management and Budget
       (OMB Bulletin No. 99-04).  Counties not meeting this criterion were classified as rural.

•      Low-income and middle/high-income strata. Sampling locations from day care centers
       were placed  in the "low income" stratum if the day care center was a Head Start center
       and in the "middle/high-income" stratum otherwise. Sampling locations from
       households,  as well as all study participants  whether stay-at-home or at-day care, were
       placed in the "low income"  stratum if the household's income status (verified during
       recruitment) achieved the Women, Infants, and Children (WIC) program income
       guidelines for the period of  7/1/2000 to 6/30/2001, which was equivalent to falling below
       185% of the U.S. Poverty Income Guidelines, and were placed in the "middle/high-
       income" stratum otherwise.

•      Children enrolled in day care and children not enrolled in day care. Children were
       considered enrolled in day care if they attended one of the selected day care centers and
       were selected to participate  based upon meeting all study criteria.  Children verified as
       not attending a day care center or otherwise  meeting the day care criteria were labeled as
       not enrolled  in day care.

•      Children and adults in the same household.  When a child was recruited into the study, a
       primary caregiver residing in the same household was also identified to participate in the
       study by providing personal samples (e.g., food, dermal wipes, urine) and activity pattern
       information  needed to calculate potential exposure and potential absorbed dose.

-------
       Table 8.3.1 shows the number of participants in each stratum, for both the NC and OH
portions of the study.  Because one adult caregiver participated with each child in the study, the
number of children and adults in the study was the same within each stratum. While the number
of day care and stay-at-home children in the study was similar within each state, the number of
participants from urban settings was considerably higher than the number from rural  settings.  In
addition, more middle/high-income households participated in the study compared to low-
income households in each state, with the difference in number more apparent in OH. However,
a few households in each state did not have sufficient information to allow for their income level
to be categorized. Data associated with these households were not included in  summaries and
statistical analyses when the income status associated with each data value needed  to be
specified.

Table 8.3.1    Number of Study Participants in Each Stratum, by State
Stratum
Stay-at-Home Child
Child Attends Day Care
Low-income
Middle/High-income
Unknown income
Urban
Rural
Number of Participants
North Carolina
Children
66
63
59
66
4
108
21
Adults
66
63
59
66
4
108
21
Ohio
Children
69
58
41
73
13
110
17
Adults
69
58
41
73
13
110
17
8.4    Procedures for Calculating Potential Exposure and Potential Absorbed Dose

       Estimates of potential exposure were calculated for each study participant under the
inhalation, dietary ingestion, and indirect ingestion exposure routes using the equations given
below. Estimates of potential exposure via the dermal route were not calculated and were
assumed to be negligible.  For each participant and exposure route, the potential absorbed dose
estimate was calculated as 50% of the potential exposure estimate divided by the participant's
body weight (Ross et al., 2001)1. Aggregate potential exposure and aggregate potential absorbed
dose were defined as the sums of the potential exposure and potential absorbed  dose estimates,
respectively, across all three exposure routes.
         If a participant's body weight was not reported, then the average body weight for other participants
within the same state and sex category that were similar in age to the participant was calculated and used in
calculating the participant's potential absorbed dose. This approach was necessary for one NC child participant.

-------
       The concentrations of measured pollutants and metabolites in urine over the 48-h
sampling period were used as biomarkers of exposure in the study participants. The urinary
concentrations of pollutants and metabolites were compared between strata for children and
adults.

       For each state, Table 8.4.1 lists those pollutants and metabolites that were among those
detected in at least 50% of the samples in at least one media type (as seen in Section 9.2) and
which were considered for estimating potential exposure and potential absorbed dose in the
study participants.  Twenty-seven pollutants are listed for NC and 26 for OH. Eight of these
pollutants are denoted with an asterisk, as their detection rates were high in multiple media, and
some have been commonly found in household consumer products.  For these eight pollutants,
potential exposure  and absorbed dose were estimated in NC and OH children and adults for each
exposure route, and aggregate potential exposure and aggregate potential absorbed dose were
calculated in these  study participants across routes. For the remaining pollutants listed in Table
8.4.1, potential  exposure and potential absorbed dose were estimated in children  and adults for a
given exposure route and state only when the following criteria were satisfied for that pollutant:

•      Inhalation route: When at least 45% of the state's indoor air samples, or at least 45% of
       the state's outdoor air samples, have detected results (i.e., at or above the MDL)
•      Dietary  ingestion route: When at least 45% of the state's solid food samples, or at least
       45% of the  state's liquid food samples, have detected results
•      Indirect ingestion route: When at least 45% of the state's (vacuum) floor dust samples, or
       at least 45% of the state's soil samples, have  detected results.

       Unless otherwise specified, when any of the data entering into the equations below were
either not available, could not be assumed to be zero, or were labeled as invalid for a particular
study participant, then the potential exposure and potential absorbed dose was not estimated for
that participant  under the given exposure route, and as a result, aggregate potential exposure and
aggregate potential absorbed dose could not be calculated.  For purposes of the statistical
summaries and  analyses, potential exposure level and potential absorbed dose estimates were
labeled as "detected" when at least one of the concentrations entering into their calculation was
labeled as "detected."

8.4.1 Potential Exposure via Inhalation

       Potential exposure via inhalation (ng/day) is a weighted average of measured air
concentrations in the different environments in which the participant was present, with the
weights corresponding to the time spent in each environment, after adjusting for the participant's
estimated ventilation rate:
                                           8-10

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Table 8.4.1   Pollutants Considered for Estimating Potential Exposure and Potential
              Absorbed Dose for Study Participants in a Given State
Pollutant
B enz [a] anthracene
Benzo [6]fluoranthene
Benzo [&]fluoranthene
Benzo [g/z/]perylene
Benzo [a]pyrene
Benzo [ejpyrene
Benzylbutylphthalate
Bisphenol-A*
a/p/za-Chlordane
gamma-Chlordane
Chlorpyrifos*
Chrysene
Cyfluthrin
Diazinon*
NC
/
/
/
/
/
/
/
/
/
/
/
/
/
/
OH
/
/
/
/
/
/
/
/
/
/
/
/
/
/
Pollutant
Dibenz [a, h] anthracene
Di-w-butylphthalate*
p,p '-DDE
2,4-Dichlorophenoxyacetic acid*
Heptachlor
Indeno [ 1 ,2,3 -cc/jpyrene
Pentachlorophenol
c/'s-Permethrin*
/raws-Permethrin*
PCB52
PCB95
PCB 101
3,5,6-Trichloro-2-pyridinol*

NC
/
/
/
/
/
/
/
/
/
/
/
/
/

OH
/
/
/
/

/
/
/
/
/
/
/
/

* Pollutants for which potential exposure and potential absorbed dose were calculated for each exposure route for
the study participants in each state, and for which aggregate potential exposure and aggregate potential absorbed
dose were calculated (across exposure routes).
  Exp
                                    (chi*th) + (cho*tj + (caway*taway)

where the notation is as follows:
cdi  =
r    =
 away
tw   =
        Indoor air concentration in the participant's day care center classroom (ng/m3)
        Outdoor air concentration at the participant's day care center (ng/m3)
        Indoor air concentration in the participant's home (ng/m3)
        Outdoor air concentration at the participant's home (ng/m3)
        Air concentrations in indoor locations other than the participant's day care center or
        home where the participant may spend time (ng/m3)
        Time spent indoors at day care when indoor air is being sampled there (hr)
        Time spent outdoors at day care when outdoor air is being sampled there (hr)
        Time spent indoors at home when indoor air is being sampled there (hr)
                                           8-11

-------
tho   =  Time spent outdoors at home when outdoor air is being sampled there (hr)
taway  =  Time spent indoors at locations other than day care or home during the sampling period
        (hr)
V   =  Ventilation rate, estimated as follows from information in the EPA Exposure Factors
        Handbook:
        •     6.8 m3/day for children less than 36 months of age
        •     8.3 m3/day for children aged 36 months or higher
        •     11.3 m3/day for adult females
        •     15.2 m3/day for adult males

       For each of the participating children and their adult caregivers, an air sample was
collected over a 48-h period in each of the indoor and outdoor environments at their homes. In
addition, an air sample was collected over a 48-h period in each of the indoor and outdoor
environments of participating day care centers, with most centers having separate indoor air
samples taken in each classroom containing a participating child.  Thus, the values of Cdi, Cdo,
Cw, and Cho for a given participant were taken to be the measured concentrations  in the four air
samples associated with that participant.  However, no air samples were taken in  indoor
environments other than homes and day care centers to allow Caway to be estimated. Thus, to
arrive at a value for Caway, the median of all indoor air concentration measures taken in a given
state was calculated for each pollutant listed in Table 8.4.1, and this median, specified in
Appendix F, was taken to be the estimate of Caway for each study participant in that state.
Equation (8-2) does not include a term for air concentration in outdoor environments  away from
homes or day care centers, as the times spent in these other outdoor environments were assumed
to be trivial (i.e., near zero) for the study participants.

       For day care children, values of tdi and tdo in equation (8-2) were obtained from
information recorded on the Child Activity Diary and Food Survey (Form  10), completed by day
care teachers.  For  day care children and their adult caregivers, values of tw and tho were obtained
from information recorded on Child Activity Diary and Food Survey (Form 9), completed by day
care parents), and taway was calculated from information recorded on Forms 09 and 10. For stay-
at-home children and their adult caregivers, values of tM tho and taway were determined from
information recorded on Form 08 (Child Activity Diary and Food Survey,  completed  by "home"
parents). For stay-at-home children and all adult caregivers in the study who were not exposed
to a day care environment, tdi and tdo were both set equal to 0.

8.4.2  Potential Exposure via Dietary Ingestion

       Potential exposure level via dietary ingestion (ng/day) is a weighted sum  of measured
concentrations in both solid and liquid food within the day care and home  environments in  which
the participant was present, with each concentration multiplied by the amount of the collected
sample (representing  the total amount of food eaten by the participant):
                                          8-12

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        EXpd = [(Cdl *Mrf/)  +  (Cds *MJ +  (Cw *MW) + (Chs *MJ]   *  -            (8.3)
where the notation is as follows:

Cdl =  Concentration in liquid food sample collected in the participant's day care classroom
       (ng/mL)
Cds =  Concentration in solid food sample collected in the participant's day care classroom
(ng/g)
Mdl =  Total volume of liquid food sample collected in the participant's day care classroom (mL)
Mds =  Total weight of solid food sample collected in the participant's day care classroom (g)
Cu =  Concentration in the participant's liquid food sample collected at home (ng/mL)
Chs =  Concentration in the participant's solid food sample collected at home (ng/g)
Mu =  Total volume of the participant's liquid food sample collected at home (mL)
Mhs =  Total weight of the participant's solid food sample collected at home (g)
Nf  =  Number of days over which all food samples (liquid and solid) associated with the
       participant were collected.

       Because each food sample  at a given location for a given study participant corresponded
to a composite of total food consumed by the participant over a two-day period, the value of Nf
was set equal to two for each participant. Participants that drank only water at day care and/or
home were assumed to have liquid food sample concentrations (Cdl and Cu, respectively) of 0
ng/mL for that environment. Although Cdl and Cds were not measured for stay-at-home children
and for all adult caregivers, the values of Mdl and Mds for these participants were zero, and
therefore, these concentrations were not a factor in calculating the potential exposure level.

8.4. 3 Potential Exposure via Indirect Ingestion

       Potential  exposure via indirect ingestion (i.e., ingestion of dust and soil) (ng/day) is a
weighted average of measured floor dust and soil concentrations in the indoor and outdoor
environments, respectively, in which the study participant was present, with each concentration
scaled by the participant's assumed ingestion rate:

where the notation is as follows:
                                            1 "5
                                           -13

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Ddd =  Concentration in the day care center/classroom's HVS3 (vacuum) floor dust sample
       (ng/g)
Dds =  Concentration in day care center's play area soil sample (ng/g)
Dhd =  Concentration in home's HVS3 floor dust sample (ng/g)
Dhs =  Concentration in home's play area soil sample (ng/g)
Md =  Participant's estimated daily ingestion rate of dust (g/day)
Ms =  Participant's estimated daily ingesti on rate of soil (g/day)

and tdi, tdo, tw, and tho are defined in the same way as in equation (8-2) (i.e., times spent indoors
and outdoors in the day care and home environments).  For stay-at-home children and all adult
caregivers who were not exposed to a day care environment, tdi and tdo were both set equal to 0.
Any indirect ingesti on that might have occurred outside of the day care center and home
environments was assumed to be trivial, and therefore, was not included in equation (8-4). Daily
ingestion rates of dust and soil were estimated according to the published literature (15-16) and
from the collected questionnaire data on children's activity patterns. For participating children,
daily ingestion rates were estimated by placing each child into one of three groups (Groups A, B,
or C) according to information recorded on study survey forms on how often the child conducted
activities that could lead to dust and soil ingestion, such as teething, chewing,  and putting objects
into his/her mouth. For soil ingestion activity, responses from the following two questions on
Form 04 (parent pre-monitoring questionnaire) were evaluated:

       (1)     Question C5:  How often did [the child] play with sand or dirt?
       (2)     Question C6:  Which of the following have you seen your child eat: dirt, sand,
              snow?

For dust ingestion activity, responses from the following questions  on Form 04 were evaluated:

       (1)     Question C12: Did your child use a pacifier in the past month?
       (2)     Question C13a: In the past month, did [your child] suck or chew his/her
              thumb/fingers?
       (3)     Question C13b: In the past month, did [your child] suck or chew his/her toe/foot?
       (4)     Question C16: Did [your child] ever put his/her mouth on the floor and lick the
              floor?
       (5)     Question C21: Is your child currently teething?
       (6)     Question C22: How often did [your child]  put toys in his/her mouth?
       (7)     Question C23: Did [your child] put any things other than toys or food in his/her
              mouth?

       Algorithms were established to assign a daily soil ingestion rate and a daily dust
ingestion rates to a child based upon the responses to the above questions for that child, with the
specific rates that entered into the algorithms being  selected in conjunction with the published
literature (15-16). Appendix G provides details on these algorithms.  Separately for dust and  soil
ingestion, the algorithms placed children into Groups A, B, or C based upon whether their
                                           8-14

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activity levels were considered high, medium, or low, respectively. For both dust and soil, daily
ingestion rates were assigned as follows:

       •      Children in Group A: Daily ingestion rate = 0.100 g/day
       •      Children in Group B: Daily ingestion rate = 0.050 g/day
              Children in Group C: Daily ingestion rate = 0.025 g/day

For all participating adult caregivers, assigned ingestion rates were Md=25 mg/day for dust and
Ms=50 mg/day for soil.  Note that while the activity diaries and questionnaires provide useful
information for exposure assessment, they were not fully validated prior to their use in this
study.

8.5    Statistical Analysis

       This section details the methods associated with the statistical summaries and analyses
that were applied to the study data in order to address each of the study's goals and sub-goals.
The data were prepared for analysis as discussed in Section 8.2,  then were statistically
summarized and analyzed using Version 8 (Release 8.2) of the SAS®  System. These statistical
methods were applied independently to data from NC and OH.

8.5.1   Descriptive Statistics

       As mentioned in Table 8.1.1, descriptive statistics were generated on the study data in
order to address the following five goals or sub-goals:

•      Sub-goal 1.1: to quantify the distribution of target pollutants in multimedia samples at
       homes and day care centers
       Goal 2: to quantify the distribution of child characteristics, activities,  and locations that
       are important for exposure
       Sub-goal 3.1: to quantify the distribution of potential exposure and potential absorbed
       dose by exposure route
•      Sub-goal 3.2: to quantify the distribution of aggregate potential exposure and potential
       absorbed dose
•      Sub-goal 3.3: to quantify the distribution of urinary biomarker concentrations as an
       indicator of absorbed dose.

The SAS® System's UNIVARIATE procedure was applied to the relevant study data to  calculate
the descriptive statistics. For Goal 2, the list of summarized parameters and the descriptive
statistics calculated on these parameters were given in Table 8.1.1. For the four sub-goals, the
descriptive statistics included the sample size, mean (arithmetic  and geometric), standard
deviation (for untransformed and log-transformed data), percent of results labeled as detected,
minimum reported value, maximum reported value, and selected percentiles of the observed  data
distribution (25th, 50th, 75th, 95th ). Means and standard deviations were reported only when at
least 50% of the data entering into their calculation were detected. A given percentile was

                                           8-15

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reported only when the observed data values at the percentile exceeded the MDL. The
maximum reported value was reported only when at least one detected measurement was
reported, and the minimum reported value was reported only when 100% of the reported
measurements were detected. These descriptive statistics are included as appendices to this
report.

       Also, for the four sub-goals specified above, boxplots were prepared which portrayed the
distribution of observed data values as a box-type diagram, within which the 25th, 50th, and 75th
percentiles, the geometric mean, and the range of the data were expressed graphically. Details
on how to interpret the boxplots are given in Section 9.3.1.

8.5.2   Analysis of Variance (ANO VA) Modeling

       Model-based analysis of variance  (ANOVA) methods were applied to the study data in
order to address Sub-goal 1.2, Sub-goal 3.4, and Goal 4, as detailed in the three subsections
below. In each case, the ANOVAs were repeatedly applied to  different subsets of study data
using the SAS®  System's MIXED and GENMOD procedures, with each subset of data
associated with a specific target pollutant and media type/dose metric. While the ANOVA
approach applies when the data used in the analysis satisfies certain statistical assumptions, the
same approach was applied to each subset of data (i.e., each combination of pollutant and sample
type) when addressing a particular study goal.  This was done in order to maintain consistency in
approach across the repeated analyses, so that the outcomes of the analyses could be more
comparable across the pollutants and sample types.  Note that the outcome  of statistical analyses
of urine, potential exposure, and potential absorbed dose data was not affected by whether the
data were expressed in mass concentration or molar concentration units.

8.5.2.1    Sub-goal 1.2: To determine  on average how multimedia concentrations differ
          between urban and rural environments, low-income and middle  high-income
          environments, and microenvironments

       Multimedia (environmental and food) samples were collected at the homes and day care
centers of the participating children.  Within a day care center, indoor environmental samples
were linked to children by classroom. These two locations, along with an indicator of whether or
not a child attended day care, defined three possible microenvironments: 1) the day care
microenvironment; 2) the home microenvironment for stay-at-home children, and 3) the home
microenvironment for children attending day care. Additionally, multimedia samples were
classified by income status (low or middle/high) and urbanicity (urban or rural) according to the
microenvironment from which they were  collected.  The primary aim of the data analysis was to
make statistical  comparisons among the three microenvironments, although comparisons were
also made according to income  status and urbanicity.

       For a given multimedia sample type and pollutant (with the exception of dermal wipes),
let Yijk denote the log-transformed analytical measurement associated with a sample collected in
the ith environment type, where the sample is identified as follows:

                                          8-16

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       •      For samples collected in a day care center environment (i=l), the sample taken in
             the jth classroom within the kth day care center in the study.
       •      For samples collected in the home environment of a stay-at-home child (i=2), the
             sample collected in the kth home of this type in the study. (Here, j is assumed to be
             equal to one as only one sample was taken per home).
             For samples collected in the home environment of a day care child (i=3), the
             sample taken in the kth home of this type in the study. (Here, j is assumed to be
             equal to one as only one sample was taken per home.)

       Then, for a particular combination of pollutant and environmental/food sample type, the
following analysis of variance (ANOVA) model was applied to the log-transformed analytical
measurements Yijk:

                                                 + dk  + eVk                       (8-5)
where
H   =  an overall constant,
T|;   =  effect of originating from the ith environment type,
Yi   =  effect of originating from a middle/high-income environment versus a low income
       environment
Mik =  indicator of income status associated with the kth day care center or home within the 1th
       environment type (i.e., Mik=l if middle/high-income and =0 if low income),
Y2   =  effect of originating from an urban environment versus a rural environment
Uik =  indicator of urbanicity associated with the kth day care center or home within the ith
       environment type (i.e., Uy=l if an urban area and =0 if a rural area),
5jk  =  a random term corresponding to the kth home or day care center, and
sijk  =  a random error term representing random variation not explained by the model.

Because no interactions are included in the model, any interaction effects are included in the
random error term. The variance-covariance matrix of 5k was defined to account for correlation
in measurements for samples taken in different classrooms (j) within the same day care center
(k), while the variance-covariance matrix of sijk was defined under the assumption that the values
of sijk for different samples are independent.

       The statistical significance of environment type (r|;), income status (YI), and  urbanicity
(Y2) on the value of Yijk was determined by applying F-tests within the ANOVA, and significance
levels of these F-tests were reported. When the F-test for the effect of environment type (r|;) was
found to be significant at the 0.05 level and all three environment types were represented by the
data, multiple comparisons (using Tukey's studentized range test) were performed to identify
which of the three pairs of environment types differed significantly, and the significance levels
(adjusted for the multiple comparisons) associated with each of the three pairs were reported.
Additionally, a t-test was performed within the ANOVA to determine if the day  care
                                          8-17

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environment differed significantly with the mean of the two home environment types, and the
significance level of this test was also reported.

       To characterize how the analytical measurements differ between two strata (e.g., urban
vs. rural, low income vs. middle/high-income), the ANOVA model was used to estimate the
average log-transformed analytical measurement ("least squares mean") for each stratum. Then,
the difference in the least squares means of the two strata was calculated, a t-test was performed
within the ANOVA to determine whether this difference was statistically significant at the 0.05
or 0.01 levels, and a 95% two-sided confidence interval on this difference was also calculated
within the ANOVA.  The estimated difference in least squares means and its 95% confidence
interval were then exponentiated, resulting in a ratio of estimated geometric means between the
two strata and a corresponding 95% two-sided confidence interval on this ratio. The  estimated
ratio, its 95% confidence interval, and the outcome of the statistical test for significant difference
between the two strata were reported.

       Because a statistical comparison between home and day care environments was also of
interest, a linear contrast was constructed within the ANOVA to estimate the difference in
average log-transformed measurements between these two environments.  Because the home
environment consisted of two of the three microenvironments (i.e., the home environment for
day care children and the home environment for stay-at-home children), the linear contrast was
specified as the average log-transformed analytical measurement for the day care
microenvironment, minus the average of the average log-transformed analytical measurements
associated with the two home microenvironments. As with the other comparisons of strata, a t-
test was performed within the ANOVA to determine whether this difference between home and
day care environments was significant at the 0.05 or 0.01 levels, and a 95% two-sided
confidence interval on this  difference was calculated within the ANOVA. A ratio of estimated
geometric means between the home and daycare environments was also calculated, along with a
95% two-sided confidence  interval on this ratio.

       While all pollutants were considered in the analysis of environmental sample  data, model
(8-5) was applied to only those combinations of pollutant and multimedia samples that met the
following two criteria:

       •     At least 50% of the values of Yijk were labeled as detected.
       •     Values of Yyk were available for at least two of the three environment  types.

Within an application of the analysis, if data were available from only one of a given
microenvironment (e.g.,  data were available for only one day care center), then data for that
microenvironment were excluded from that application of the analysis. The check for whether at
least 50% of the values were detected occurred after any necessary data exclusions were made.

For the adult food sample type, microenvironments were relevant based upon whether or not
their child attended day care: home microenvironment for stay-at-home children (i=2), and home
                                          8-18

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microenvironment for day care children (i=3).  This is because all adult-specific data were
collected within the home microenvironment.

       A slightly different ANOVA model was used for analysis of dermal wipe data. Dermal
wipes were collected for each study participant (child and adult) at their home and, for day care
children, at their day  care center.  Thus, day care children could have up to two dermal wipe
measurements, corresponding to their home and day care microenvironments. The statistical
analysis of dermal wipe data, therefore, needed to take into account correlation in the day care
and home dermal wipe samples for day care children. In the analysis of dermal wipe data, let Yijk
denote the log-transformed analytical measurement associated with a dermal wipe sample
collected in the ith environment type, where the sample is identified as follows:

             For day care children, the sample taken in the ith environment (day care [i=l] or
             home  [i=3]) from the jth child enrolled in the kth day care center of the study.
             For stay-at-home children and for all adult participants, the sample collected in
             the kth home of the environment type determined by whether or not the child
             attends day care (i=2 or 3).  (Here, j is assumed to be equal to one as only one
             child and one adult participated from each home.)

The ANOVA model applied to the dermal wipe sample data took the following form:
                                                 +  dk +  eijk                       (8-6)
where the terms are as defined for equation (8-5) except for the following:

My =  indicator of income status associated with the jth study participant within the ith
       environment type (i.e., My=l if middle/high-income and =0 if low income),
Ujj  =  indicator of urbanicity associated with the jth study participant within the ith environment
       type (i.e., Uy=l if an urban area and =0 if a rural area),

Because no interactions are included in the model, any interaction effects are included in the
random error term (Sp). The variance-covariance matrix of 5k was defined to account for
correlation in measurements for samples taken from different children (j) within the same day
care center (k), while the variance-covariance matrix of suk was defined to account for
correlation in measurements for samples taken from the same child (j) at different environment
types (i) (i.e, day care and home).

       The results  for the tests of significance for environment, urbanicity, and income status on
the log-transformed analytical measurement, and their estimated geometric ratios and associated
95% confidence intervals, were reported in the same manner  as for the environmental/food
samples.  Model (8-6) was fitted separately for each pollutant, as well as separately for adults
and children.
                                          8-19

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8.5.2.2.    Sub-goal 3.4: To determine on average how potential exposure and absorbed dose
           metrics for each route and aggregated over routes differs between children in urban
           and rural settings, children in low and middle/high-income settings, day care children
           and stay-at-home children, and children and adults by stratum

        The analysis approach presented in this subsection was performed on the potential
exposure and absorbed dose estimates for the target pollutants listed in Table 8.4.1, when the
data for these pollutants achieved the criteria specified in Section 8.4 for a given exposure route.
The analyses were executed separately for each exposure route.  In addition, this approach was
performed on urine concentration data (both adjusted and unadjusted for specific gravity and
creatinine concentration), separately for each pollutant measured in urine, and on aggregated
potential exposure level and aggregated potential absorbed dose estimates, separately for each of
the eight pollutants labeled with asterisks in Table 8.4.1.

       Let j denote a specific household enrolled in the study. The analyses addressing Sub-
goal 3.4 were performed on the measures Yj, with separate analyses being conducted by
pollutant and for each of the following definitions of Y^:

       •      Log-transformed potential exposure level for the child in the jth household
              (separate analyses by exposure route)
              Log-transformed potential absorbed dose  for the child in the jth household
              (separate analyses by exposure route)
              Log-transformed aggregated potential exposure level for the child in the jth
              household
       •      Log-transformed aggregated potential absorbed dose for the child in the jth
              household
       •      Log-transformed unadjusted urine concentration for the child in the jth household
              Log-transformed urine concentration, adjusted for specific gravity, for the child in
              the jth household
              Log-transformed urine concentration, adjusted for creatinine, for the child in the
              jth household
       •      Difference in log-transformed potential exposure level between the  child and
              adult in the jth household (separate analyses by exposure route)
       •      Difference in log-transformed potential absorbed dose between the child and adult
              in the jth household (separate analyses by  exposure route)
              Difference in log-transformed aggregated potential exposure level between the
              child and adult in the jth household
              Difference in log-transformed aggregated potential absorbed dose between the
              child and adult in the jth household
       •      Difference in log-transformed unadjusted urine concentration between the child
              and adult in the jth household
       •      Difference in log-transformed urine concentration, adjusted for specific gravity,
              between the child and adult in the jth household
                                           8-20

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       •       Difference in log-transformed urine concentration, adjusted for creatinine,
              between the child and adult in the jth household.

The ANOVA model applied to data for a given combination of pollutant and Yj definition was
the following:
                          =  \i + Tj.  +  j2j  + j3j + e                           (8-7)
where
|i   = an overall constant,
Yi   = effect of a middle/high-income household versus a low income household,
Mj  = indicator of the jth household's income status (Mj=l if middle/high-income, =0 if low
       income),
Y2   = effect of an urban household versus a rural household,
Uj  = indicator of the jth household's urbanicity (Uj=l if urban, =0 if rural),
Y3   = effect of a child enrolled in day care versus staying at home,
Dj  = indicator of child's day care status in the jth household (Dj=l if day care, =0 if non-day
       care), and
Sj   = a random error term representing random variation not explained by the model.

The variance-covariance matrix of Sj was defined to account for correlation  in measurements
among households whose children attend the same day care center.

       In a given fitting of model (8-7), the statistical significance of urbanicity, income status,
and day care status on the value of Yj was determined by testing for the significance of their
corresponding coefficients in the model using F-tests and reporting the significance levels of
these tests. As in the previous models, because no interactions of these factors are included in
the model, only the main effects of these factors were tested. Thus, any interaction effects are
included in the model's random error term.

       When the definition of Yj corresponded to some child-specific measure (i.e.,  not a child
vs. adult difference), the ratio of estimated geometric means between two strata (e.g., urban vs.
rural,  low income vs. middle/high-income, day care vs. non-day care) were  reported for this
measure as in the previous models, along with 95% two-sided confidence intervals.  T-tests were
also performed to determine whether a particular ratio was significantly different from one,
implying no significant difference between the two strata represented by the ratio. When the
definition of Yj corresponded to a difference in measures between children and adults within the
same household, the ratio of estimated geometric means for children versus adults in the same
household were reported overall and for each stratum, along with 95% two-sided confidence
intervals. In addition, a one-sided t-test was performed within the model fitting that tested
whether, overall, children tended to have significantly higher measures than their adult
caregivers. For the individual strata, two-sided t-tests were performed to test whether children's
measures differed significantly from their adult caregivers.

                                           8-21

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8.5.2.3    Goal 4: To apportion the exposures through the inhalation, dietary ingestion, and
          indirect ingestion routes

       For the eight pollutants highlighted in Table 8.4.1 for which aggregated potential
exposure level and aggregated potential absorbed dose were estimated, this goal focuses on
characterizing how these aggregated estimates were apportioned across the three exposure routes
considered in this study (inhalation,  dietary ingestion, and indirect ingestion) and noting which
routes were more important contributors to aggregate potential exposure or aggregate potential
absorbed dose than others. As indicated in Table 8.1.1, this goal was divided into the following
five sub-goals:

       4.1    To estimate the proportion of aggregated exposure and dose that is associated
             with a given exposure route for the study children overall and by stratum.
       4.2   For each exposure route, determine if this proportion differs for children
              a.      in urban and rural settings
             b.      from low and middle/high-income families
              c.      who attend day care or stay at home
       4.3   Determine whether significant differences exist between exposure routes
       4.4    Characterize how these estimates differ overall between pairs of exposure routes
       4.5   Identify which pairs of exposure routes differ significantly in these estimates

To address each of these sub-goals, two types of analyses were developed and executed:

       •      Analysis #1 (Sub-goals 4.1 and 4.2):  Characterizes the proportion of the
              aggregated value that is associated with a specific exposure route, both overall
              and by stratum, and determines whether these proportions differ significantly
             between strata. This  analysis was performed separately by pollutant and exposure
             route.

             Analysis #2 (Sub-goals 4.3, 4.4, and 4.5): Compares average log-transformed
             measures between exposure routes. This analysis was performed separately by
             pollutant and for potential exposure and potential absorbed dose.

Each of these analysis approaches is now discussed.

       Analysis #1. When applied to a given exposure route, this analysis involved calculating
Pj, or the proportion of the estimated aggregated exposure that is associated with  the given
exposure route, for the jth participant. To make statistical comparisons of the value of PJ between
strata, the following logistic regression model was used:

                  log(p/(l-/?,))  =  |i + YjM, + j2Uj + j3Dj +  e.                      (g-S)
                                           8-22

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where the terms in this model are as defined for equation (8-7). Generalized estimating
equations were used to allow values of the proportion PJ associated with children enrolled in the
same day care center to be correlated.

       The presence of significant differences among strata was determined by testing the
statistical significance of the corresponding model coefficients via a Wald chi-square test.  For
example, the differences of the proportion between children living in urban areas and children
living in rural areas was investigated by testing for the significance of the y2 coefficient in model
(8-8). Significance levels of tests for significant differences between urban and rural strata,
between middle/high and low income strata, and between day care and non-day care strata were
reported, along with estimates and corresponding 95% confidence intervals for the average
proportion for each stratum.  The estimated average proportion for each stratum was determined
by solving model (8-8) for the value of PJ for the given stratum (i.e., calculating the inverse
logit).

       Because the proportion PJ is calculated for each participant for a given exposure route, the
outcome of this calculation is the same whether potential exposure level or potential absorbed
dose is used. This is because the absorption rate (50%) and the participant's body weight cancel
out from the numerator and denominator of the proportion equation.  Thus, for a given exposure
route, only one analysis was necessary between these two endpoints.

       Analysis #2.  To investigate whether potential exposure level or potential absorbed dose
differed significantly among the three exposure routes and among strata, this analysis involved a
multivariate ANOVA fitted to the log-transformed estimates for a given pollutant. This
approach is  similar to that discussed in Section 8.5.2.2, except the model is multivariate in nature
in that it is applied to the vector of three log-transformed estimates associated with each
exposure route. For the ith entry (or exposure route) in this vector (i=l, 2, 3), the multivariate
ANOVA model is as follows:

                                                   +  5y + %                         (8-9)
where
Yy  = log-transformed exposure or dose estimate for the jth study participant via the ith exposure
       route,
H   = an overall constant,
Yi   = effect of a middle/high-income household versus a low income household,
Mj  = indicator of the household income status for the jth study participant (Mj=l if
       middle/high-income, =0 if low income),
Y2   = effect of an urban household versus a rural household,
Uj  = indicator of the urbanicity of the household containing the jth study participant (Uj=l if
       urban, =0 if rural),
Y3   = effect of a child enrolled in day care versus staying at home,
                                             8T3
                                            -23

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Dj  =  indicator of child's day care status in the household containing the jth study participant
       (Dj=l if day care, =0 if non-day care),
5j   =  random day care center effect, which accounts for correlation between children attending
       the same day care center, and
Sj   =  a random error term representing random variation not explained by the model that
       accounts for correlation between  exposure routes for each participant.

When fitting model (8-9), a statistical test was performed to determine whether significant
differences existed in the log-transformed exposure or dose estimates among the three exposure
routes. Then, pairwise comparisons among the three exposure routes were performed, and the
results were reported.  In addition, the estimated ratio of geometric means between two exposure
routes were calculated and reported for each pair of routes, along with a 95% confidence interval
on the ratio.
                                           8-24

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                                       Chapter 9
                               Results and Discussion
9.1    Overview

       This chapter presents the results of the statistical analyses of the CTEPP study data.  The
presentation includes descriptive statistics and the outcome of statistical modeling efforts which
were performed to address the following four statistical goals:

       Goal 1:      To measure the environmental concentrations of pesticides and other
                    persistent and non-persistent organic pollutants in multimedia at the
                    homes and day care centers of a set of preschool children in several North
                    Carolina (NC) and Ohio (OH) counties.
•      Goal 2:      To quantify the distribution of child characteristics, activities, and
                    locations that are important for exposure.
•      Goal 3:      To estimate the exposures of the preschool children to these pollutants that
                    they may encounter in their everyday environments.
       Goal 4:      To apportion the exposures through the ingestion, inhalation, and dermal
                    routes.

The results presented in this chapter characterize only those children who participated in the
CTEPP study. The results should not be used to make inferences to larger populations of
children, such as all children "in NC, OH, or in the United States," "in low-income and
middle/high-income families,"  "in day care centers," etc.  Neither can the study design permit
results to be used to test hypotheses such as whether exposures differ significantly between all
NC children and all OH children.  The statistical analysis did not calculate sample weights
assigned to the study participants that would represent larger populations of children.

       Compound prevalence is reported for each pollutant by matrix for each state (section
9.2). Statistical analysis was conducted on the most  frequently detected pollutants. The results of
these analyses of the data that address the four specific goals of the study are presented in
sections 9.3 through 9.6.

9.2    Method Quantifiable Limits and Compound Prevalence

       The method quantifiable limits  (MQLs) were based on instrumental performance alone
and were estimated based on the lowest calibration standard that could be measured within 30%
of the true value and had a signal-to-noise ratio that  exceeded three to five. The method detection
limit (MDL) was defined as the minimum concentration at which a pollutant can be detected in a
sample and was estimated to be one-half of the MQL.

                                           9-1

-------
       High and variable concentrations were observed in blank samples for several pollutants
and matrices. These include:

       benzylbutylphthalate and di-w-butylphthalate in all sample media for both NC and OH,
•      bisphenol-A in NC wipe blanks, and
•      c/s-permethrin and fram'-permethrin in OH air blanks

For these pollutants and matrices, the MDL and MQL were calculated using the following
equations:
                                MDL = [z095*se(FMB)]/S

where za is the a* 100th percentile of the standard normal distribution (z095 = 1.645), se(FMB) is
the standard error of the measurements associated with field blanks, and S corresponds to the
sample volume, area, or weight, whichever is relevant for the given media type.

       For each pollutant and metabolite, the MDL was initially reported in mass units (ng) for
each collected multimedia sample and then converted to concentration units by dividing by the
sample volume, weight, or area. Tables 9.2.1 and 9.2.2 give the median MDL values for neutral
and acid pollutants, respectively, in the multimedia samples, while Table 9.2.3 provides the
median MDL values for pollutants and metabolites measured in urine samples.

       With some exceptions, median MDL values were the same or very similar across neutral
pollutants for a given media type (Table 9.2.1).  Median MDLs were somewhat higher for the
two phthalates compared to other neutral pollutants, mainly due to the background corrections as
described above. For bisphenol-A, nonylphenol, and cyfluthrin, the estimated instrumental
detection limits were about ten times the detection levels of the other neutral pollutants due to
their chromatographic properties and the relative abundances of the quantitation ions. For PCB
congeners, the median MDL in transferable residue (PUF) samples was twice as large for OH
than for NC  due to differences in sample matrices. Among acid pollutants and metabolites
measured in urine (Table 9.2.3), MDL values differed between the methylated
pollutants/metabolites (2,4-D, hydroxy-PAHs, and PCP) and the silylated metabolites (3,5,6-
TCP) due to the amounts of urine used for analysis (10 mL for the methylated
pollutants/metabolites versus 1 mL for the silylated metabolites) and their different detection
capabilities.

       For each pollutant, percentages of collected samples with  concentrations at or above the
MDL are presented by media type in Tables 9.2.4 and 9.2.5 for NC and OH, respectively.
Detection percentages associated with special samples collected from homes having recent
pesticide applications (i.e., hard floor and food preparation surface wipes, PUF samples) are
presented in Table 9.2.6 for NC and OH. Within these four tables, pollutants  with detection
percentages of at least 50% in a particular medium are shaded in gray.  Similar tables
                                           9-2

-------
Table 9.2.1    Median MDL Values for Neutral Pollutants Measured in Multimedia
                 Samples from North Carolina and Ohio
Pollutant3
Benzylbutylphthalate
Di-w-butylphthalate
Bisphenol-A
Nonylphenol
Cyfluthrin
cw-Permethrin
frvms-Permethrin
PCB congeners
All other neutral
pollutants a
Location
NC
OH
NC
OH
NC
OH
NC
OH
NC
OH
NC
OH
NC
OH
NC
OH
NC
OH
Median MDL Values
Indoor
Air
(ng/m3)
57
35
13
25
0.87
0.87
0.87
0.87
0.87
0.87
0.09
0.39
0.09
0.33
0.04
0.04
0.09
0.09
Outdoor
Air
(ng/m3)
57
35
13
25
0.87
0.86
0.87
0.87
0.87
0.87
0.09
0.38
0.09
0.33
0.04
0.04
0.09
0.09
Soil
(ng/g)
12
5.6
7.7
23
4.9
5.0
4.9
5.0
4.9
5.0
0.49
0.50
0.49
0.50
0.49
0.50
0.49
0.50
Dust
(ng/g)
50
22
32
94
20
25
20
20
20
20
2.0
2.0
2.0
2.3
2.0
2.0
2.0
2.0
Dermal
Wipe
(ng/m2)
6,400
8,000
1,900
8,200
320
280
320
280
320
250
32
32
32
32
32
32 b
32
32 b
Solid
Food
(ng/g)
52
5.7
62
18
0.83
0.83
0.83
0.83
0.83
0.83
0.08
0.08
0.08
0.08
0.08
0.08
0.08
0.08
Liquid
Food
(ng/mL)
27
18
22
7.4
0.33
0.33
0.33
0.33
0.33
0.33
0.03
0.03
0.03
0.03
0.03
c
0.03
0.03
Surface
Wipe
(ng/m2)
1,400
1,700
400
1,800
68
69
69
69
69
69
6.9
6.9
6.9
6.9
6.9
6.9
6.9
6.9
PUFd
(ng/m2)
4.4
4.4
4.4
4.4
44
44
44
44
44
44
4.4
4.4
4.4
4.4
4.4
8.8
4.4
4.4
a Atrazine is not showed in this table as it was measured only in drinking water samples. It had a median MDL value of 0.01 ng/mL for both NC
and OH.
b Across PCB congeners and all other neutral pollutants, median MDL values in Ohio ranged from 31 to 32 ng/m2.
0 Ohio liquid food samples were not analyzed for PCB congeners.
d There were no field blanks for PUF samples in NC and only one field blank for PUF samples in OH; the MDLs for the two phthalates in PUF
were not corrected for the background levels.
                                                     9-3

-------
Table 9.2.2   Median MDL Values for Acid Pollutants and Metabolites Measured in
              Multimedia Samples from North Carolina and Ohio
Pollutant/
Metabolite
Dicamba
2,4-D
IMP
Pentachlorophenol
2,4,5-T
3,5,6-TCP
Location
NC
OH
NC
OH
OH
NC
OH
NC
OH
NC
OH
Median MDL Values
Indoor
Air
(ng/m3)
0.17
0.17
0.17
0.17
0.09
0.09
0.17
0.17
0.17
0.09
0.09
Outdoor
Air
(ng/m3)
0.17
0.17
0.17
0.17
0.09
0.09
0.17
0.17
0.17
0.09
0.09
Soil
(ng/g)
0.40
0.40
0.40
0.40
0.20
0.40
0.40
0.40
0.40
0.20
0.20
Dust
(ng/g)
4.0
4.0
4.0
4.0
2.0
4.0
4.0
4.0
4.0
2.0
2.0
Dermal
Wipe
(ng/m2)
63
61
63
61
30
63
61
63
61
33
31
Solid
Food
(ng/g)
0.25
0.25
0.25
0.25
0.12
0.25
0.25
0.25
0.25
0.12
0.13
Liquid
Food
(ng/mL)
0.20
0.20
0.20
0.20
0.10
0.20
0.20
0.20
0.20
0.10
0.10
Surface
Wipe
(ng/m2)
14
14
14
14
6.9
14
14
14
14
6.9
6.9
PUF"
(ng/m2)
a
4.4
4.4
4.4
4.4
4.4
4.4
a A dash indicates that the pollutant was not measured in PUF samples.
b There were no field blanks for PUF samples in NC and only one field blank for PUF samples in OH.


Table 9.2.3   Median MDL Values for Pollutants and Metabolites Measured in Urine
              Samples from North Carolina and Ohio
Pollutant/Metabolite
2,4-D
l-hydroxybenz[a]anthracene
3-hydroxybenz[a]anthracene
3 -hydroxybenz[a]pyrene
3 -hydroxychry sene
6-hydroxychrysene
6-hydroxy indeno[l,2,3-c
-------
Table 9.2.4  Percentages of NC Samples With Detectable Pollutant and Metabolite Levels
            (At or Above the MDL) in Multimedia and Urine Samplesa
Pollutant/Metabolite b
Percentage of Results At or Above the MDL in Multimedia and Urine Samples
INDOORS
Indoor
Air
Dust
OUTDOORS
Outdoor
Air
Soil
PERSONAL
Dermal
Wipe
Solid
Food
Liquid
Food || Urine
OP Pesticides and Metabolite
Chlorpyrifos
Diazinon
3,5,6-TCP
100
100
99
100
96
100
83
51
88
18
16
69
80
51
98
63
22
99
11
0.68
40
c
-
97
OC Pesticides
Aldrin
alpha-Chlordane
gamma-Chlordane
p,p'-DDE
py-DDT
Dieldrin
Endrin
Heptachlor
Lindane
Pentachloronitrobenzene
41
99
100
31
34
40
34
93
14
14
16
96
97
41
38
45
18
43
15
2.8
8.6
54
64
0.71
12
14
41
61
11
2.9
0.0
31
31
15
20
13
4.2
4.9
6.3
0.0
3.1
59
61
3.6
6.7
4.9
2.2
20
3.1
0.45
2.6
16
18
58
3.9
2.0
0.65
14
7.2
0.65
0.0
5.4
0.0
21
2.0
0.0
0.0
0.0
2.0
1.4
-
-
-
-
-
-
-
-
-
-
Pyrethroid Pesticides
Cyfluthrin
c«-Permethrin
/r
-------
Table 9.2.4.   Percentages of NC Samples With Detectable Pollutant and Metabolite Levels
                 (At or Above the MDL) in Multimedia and Urine Samplesa (cont.)
Pollutant/Metabolite b
Percentage of Results At or Above the MDL in Multimedia and Urine Samples
INDOORS
Indoor
Air
Dust
OUTDOORS
Outdoor
Air
Soil
PERSONAL
Dermal
Wipe
Solid
Food
Liquid
Food || Urine
Phthalates
Benzylbutylphthalate || 34
Di-w-butylphthalate | 100
100 I! 6.4
100 1 39
34 I! 57
36 1 84
3.2
32
4.3 I!
30 1
Phenols
Bisphenol-A
Nonylphenol
Pentachlorophenol
65
9.5
97
29
4.5
93
31
2.1
95
2.9
1.9
32
94
1.3
31
88
2.6
7.8
79
4.6
1.5
-
-
75
PCBs
PCB44
PCB52
PCB70
PCB77
PCB95
PCB 101
PCB 105
PCB 110
PCB 118
PCB 138
PCB 153
PCB 180
48
91
47
0.0
75
53
6.8
42
24
13
21
4.7
20
36
22
0.0
38
38
5.7
42
26
20
30
12
24
65
18
0.0
44
26
0.71
19
8.6
2.9
2.9
0.71
1.4
4.2
1.4
0.0
2.8
3.5
2.1
7.1
5.6
9.9
9.2
7.7
1.8
6.7
1.8
0.0
8.5
11
0.89
12
8.0
2.2
3.6
0.89
1.3
7.2
0.0
0.0
2.6
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
-
-
-
-
-
-
-
-
-
-
-
-
PAH Metabolites Measured in Urine Only
l-hydroxybenz[a]anthracene ||
3-hydroxychrysene ||
«--
-
»--
-
-
-
»11
2.8
a The percentages were calculated using results from individual samples. Multiple samples for the same person or room were considered as
individual samples. Cells corresponding to pollutants having at least 50% of samples detected in the specified matrix are shaded in gray.
b In addition to the pollutants represented in this table, atrazine was measured in drinking water samples. Thirty-eight percent of NC drinking
water samples had atrazine levels at or above the MDL.
0 A dash indicates that the pollutant was not measured in the specified matrix.
                                                       9-6

-------
Table 9.2.5  Percentages of OH Samples With Detectable Pollutant and Metabolite Levels
            (At or Above the MDL) in Multimedia and Urine Samplesa
Pollutant/Metabolite b
Percentage of Results At or Above the MDL in Multimedia and Urine Samples
INDOORS
Indoor
Air
Dust
OUTDOORS
Outdoor
Air
Soil
PERSONAL
Dermal
Wipe
Solid
Food
Liquid
Food || Urine
OP Pesticides and Metabolites
Chlorpyrifos
Diazinon
IMP
3,5,6-TCP
99
98
95
100
100
97
87
99
75
74
86
88
39
32
40
80
61
39
25
94
66
17
86
99
7.1
1.9
33
36
c
-
__d
97
OC Pesticides
Aldrin
alpha-Chlordane
gararaa-Chlordane
py-DDE
p,;/-DDT
Dieldrin
Endrin
Heptachlor
Lindane
Pentachloronitrobenzene
2.7
93
97
35
22
12
12
34
4.1
11
3.5
86
85
48
39
21
7.0
5.6
11
0.70
1.4
56
59
2.8
2.1
7.0
19
18
3.5
3.5
2.1
55
51
42
29
17
2.8
2.1
0.70
0.0
0.45
29
29
4.5
3.6
0.45
2.7
2.2
1.8
1.3
0.65
7.1
5.8
73
5.2
8.4
1.3
7.8
3.2
1.9
0.65
0.0
0.0
6.5
1.9
0.0
0.0
1.3
1.3
0.0
-
-
-
-
-
-
-
-
-
-
Pyrethroid Pesticides and Metabolite
Cyfluthrin
cw-Permethrin
/r
-------
Table 9.2.5    Percentages of OH Samples With Detectable Pollutant and Metabolite Levels
                  (At or Above the MDL) in Multimedia and Urine Samplesa (cont.)
Pollutant/Metabolite b
Percentage of Results At or Above the MDL in Multimedia and Urine Samples
INDOORS
Indoor
Air
Dust
OUTDOORS
Outdoor
Air
Soil
PERSONAL
Dermal
Wipe
Solid
Food
Liquid
Food || Urine
Phthalates
Benzylbutylphthalate | 33
Di-w-butylphthalate || 97
100 I! 11
100 I 49
37 I! 46
58 | 45
58
25
6.6 I! -
3.3 1 -
Phenols
Bisphenol-A
Nonylphenol
Pentachlorophenol
65
0.68
88
51
3.6
94
35
0.0
60
2.1
2.4
50
98
1.3
47
100
1.3
22
71
0.0
4.3
-
-
92
PCBs
PCB44
PCB52
PCB70
PCB77
PCB95
PCB 101
PCB 105
PCB 110
PCB 118
PCB 138
PCB 153
PCB 180
31
88
36
0.0
63
55
5.4
44
23
9.5
17
2.7
24
50
25
0.0
42
45
14
48
41
28
41
16
15
66
14
0.0
36
25
2.8
21
8.5
2.8
1.4
0.0
15
20
19
0.70
23
25
20
31
30
31
34
22
7.6
19
14
0.0
7.6
11
2.7
12
8.5
1.3
2.7
0.45
0.0
5.8
0.0
0.0
0.65
0.65
0.0
0.65
1.3
0.65
1.3
0.0
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
PAH Metabolites Measured in Urine Only
1 -hy droxybenz [a] anthracene
3 -hy droxybenz [a] anthracene
3-hydroxybenz[a]pyrene
3-hydroxychrysene
6-hydroxychrysene
6-hydroxyindeno[ 1 ,2,3-o/]pyrene
1 -hy droxypyrene
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
12
1.1
0.0
0.67
0.90
0.0
62
a The percentages were calculated using results from individual samples. Multiple samples for the same person or room were considered as
individual samples. Cells corresponding to pollutants having at least 50% of samples detected in the specified matrix are shaded in gray.
b In addition to the pollutants represented in this table, atrazine was measured in drinking water samples. Fifty-nine percent of OH drinking water
samples had atrazine levels at or above the MDL.
0 A dash indicates that the pollutant was not measured in the specified matrix.
d Low recovery (<10%) of IMP was observed in matrix spikes, and therefore, IMP was not quantifiable in urine samples.

-------
Table 9.2.6   Percentages of NC and OH Samples With Detectable Pollutant and
            Metabolite Levels (At or Above the MDL) in Surface Samplesa
Pollutant/Metabolite
Percentage of Results At or Above the MDL in Samples Collected From
Homes After Recent Pesticide Applications
North Carolina
Hard Floor
Surface Wipe
Food Prep.
Surface Wipe
Trans.
Residue (PUF)
Ohio
Hard Floor
Surface Wipe
Food Prep.
Surface Wipe
Trans.
Residue (PUF)
OP Pesticides and Metabolites
Chlorpyrifos
Diazinon
IMP
3,5,6-TCP
91
69
__b
100
89
61
-
-
94
67
-
-
73
31
33
92
62
31
0.0
67
85
54
0.0
33
OC Pesticides
Aldrin
alpha-Chlordane
gararaa-Chlordane
py-DDE
py-DDT
Dieldrin
Endrin
Heptachlor
Lindane
Pentachloronitrobenzene
13
59
66
16
19
25
13
38
9.4
0.0
5.6
56
56
11
17
17
28
33
0.0
0.0
11
44
44
28
28
22
11
28
28
0.0
3.8
23
23
12
19
3.8
0.0
3.8
0.0
0.0
0.0
15
15
0.0
7.7
0.0
0.0
0.0
0.0
0.0
0.0
23
23
0.0
0.0
23
7.7
0.0
0.0
0.0
Pyrethroid Pesticides
Cyfluthrin
cw-Permethrin
/r
-------
Table 9.2.6   Percentages of NC and OH Samples With Detectable Pollutant and
              Metabolite Levels (At or Above the MDL) in Surface Samplesa (cont.)
Pollutant/Metabolite
Percentage of Results At or Above the MDL in Samples Collected From
Homes After Recent Pesticide Applications
North Carolina
Hard Floor
Surface Wipe
Food Prep.
Surface Wipe
Trans.
Residue (PUF)
Ohio
Hard Floor
Surface Wipe
Food Prep.
Surface Wipe
Trans.
Residue (PUF)
Phthalates
Benzylbutylphthalate || 97
Di-w-butylphthalate | 100
56
72
100 I! 77
100 | 65
54
85
100
100
Phenols
Bisphenol-A
Nonylphenol
Pentachlorophenol
81
0.0
43
89
0.0
-
100
6.3
-
96
0.0
33
85
0.0
0.0
71
8.3
33
PCBs
PCB44
PCB52
PCB70
PCB77
PCB95
PCB 101
PCB 105
PCB 110
PCB 118
PCB 138
PCB 153
PCB 180
9.4
22
13
0.0
13
6.3
0.0
19
9.4
3.1
3.1
3.1
22
22
17
0.0
22
17
0.0
28
17
0.0
11
0.0
11
6.3
17
0.0
13
20
22
10
33
0.0
17
5.6
12
38
50
0.0
3.8
7.7
12
38
15
0.0
3.8
0.0
7.7
7.7
15
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
15
50
23
0.0
31
46
7.7
46
23
7.7
23
0.0
a The percentages were calculated using results from individual samples. Multiple samples for the same person or room were considered as
individual samples. Cells corresponding to pollutants having at least 50% of samples detected in the specified matrix are shaded in gray.
b A dash indicates that the pollutant was not measured in the specified matrix.
documenting the percentages of samples with concentrations at or above the MQL are presented
by media type in Appendix H for NC and OH. These percentages take into account all samples
collected in the study within the given state for which a valid measurement for the pollutant was
available.

       For NC, pollutants and metabolites that were most commonly detected in the sampled
environmental and personal media were the following:

       The OP pesticides, chlorpyrifos and diazinon, were frequently detected in indoor air
       (100%), floor dust (>96%), transferable residue (>67%), surface wipe (>61%),  outdoor
       air (>51%), and dermal wipe (>51%) samples. The metabolite of chlorpyrifos, 3,5,6-
                                            9-10

-------
       TCP, had high detection rates in floor dust and hard floor surface wipes (100%), indoor
       air and solid food (99%), dermal wipe (98%), urine (97%), outdoor air (88%), and soil
       (69%) samples.

       Two OC pesticides, alpha- and gamma-chlordane, were both frequently detected in
       indoor air (>99%), floor dust (>96%), dermal wipe (>59%), surface wipe (>56%), and
       outdoor air (>54%) samples.

•      Two pyrethroid pesticides, cis- and trans-permethrin, were both frequently detected in
       floor dust (100%), surface wipe (>83%), transferable residue (83%), dermal wipe (82%),
       and  indoor air (>64%) samples.

       The acid herbicide, 2,4-D, had the highest detection percentages in urine (78%), floor
       dust (67%), and solid food (52%) samples.

•      All nine PAHs were frequently detected above 50% in dust, soil, and floor  surface wipe
       samples, except for dibenz[a,h]anthracene in floor surface wipes (34%).  These PAHs
       were frequently detected above 50% in  outdoor air and transferable residue samples,
       except for dibenz [a, h] anthracene.  Five  of these PAHs (benzo[&]fluoranthene,
       benzo[g/7/']perylene, benzo[a]pyrene, chrysene, and indeno[l,2,3-cJ]pyrene) were
       detected in at least 50% of indoor air samples, while two other PAHs
       (benzo[a]anthracene and benzo[e]pyrene) were detected in slightly below 50% of the
       indoor air samples.

•      The two phthalates, benzylbutylphthalate and di-w-butylphthalate, were frequently
       detected in floor dust (100%), transferable residue (100%), floor surface wipe (>97%),
       dermal wipe (>57%), and food preparation surface wipe (>56%) samples.  In addition,
       di-w-butylphthalate was detected in 100% of indoor air samples.

       Among the phenols, bisphenol-A was detected most frequently in transferable residue
       (100%), dermal wipe (94%), solid food (88%), surface wipe (>81%), and liquid food
       (79%) samples.  Pentachlorophenol was detected most frequently in indoor air (97%),
       outdoor air (95%), floor dust (93%), and urine (75%) samples.

For OH, pollutants and metabolites that were most commonly detected in the environmental and
personal media were the following:

       The OP pesticides, chlorpyrifos and diazinon, were both frequently detected in indoor air
       (>98%), floor dust (>97%), and outdoor air (>74%) samples. The two OP  metabolites,
       IMP and 3,5,6-TCP, were also frequently detected in indoor air (>95%), floor dust
       (>87%), and outdoor air (>86%) samples. In addition, 3,5,6-TCP was detected frequently
       in solid food (99%), urine (97%), dermal wipe (94%), floor surface wipe (92%), and soil
       (80%) samples.
                                         9-11

-------
•      Two OC pesticides, alpha- and gamma-chlordane, were both frequently detected in
       indoor air (>93%) and floor dust (>85%) samples, while detection percentages for
       outdoor air (>56%) and soil (>51%) samples were somewhat lower but still above 50%.

       Two pyrethroid pesticides, cis- and rram'-permethrin, were both frequently detected in
       floor dust (100%), dermal wipe (82%), hard floor surface wipe (69%), and transferable
       residue (69%) samples. Cyfluthrin was detected in 74% of the floor dust samples. A
       urinary metabolite of cis- and ^raws-perm ethrin, 3-PBA, was found in 60% of urine
       samples.

•      The acid herbicide, 2,4-D, was frequently detected in floor dust (96%) and urine (92%)
       samples.

       The PAHs were frequently detected in floor dust (>99%),  soil (>75%), floor surface wipe
       (>62%), transferable residue (>62% for all but dibenz[a,h]anthracene), and dermal wipe
       (>58% for all but dibenz[a,/z]anthracene) samples.

•      The two phthalates, benzylbutylphthalate and di-w-butylphthalate, were both detected
       most frequently in floor dust (100%), transferable residues (100%), and floor surface
       wipes (>65%). In addition, di-w-butylphthalate was detected in 97% of indoor air
       samples and 85% of food preparation surface wipe samples.

       Among the phenols, bisphenol-A was detected most frequently in solid food (100%),
       dermal wipe (98%), surface wipe (>85%), liquid food (71%), and transferable residue
       (71%) samples. Pentachlorophenol was detected most frequently in floor dust (94%),
       urine (92%),  and indoor air (88%)  samples.

       For each state, the detection percentages in Tables 9.2.4 through 9.2.6 were used to
classify the pollutants and metabolites measured in multimedia samples into the following three
groups:

•      Frequently Detected - pollutants detected in 50% or more of samples in 4 or more
       different media types.
•      Sometimes Detected - pollutants detected in 50% or more  of samples  in 1, 2, or 3 media
       types.
       Rarely Detected: pollutants detected in less than 50% of the samples in all media types.

Results of this classification for each state are presented in Table 9.2.7.
                                          9-12

-------
Table 9.2.7   Pollutants Were Classified Into Three Groups, By State, Based On Their
             Level of Detection in the Multimedia Samples
              North Carolina
                            Ohio
 OP pesticides/metabolites
 Chlorpyrifos, Diazinon, 3,5,6-TCP
 OC pesticides
 alpha-Chlordane, gamma-Chlordane
 Pyrethroid pesticides
 c/5-Permethrin, tmns-Permethrin
 PAHs
 Benz[a]anthracene, Benzo[&]fluoranthene,
 Benzo[&]fluoranthene, Benzo\ghi\pery 1 ene,
 Benzo[a]pyrene, Benzo[e]pyrene, Chrysene,
 Indeno[l,2,3-cJ]pyrene,
 Phthalates
 Benzylbutylphthalate, Di-w-butylphthalate
 Phenols
 Bisphenol-A, Pentachlorophenol
 PCBs
 None
 OC pesticides
 p,p '-DDE, Heptachlor
 Pyrethroid pesticides
 Cyfluthrin
 Acid Herbicides
 2,4-D
 PAHs
 Dib enzo [a, h] anthracene
 PCBs
 Congeners 52,  95, 101
Frequently Detected
          OP pesticides/metabolites
          Chlorpyrifos, Diazinon, IMP, 3,5,6-TCP
          OC pesticides
          a^/za-Chlordane, gamma-Chlordane
          Pyrethroid pesticides
          c/5-Permethrin, ^raws-Permethrin
          PAHs
          B enz [a] anthracene, B enzo [b] fluoranthene,
          Benzo[&]fluoranthene, Benzo[g/7/']perylene,
          Benzo[a]pyrene, Benzo[e]pyrene, Chrysene,
          Indeno[ 1,2,3 -c d]pyrene
          Phthalates
          Benzylbutylphthalate, Di-w-butylphthalate
          Phenols
          Bisphenol-A, Pentachlorophenol
          PCBs
          Congener 52
Sometimes Detected
          OC pesticides
          p,p '-DDE
          Pyrethroid pesticides
          Cyfluthrin
          Acid Herbicides
          2,4-D
          PAHs
          Dib enz [a, h] anthracene
          PCBs
          Congeners 70,  95, 101
                                         9-13

-------
Table 9.2.7   Pollutants Were Classified Into Three Groups, By State, Based On Their
             Level of Detection in the Multimedia Samples (cont.)
              North Carolina
                   Ohio
                                   Rarely Detected
 OC Pesticides
 Aldrin, p,p '-DDT, Dieldrin, Endrin,
 Lindane, Pentachloronitrobenzene
 Acid Herbicides
 Dicamba, 2,4,5-T
 Phenols
 Nonylphenol
 PCBs
 Congeners 44, 70, 77, 105, 110, 118, 138,
 153, 180
OC Pesticides
Aldrin, p,p '-DDT, Dieldrin, Endrin,
Heptachlor, Lindane, Pentachloronitrobenzene
Acid Herbicides
Dicamba, 2,4,5-T
Phenols
Nonylphenol
PCBs
Congeners 44, 77, 105, 110, 118, 138, 153,
180
       The pollutants and metabolites that are classified as "frequently" or "sometimes"
detected in Table 9.2.7 were among those considered for calculating potential exposure level and
potential absorbed dose of these pollutants in the study participants. Although IMP was
classified as "frequently" detected in OH multimedia samples, it was not measured in NC
multimedia samples.

       For the study participants, aggregate exposure level and aggregate potential absorbed
dose were calculated for bisphenol-A (BPA), chlorpyrifos (CPS), diazinon (DZN), di-n-
butylphthalate (DBF), 2,4-D, cis- and trans- permethrin (cis- and trans-P), and the metabolite
3,5,6-TCP (TCP). These eight pollutants/metabolites were detected in a majority of samples
across multiple media, including urine, and some were commonly found in consumer products
used by the participating households and day care centers.

9.3    Goal 1:  To Measure the Environmental Concentrations of Pesticides and Other
       Persistent and Non-Persistent Organic Pollutants in Multimedia (Environmental
       and Personal Samples) at Participating Homes and Day Care Centers.

       Goal 1 focused on quantifying the concentration of each pollutant by medium and
determining whether these concentrations differed significantly between microenvironments
(i.e., urbanicity, income level, home versus day  care environments).
                                         9-14

-------
9.3.1   Sub-goal 1.1: To Quantify the Distribution of Target Pollutants in Multimedia at
       Participating Home and Day Care Centers

       Descriptive statistics for pollutant and metabolite concentrations in multimedia samples
are given in Appendix I for NC and Appendix J for OH. These appendices display the
descriptive statistics (number of samples, percentage of samples with detected results, arithmetic
mean, standard deviation, geometric mean, log standard deviation, selected percentiles [25th, 50th,
75th, and 95th], and range) within two tables for each measured pollutant. For a given sample
type, descriptive statistics are presented separately for samples collected at the homes of study
participants and for samples collected at participating day care centers.  In addition, for the home
environment, descriptive statistics are presented separately for the homes of day care children
and the homes of stay-at-home children. In these tables, the arithmetic and geometric means, as
well as the standard deviations for both untransformed and log-transformed measurements, are
specified only when more than 50% of the  data entering into their calculation exceeded the
MDL.  In addition, percentiles of the observed data distribution are reported when the data
values at the percentile exceeded the MDL, otherwise "
-------
Table 9.3.1   Median Levels of 27 Target Pollutants in NC Multimedia Samples Collected
                from Home Environments"
Pollutant/Metabolite
Median Values
INDOORS
Indoor
Air
(ng/m3)
Dust
(ng/g)
Dust
(ng/m2)
Hard
Floor
Wipe
(ng/m2)
Food
Prep.
Wipe
(ng/m2)
Trans.
Residue
(PUF)
(ng/m2)
OUTDOORS
Outdoor
Air
(ng/m3)
Soil
(ng/g)
PERSONAL
Dermal
Wipe
ng/m2)
Solid
Food
(ng/g)
Liquid
Food
(ng/mL)
Urine
(ng/mL)
OP Pesticides and Metabolite
Chlorpyrifos
Diazinon
3,5,6-TCP
6.2
2.0
1.9
140
18
96
94
16
83
68
11
50
69
16
--
35
33
--
0.27
0.090
0.23

-------
Table 9.3.2   Median Levels of 27 Target Pollutants in NC Multimedia Samples Collected
                from Day Care Center Environments"
Pollutant/Metabolite
Median Values
INDOORS
Indoor
Air
(ng/m3)
Dust
(ng/g)
Dust
(ng/m2)
Hard
Floor
Wipe
(ng/m2)
Food
Prep.
Wipe
(ng/m2)
Trans.
Residue
(PUF)
(ng/m2)
OUTDOORS
Outdoor
Air
(ng/m3)
Soil
(ng/g)
PERSONAL
Dermal
Wipe
ng/m2)
Solid
Food
(ng/g)
Liquid
Food
(ng/mL)
Urine
(ng/mL)
OP Pesticides and Metabolite
Chlorpyrifos
Diazinon
3,5,6-TCP
3.0
2.3
0.93
140
65
66
570
180
200
130
33
53
_=
--
--
--
--
--
0.34
0.12
0.13

-------
Table 9.3.3   Median Levels of 26 Target Pollutants in OH Multimedia Samples Collected
                from Home Environments"
Pollutant/Metabolite
Median Values
INDOORS
Indoor
Air
(ng/m3)
Dust
(ng/g)
Dust
(ng/m2)
Hard
Floor
Wipe
(ng/m2)
Food
Prep.
Wipe
(ng/m2)
Trans.
Residue
(PUF)
(ng/m2)
OUTDOORS
Outdoor
Air
(ng/m3)
Soil
(ng/g)
PERSONAL
Dermal
Wipe
ng/m2)
Solid
Food
(ng/g)
Liquid
Food
(ng/mL)
Urine
(ng/mL)
OP Pesticides and Metabolite
Chlorpyrifos
Diazinon
3,5,6-TCP
1.7
0.97
0.63
52
20
41
64
22
38
24
<
9.0
12
<
7.6
20
7.3
<
0.20
0.17
0.23

-------
Table 9.3.4   Median Levels of 26 Target Pollutants in OH Multimedia Samples Collected
                from Day Care Center Environments"
Pollutant/Metabolite
Median Values
INDOORS
Indoor
Air
(ng/m3)
Dust
(ng/g)
Dust
(ng/m2)
Hard
Floor
Wipe
(ng/m2)
Food
Prep.
Wipe
(ng/m2)
Trans.
Residue
(PUF)
(ng/m2)
OUTDOORS
Outdoor
Air
(ng/m3)
Soil
(ng/g)
PERSONAL
Dermal
Wipe
ng/m2)
Solid
Food
(ng/g)
Liquid
Food
(ng/mL)
Urine
(ng/mL)
OP Pesticides and Metabolite
Chlorpyrifos
Diazinon
3,5,6-TCP
2.0
0.96
0.71
170
40
58
450
220
170

-------





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-------
Each boxplot shows the distribution as a box-type diagram, where the lower and high limits of
the box represent the 25th and 75th percentiles, respectively, of the observed data distribution.
The length of the box (from top to bottom) represents the data's interquartile range (IQR), or the
difference between the 75th and 25th percentiles, and is an indicator of data variability. A
horizontal line within the box represents the 50th percentile, or median.  The geometric mean is
plotted with an open circle.  Vertical lines extend from the top and/or bottom of the box to the
value of the most extreme data point which falls within 1.5 IQRs from the box. Each data point
extending beyond 1.5 IQRs  from the box is plotted by an asterisk.  Abbreviations for the
pollutants that are specified  along the horizontal axis of each figure were defined in the last
paragraph of Section 9.2.

       The boxplots show that, even when plotted using a logarithmic vertical axis, most data
distributions for the eight pollutants and metabolites show skewness toward lower levels within
all sample media, and most contain several measurements within the upper quartile that are at a
considerable distance from the distribution's 75th percentile (i.e., top of box).  This supports the
approach of performing data analyses on log-transformed data, although some skewness remains
in the distribution of the  log-transformed data. Boxplots portrayed as very short boxes (e.g.,
measurements of the two permethrins within outdoor air samples from NC and OH) represent
measurements that are nearly constant, which occurs most often when a large  percentage of
measurements are not detected.  Other observations include the following:

       Indoor air and floor dust measurements tend to cover wider ranges than outdoor air and
       soil measurements, especially inNC.

•      Soil concentrations tend to have highly skewed distributions across all pollutants,
       although on average, these concentrations are lower than for indoor dust.

       The distributions of loadings from surface wipe samples tend to be consistent between
       different surface types.

       Di-w-butylphthalate is frequently associated with higher measurements across the
       pollutants and metabolites, especially with regard to  concentrations in  air, dust, soil, and
       food samples.

9.3.2   Sub-goal 1.2: To Determine on Average How Multimedia Concentrations Differ
       Between Urban and Rural Environments, Low-Income and Middle/High-Income
       Environments, and Microenvironments (i.e.,  home for families with stay-at-home
       children, home for families with day care children,  and day care centers)

       To address this sub-goal, statistical analysis was performed on log-transformed
measurements whenever at least 50% of these measurements were detected for a given pollutant
and multimedia sample type. An analysis of variance using  models (8-5)  and  (8-6) from Section
8.5.2.1 was performed to calculate a least squares mean of the log-transformed measurements for
each environment type and microenvironment of interest.  For a given pair of  environment types

                                          9-25

-------
or microenvironments, the difference in the least-squares mean concentrations was calculated
within the analysis of variance along with a 95% confidence interval on this difference, and a li-
test was applied to test whether the difference was statistically significant.  This difference and
its confidence interval were exponentiated back to regular units, resulting in a ratio of the least-
squares geometric mean concentrations for one environment type versus another and an
approximate 95% confidence interval on this ratio.

       For ease of discussion here and throughout Chapter 9, children recruited from the child
day care sampling frame are referred to as "day care children," while those from the telephone
screening sampling frame are referred to as "stay-at-home children." Analyses were performed
and results are reported separately for NC and OH phases of the study, and pollutants are
addressed according to their chemical class.  Because no day care centers in this study had recent
pesticide applications prior to multimedia sampling, no data were available from day care centers
for food preparation surface wipes and transferable residue samples. In addition, no adult food
or dermal wipe data were available for the day care environment.

       For indoor and outdoor environmental  samples and personal (food) samples, ratios and
their 95%  confidence intervals are presented by pollutant and sample type in Appendix K (Table
K-l for NC and Table K-2 for OH). These ratios are of the least-squares geometric mean
concentration for the first environment type specified in the column heading versus the second
specified type, and 95% confidence intervals are shown in parentheses. The t-test applied to the
log-transformed data also is a test of whether this ratio differs significantly from one; p-values
associated with these tests are also given in Appendix K (Table K-3 for NC and Table K-4 for
OH).  Within these tables,  p-values for tests that compare a specific pair of microenvironments,
as well as home versus day care environments, are presented only when the test for general
differences among the three microenvironments was significant at the 0.05 level.

       Table 9.3.5 has condensed the information provided within Tables K-l and K-2 of
Appendix K for a given  sample type by presenting only those pollutants whose ratios were
significantly different from one at the 0.05 level for pairs of strata determined by urbanicity,
income status, or environmental type. Within Table 9.3.5, a dashed cell indicate that the
statistical analysis was not performed because either the study design did not permit such
analysis or the data were less than 50% detected.  A blank cell means that the ratio was not
significantly different from one at the 0.05 level.  If a pollutant or sample type does not appear in
this table, then none of the estimated ratios were significantly different from one at the 0.05
level.

       To illustrate how to interpret the numbers in Tables K-l and K-2 of Appendix K and
Table 9.3.5, consider the results presented for a^>/za-chlordane in NC indoor floor dust (ng/m2).
Results of the model  fitting indicated that the least squares mean log-transformed measure was
4.69 for the low-income stratum and 3.93 for the middle/high-income stratum (data not shown).
The difference in these two least squares means is 0.76, which when exponentiated, becomes
2.13.  It is interpreted as the estimated ratio of least-squares geometric mean concentrations
between low-income and middle/high-income environments, and it implies that the geometric
mean of a^/za-chlordane in floor dust (ng/m2) was estimated to be 113% higher in low-income

                                           9-26

-------
Table 9.3.5.  Environmental and Food Samples: Estimated Ratios of Geometric Mean
            Pollutant Levels Between Urban and Rural, Low-Income and Middle/High-
            Income, and Home and Day Care Environments, When These Ratios Were
            Significantly Different from One at the 0.05 LeveP
Pollutant/Metabolite
Sample
Medium1"
Estimated Ratio of Geometric Means
(When Significantly Different from 1 at the 0.05 Level)
North Carolina
Urban vs.
Rural
Low- vs.
Mid/High-
Income
Home vs.
Day Care
Ohio
Urban vs.
Rural
Low- vs.
Mid/High-
Income
Home vs.
Day Care
OP Pesticides and Metabolites
Chlorpyrifos
Diazinon
IMP
3,5,6-TCP
Outdoor air
Dust (ng/g)
Dust (ng/m2)
C-solid food
Indoor air
Outdoor air
Dust (ng/g)
Dust (ng/m2)
Indoor air
Outdoor air
Dust (ng/m2)
Indoor air
Outdoor air
Soil
Dust (ng/m2)
C-solid food








--
--
--





0.64*

2.88**

3.59**

2.06*
6.32**
--
--
--

0.65*

3.40**
0.48**


0.27*



0.36*
0.10**
--
--
--

1.84*
2.29*







2.70**



3.87**



2.80**



2.09*
3 39**
2.06**

0.60*

2.24*
1.66*
0.48**

1.72*


2.35*

1.74*
0.37*
0.14**




0.17**


0.39*



0.29**

OC Pesticides
alpha-Chlordane
gamma-Chlordsme
Outdoor air
Soil
Dust (ng/g)
Dust (ng/m2)
Outdoor air
Dust (ng/g)
Dust (ng/m2)

--






--

2.13*
1.60*


0.44**
--
0.42*
0.09**
0.41*
0.40*
0.09**








2.12*





1.63*
2.80*


1.62*


Pyrethroid Pesticides
Cyfluthrin
cw-Permethrin
trans-Permetbnn
Dust (ng/g)
Dust (ng/m2)
Indoor air
Dust (ng/m2)
Indoor air
Dust (ng/m2)
--
--




--
--
4.17**
3.19**
3.85**
2.89*
--
--

0.18**

0.16**
2.33*

--

--


2.12*
--
2.21*
--


0.23**
--
0.20**
--
0.19**
                                      9-27

-------
Table 9.3.5.  Environmental and Food Samples: Estimated Ratios of Geometric Mean
            Pollutant Levels Between Urban and Rural, Low-Income and Middle/High-
            Income, and Home and Day Care Environments, When These Ratios Were
            Significantly Different from One at the 0.05 LeveP (cont.)
Pollutant/Metabolite
Sample
Medium1"
Estimated Ratio of Geometric Means
(When Significantly Different from 1 at the 0.05 Level)
North Carolina
Urban vs.
Rural
Low- vs.
Mid/High-
Income
Home vs.
Day Care
Ohio
Urban vs.
Rural
Low- vs.
Mid/High-
Income
Home vs.
Day Care
Acid Herbicides
2,4-D
Dust (ng/g)
Dust (ng/m2)
C-solid food0
3.20**
2.64*
1.60*
0.22**





2.38*

--
0.24**
0.39*
--

0.38*
--
PAHs
Benz[a]anthracene
Benzo[&]fluoranthene
Benzo[fc]fluoranthene
Benzofg/w'Jperylene
Benzo[a]pyrene
Benzo[e]pyrene
Chrysene
Outdoor Air
Soil
Dust (ng/g)
Dust (ng/m2)
Indoor air
Soil
Dust (ng/g)
Dust (ng/m2)
Soil
Dust (ng/g)
Dust (ng/m2)
Indoor air
Soil
Dust (ng/g)
Dust (ng/m2)
Indoor air
Outdoor air
Soil
Dust (ng/g)
Dust (ng/m2)
Soil
Dust (ng/g)
Dust (ng/m2)
Indoor air
Soil
Dust (ng/g)
Dust (ng/m2)
1.58*















1.47*











2.55**
0.54**

1.95**
2.54*
0.57**

2.21*
0.56**

1.76**
2.49**
0.57**

1.94**

2.30*
0.55**

2.49**
0.60*

1.76**
2.53**
0.59*




0.12**



0.12**


0.13**



0.12**




0.13**


0.12**



0.12**


3 97**
3.19**
-

3.63**
2 92**

3.35**
2.70*
-

3.28**
2.64*
-
-

3.57**
2.87*

3.40**
2.73*
-

3.71**
2 99**


0.58*

-

0.57*


0.58*

-

0.56*

-
-

0.55*


0.57*

-

0.56*



0.45*
0.17**
-

0.44**
0.16**

0.43**
0.16**
-

0.43**
0.16**
-
-

0.49*
0.18**

0.45*
0.16**
-

0.43**
0.16**
                                      9-28

-------
Table 9.3.5.   Environmental and Food Samples: Estimated Ratios of Geometric Mean
                Pollutant Levels Between Urban and Rural, Low-Income and Middle/High-
                Income, and Home and Day Care Environments, When These Ratios Were
                Significantly Different from One at the 0.05 LeveP (cont.)
Pollutant/Metabolite
Dibenz [a, AJanthracene
Indenofl ,2,3-cd]pyrene
Sample
Medium1"
Dust (ng/g)
Dust (ng/m2)
Indoor air
Soil
Dust (ng/g)
Dust (ng/m2)
Estimated Ratio of Geometric Means
(When Significantly Different from 1 at the 0.05 Level)
North Carolina
Urban vs.
Rural






Low- vs.
Mid/High-
Income
0.57**

1.90**
2.61**
0.59**

Home vs.
Day Care
0.52*
0.12**



0.12**
Ohio
Urban vs.
Rural
3.66**
2.94*
-

3.43**
2.75*
Low- vs.
Mid/High-
Income
0.58*

-

0.56*

Home vs.
Day Care
0.42**
0.15**
-

0.41**
0.15**
Phthalates
Benzylbutylphthalate
Di-w-butylphthalate
Dust (ng/g)
Dust (ng/m2)
Indoor air
Dust (ng/g)
Dust (ng/m2)





1.76**
4.75**


2.56**
0.48**
0.10**
0.56**
0.50**
0.10**






2.52**


1.76*
0.41**
0.14**
0.56**
0.38**
0.14**
Phenols
Bisphenol-A
Pentachlorophenol
Dust (ng/m2)
Indoor air
Outdoor air
Dust (ng/m2)
--



--
1.77*
0.69*
2.56*
--


0.24*








0.33**
2.16*


PCBs
PCB52 |Dust(ng/m2) ||
-
" H

0.24**
* Dashed cells indicate that no analysis was performed due to the data being less than 50% detected. Blank cells indicate that a ratio was
estimated but was not significantly different from one at the 0.05 level. Note that pollutants, or sample media for a given pollutant, have been
excluded from this table if all cells within the rows corresponding to these pollutants or media would have been blank or dashed within this table.
All estimated ratios for each sample medium and each pollutant, along with corresponding 95% confidence intervals on these ratios, are presented
in Table K-l (NC) and Table K-2 (OH) of Appendix K.
b "Dust" = Indoor floor dust collected via HVS3 vacuum.  "C-solid food" = Children's solid food.

* Significantly different from 1 at the 0.05 level, but not at the 0.01 level.
** Significantly different from 1 at the 0.01 level.
                                                   9-29

-------
environments than in middle/high-income environments.  The 95% confidence interval of (1.03,
4.41) indicates that we can conclude with 95% confidence that the actual ratio falls within this
interval.  The single asterisk indicates that the estimated ratio (2.13) was significantly different
from one (and, equivalently, that the difference of 0.76 between the least squares means of the
log-transformed measurements was significantly different from zero) at the 0.05 level, but not at
the 0.01 level (p=0.041).  For a^/za-chlordane in NC outdoor air samples, the estimated ratio of
home versus day care environments was 0.44, implying that the geometric mean concentration at
home environments was 44% of the corresponding geometric mean for day care centers.  This
ratio was significantly different from one at the 0.01 level (p=0.009).

       For dermal wipe loadings, ratios and confidence intervals are presented by pollutant for
children and adults in Appendix K (Table K-5 for NC and Table K-6 for OH). Appendix K also
contains tables of p-values associated with t-tests applied to the log-transformed dermal wipe
loadings (Table K-7 for NC and Table K-8 for OH).  Those ratios found to be significantly
different from one at the 0.05 level are listed in Table 9.3.6 for both states.  All  of these tables
are constructed, and their contents are interpreted, in the same manner as in Tables K-l through
K-4 of Appendix K  and Table 9.3.5.

9.3.2.1 Comparing Pollutant Concentrations inNC Multimedia Samples Among Strata

       Significant differences between urban and rural sampling locations were observed rather
infrequently in the NC data.  Significant differences occurred at the 0.01 level only in two
instances: for concentrations of 2,4-D in indoor floor dust (ng/g), and for loadings of
bisphenol-A in adult dermal wipes.  On  average, concentrations of 2,4-D in floor dust (ng/g)
were about 3.2 times higher in urban locations than in rural locations. Bisphenol-A levels in
adult dermal wipe samples were about 2.6 times higher when taken in urban locations.

       Within Table 9.3.5 and  9.3.6, across all pollutants and sample media for NC, significant
differences in pollutant levels were most frequently observed between low-income and
middle/high-income locations.  In fact, whenever a pollutant had at least 50% detected data for
NC in at least one sample medium, therefore allowing that data to be analyzed statistically,
significant differences were observed at the 0.05 level between low-income and middle/high-
income strata for that pollutant in at least one sample medium.  Incidences of significant
differences at the  0.01 level between low-income and middle/high-income strata were as follows,
according to pollutant class:

       For the two OP pesticides, chlorpyrifos and diazinon, along with the metabolite
       3,5,6-TCP, significant differences were observed at the 0.01 level in floor dust loadings
       (ng/m2), with loadings in low-income households  ranging from 2.9 times (chlorpyrifos)
       to 6.3 times (diazinon) higher on average than middle/high-income households. Levels
       of 3,5,6-TCP in children's solid food samples collected in low-income households were
       about 48% of the levels in samples collected in middle/high-income areas; this difference
       was significant at the 0.01 level.  Diazinon levels in indoor
                                           9-30

-------
Table 9.3.6.   Dermal Wipe Samples:  Estimated Ratios of Geometric Mean Pollutant
               Levels Between Urban and Rural, Low-Income and Middle/High-Income,
               and Home and Day Care Environments, When These Ratios Were
               Significantly Different from One at the 0.05 LeveP
Pollutant/Metabolite
Type of
Dermal Wipe
Sample
Estimated Ratio of Geometric Means
(When Significantly Different from 1 at the 0.05 Level)
North Carolina
Urban vs.
Rural
Low- vs.
Mid/High-
Income
Home vs.
Day Care
Ohio
Urban vs.
Rural
Low- vs.
Mid/High-
Income
Home vs.
Day Care
OP Pesticides and Metabolites
Chlorpyrifos
3,5,6-TCP
Child
Adult
Child
Adult





1.91*

1.47*
1.75*
--
1.88**
--




2.53**
4.08**



--

--
PAHs
Chrysene
Adult ||
--
- || 1.81*

--
Phthalates
Benzylbutylphthalate
Child ||
1.64*
II "
--
--
Phenols
Bisphenol-A
Child 1
Adult | 2.61**


0.33** ||
1


2.90**
--
a Dashed cells indicate that the study data or design did not permit the given ratio to be estimated for the specified type of dermal wipe sample, or
that no analysis was performed due to the data being less than 50% detected. Blank cells indicate that a ratio was estimated but was not
significantly different from one at the 0.05 level. Note that pollutants, or sample types for a given pollutant, have been excluded from this table if
all cells within the rows corresponding to these pollutants or sample types would have been blank or dashed within this table. All estimated ratios
for each sample type and each pollutant, along with corresponding 95% confidence intervals on these ratios, are presented in Table K-5 (NC) and
Table K-6 (OH) of Appendix K.

* Significantly different from 1 at the 0.05 level, but not at the 0.01 level.
** Significantly different from 1 at the 0.01  level.
        air were about 3.6 times higher in low-income areas compared to middle/high-income
        areas; this difference was significant at the 0.01 level.

        Concentrations of cis- and /ram'-permethrin in indoor air were about 4 times higher in
        low-income locations compared to middle/high-income locations, with the difference
        being significant at the 0.01 level. For both pollutants, low-income locations had higher
        loadings in floor dust compared to middle/high-income locations, with loadings being
        about 220% higher for c/'s-permethrin (which was significant at the 0.01 level).

        Concentrations of 2,4-D in floor dust (ng/g) were about 4.5 times higher in middle/high-
        income locations compared to low-income locations; this difference was significant at the
        0.01 level.
                                               9-31

-------
•      Among the PAHs, concentrations in indoor floor dust were higher for middle/high-
       income locations, while concentrations in yard soil and indoor air were higher for low-
       income locations. For all nine target PAHs, indoor floor dust from middle/high-income
       locations had concentrations (ng/g) that were from 67% to 85% higher than low-income
       locations, with the difference being significant at the 0.01 level for all but benzo[e]pyrene
       and chrysene. For all PAHs except dibenz[a,/z]anthracene, yard soil from low-income
       locations had concentrations that were from 121% to 161% higher than middle/high-
       income locations, with the difference being significant at the 0.01 level for
       benz[a]anthracene, benzo[g/7/']perylene, benzo[e]pyrene, chrysene, and indeno[l,2,3-
       cd]pyrene. For five PAHs (benzo[&]flouranthene, benzo[g/2/']perylene, benzo[a]pyrene,
       chrysene, and indeno[l,2,3-cd]pyrene), indoor air concentrations ranged from 76% to
       94% higher in low-income areas than in middle/high-income areas, with the difference
       being significant at the 0.01 level.

       For di-w-butylphthalate and benzylbutylphthalate, loadings in indoor floor dust (ng/m2)
       were 2.6 and 4.8 times as high, respectively, in low-income locations than in
       middle/high-income locations, with the difference being significant at the 0.01 level.  In
       addition, benzylbutylphalate concentration in indoor floor dust (ng/g) averaged nearly
       80% higher in low-income locations, with the difference also being significant at the 0.01
       level.

       Across pollutants and sample media, frequent incidences of significant  differences in the
NC data also occurred between home and day care environments. Home environments often had
lower pollutant levels on average compared to day care environments, with 3,5,6-TCP being the
primary exception. Incidences of significant differences at the 0.01 level were as follows:

•      Among the OC pesticides and metabolite, only two instances of significant difference
       between home and day care environments at the 0.01 level were observed: for diazinon
       in floor dust (ng/m2), where home environments averaged only 10% of the loading found
       in day care environments, and for 3,5,6-TCP in children's dermal wipes, where samples
       taken in home environments averaged 88% higher than in day care environments.

•      For both alpha-  and gamma-chlordane, differences in loadings found in indoor floor dust
       (ng/m2) were significant between home and day care environments at the 0.01 level, with
       home environments averaging only 9% of the loadings in day care environments. For
       indoor floor dust concentration (ng/g) and outdoor air concentration, home environments
       averaged about 44% of the levels of alpha- and gamma-chlordane compared to day care
       environments, with the difference being significant at the 0.01 level for a^/za-chlordane
       in outdoor air samples.

•      For both cis- and trans-permethnn, significant differences were observed at the 0.01 level
       between home and day care environments for loadings in indoor floor dust (ng/m2), with
       home environments having slightly less than 20% of the loadings observed in day care
       environments, on average.

                                          9-32

-------
•      For each of the nine PAHs, loadings (ng/m2) in indoor floor dust differed significantly at
       the 0.01 level between home and day care environments, with home environments having
       approximately 12% of the loadings observed in day care environments, on average.

       For benzylbutylphthalate and di-w-butylphthalate, levels in indoor floor dust samples
       taken from home environments averaged approximately 10% of the levels for day care
       environments when expressed as a loading (ng/m2) and approximately 50% of the levels
       for day care environments when expressed as a concentration (ng/g). In each case, the
       difference was significant at the 0.01 level.  In addition, concentrations of di-n-
       butylphthalate in indoor air were significantly different at the 0.01 level, with home
       environments averaging about 56% of the levels observed in day care environments.

       Among the two phenols, significant differences occurred between home and day care
       environments at the 0.01 level only for bisphenol-A in children's dermal wipe samples,
       where samples taken from day care environments had loadings that were approximately
       three times higher than for samples taken from home environments.

9.3.2.2 Comparing Pollutant Concentrations in OH Multimedia Samples Among Strata

       Incidences of significant differences in sample media concentrations between urban and
rural locations occurred more frequently for OH data compared to NC data, with the following
differences being significant at the 0.01 level:

•      Among the OP pesticides and metabolites, significant differences in outdoor air
       concentrations between urban and rural locations were observed at the 0.01 level for
       diazinon and IMP, with urban locations averaging 2.7 and 3.9 times the concentrations,
       respectively, of rural locations. In addition, for 3,5,6-TCP, significant differences in soil
       concentrations were observed at the 0.01 level, with urban locations averaging 2.8 times
       the concentrations of rural locations.

•      Among all nine PAHs, significant differences were observed between urban and rural
       locations for indoor floor dust levels. When expressed as a concentration (ng/g),
       significance was at the 0.01 level, and urban locations averaged from 3.3 to 4.0 times
       higher loadings compared to rural locations. When expressed as a loading (ng/m2),
       significance was at the 0.01 level for three PAHs (benz[a]anthracene,
       benzo[6]fluoranthene, and chrysene), where urban locations averaged from 2.9  to 3.2
       times higher concentrations compared to rural locations.

       While frequent occurrences of significant differences were observed in the OH  data
between low-income and middle/high-income strata, their occurrence was somewhat less
frequent for OH than for NC.  Incidences of significant differences at the 0.01 level were as
follows, according to pollutant class:
                                          9-3

-------
•      The most frequent occurrences of significant differences among income strata occurred
       with the OP pesticides and metabolites. Significant differences at the 0.01 level occurred
       for chlorpyrifos in dermal wipe samples for both children and adults, with low-income
       locations having 2.5 and 4.1 times the levels of middle/high-income locations,
       respectively. Significant differences at the 0.01 level also occurred for chlorpyrifos in
       children's solid food samples, where low-income locations had roughly twice the levels
       of middle/high-income locations, and for IMP in outdoor air samples, where middle/high-
       income locations had roughly twice the levels of low-income locations. For chlorpyrifos,
       diazinon, and 3,5,6-TCP, loadings in indoor floor dust (ng/m2) averaged from 2.2 to 3.4
       times higher in low-income locations than in middle/high-income locations, with the
       difference significant at the 0.01 level for chlorpyrifos.

•      Concentrations of 2,4-D in indoor floor dust (ng/g) differed significantly at the 0.01 level
       between low-income and middle/high-income locations, with middle/high-income
       locations having about four times higher concentrations on average compared to low-
       income locations.

•      Loadings of benzylbutylphthalate in indoor floor dust (ng/m2) differed significantly at the
       0.01 level, with loadings in low-income locations being 2.5 times higher than for
       middle/high-income locations.

       The following occurrences of significant differences in OH data between home and day
care environments were observed at the 0.01 level:

•      For all OP pesticides and metabolites except IMP, significant differences in loadings
       were observed at the 0.01 level between home and day care environments for indoor floor
       dust (ng/m2), with home environments  having from 14% to 29% of the loadings observed
       in day care environments, on average.

       For all three pyrethroid pesticides, significant differences in loadings were observed at
       the 0.01 level between home and day care environments for indoor floor dust (ng/m2),
       with day care environments having about five times higher loadings compared to home
       environments.

•      Among the PAHs, significant differences were observed between home and day care
       environments for indoor floor dust levels. When expressed as a loading (ng/m2),
       significance was at the 0.01 level for all nine PAHs, where home environments averaged
       from 15% to 18% of the loadings associated with day care environments.  When
       expressed as a concentration (ng/g), significance was at the 0.01 level all but three PAHs
       (benz[a]anthracene, benzo[a]pyrene, and benzo[e]pyrene), where home environments
       averaged from 41% to 45% of the concentrations associated with day care environments.

•      Similar to the PAHs, significant differences were present at the 0.01 level for both
       phthalates in indoor floor dust samples, regardless of whether the levels were expressed

                                          9-34

-------
       as a concentration or a loading. When expressed as a loading (ng/m2), home
       environments averaged 14% of the loadings associated with day care environments,
       while when expressed as a concentration (ng/g), home environments averaged about 40%
       of the concentrations associated with day care environments. In addition, indoor air
       concentrations of di-w-butylphthalate differed significantly at the 0.01 level between
       home and day care environments, with day care environments having roughly twice the
       concentration on average compared to home environments.

•      For bisphenol-A, significant differences were observed at the 0.01 level between home
       and day care environments for loadings in floor dust samples (ng/m2), with day care
       environments averaging roughly three times higher loadings compared to home
       environments, and for children's dermal wipe samples, where samples taken in home
       environments had about 2.9 times higher levels compared to day care environments.

       Significant differences were observed at the 0.01 level in floor dust loading (ng/m2) of
       PCB 52, with day care environments having roughly four times the loadings, on average,
       compared to home environments.

9.4    Goal 2: To Quantify the Distributions of Child Characteristics, Activities, and
       Location that are Important for Exposure.

       Important factors for helping to determine the estimated potential exposures and potential
absorbed doses of the children and their primary caregivers to pollutants in these environments
included their physical characteristics, activity patterns, locations where they spend their time,
and the amount of food they consume. Table 9.4.1 contains summary statistics of the physical
characteristics  of the children and their primary caregivers including age, gender, body weight,
height, and hand surface area in both states. Table 9.4.2 provides the common activities of the
preschool children that were recorded by the parents in the questionnaires.  These included such
activities as frequency of placing toys and  other objects in the mouth, pacifier use, teething, and
frequency of washing hands.  Table 9.4.3 and Table 9.4.4 contain the daily percentage of time
that the participating children and adults, respectively, spent indoors or outdoors at their homes,
day care centers, or other places. The children spent a daily average of 94% and 90% of their
time indoors in NC and OH, respectively, while adults spent a daily average of 73% and 69% of
their time indoors at their home in NC and OH, respectively. Table 9.4.5 contains summary
statistics for the amount of solid food  (g) and liquid food (mL) samples that were collected over
the 48-h sampling period from children and their primary caregivers by group (stay at home or
attended day care). Many of these factors were used to determine the children's estimated
potential exposures and potential absorbed doses to pollutants at homes and day care centers.
                                          9-35

-------
Table 9.4.1   Summary of Selected Physical and Demographic Characteristics of the
             Participating Children and Their Primary Caregivers, for NC and OH
Physical Characteristics
# Participants
# Participants, by Gender
Male
Female
Age of participants (yr)b
Mean
SEC
Median
Minimum
Maximum
Height of participants (cm)
Mean
SE
Median
Minimum
Maximum
Weight of participants (kg)
Mean
SE
Median
Minimum
Maximum
Hand surface aread of participants (cm2)
Mean
SE
Median
Minimum
Maximum
Highest education level
1 1th grade or less
High school (HS) graduate/GED
Post-HS training
Some college
College graduate
Post-graduate
Unknown (missing)
Children
NC
129a
58
71
3.9/46.8
0.9/0.9
3.9/47.2
1.7/20.0
5.5/65.5
103.0
8.8
104.1
78.7
124.5
17.2
4.3
16.7
10.4
44.1
261.5
42.1
255.0
175.0
380.0

OH
127
63
64
3.9/47.1
0.8/0.9
4.0/47.9
1.7/20.3
5.6/66.6
102.1
9.0
101.6
78.7
121.9
17.7
4.0
17.1
10.8
33.3
269.2
44.6
260.0
190.0
405.0

Adults
NC
129a
8
121
31.3
6.8
31.0
19.0
46.0
165.9
7.9
165.1
144.8
190.5
76.1
19.4
72.5
45.0
151.7
571.2
70.0
560.0
460.0
825.0
12.3%
20.8%
5.4%
23.1%
23.1%
14.6%
0.8%
OH
127
12
115
32.2
6.5
32.0
19.0
49.0
166.4
8.3
165.1
152.4
203.2
75.2
19.4
72.0
45.0
140.0
561.5
73.7
550.0
410.0
840.0
6.3%
22.1%
5.5%
20.5%
34.6%
11.0%
0.0%
                                        9-36

-------
Table 9.4.1    Summary of Selected Physical and Demographic Characteristics of the
               Participating Children and Their Primary Caregivers, for NC and OH
               (cont.)
Physical Characteristics
Racial background
White
Black
Hispanic
Asian/Pacific Islander
Other
Unknown (missing)
Total household income
Less than $15,000
$15,001 to $25,000
$25,001 to $35,000
$35,001 to $50,000
More than $50,000
Refused
Don't know
Unknown (missing)
Children
NC
55.4%
36.9%
3.9%
0.0%
3.1%
0.8%




OH
70.1%
25.2%
2.4%
2.4%
0.0%
0.0%




Adults
NC
57.7%
36.9%
2.3%
0.0%
2.3%
0.8%

20.0%
17.7%
6.9%
16.1%
35.4%
3.1%
0.8%
0.0%
OH
73.2%
22.8%
2.4%
1.6%
0.0%
0.0%

9.5%
16.5%
7.9%
24.4%
30.7%
5.5%
2.4%
3.2%
a One adult and their child dropped out of the study before field sampling was completed.
b For children, age is given in total years, followed by total months.
c Standard error of the mean
d Hand surface are of both hands.
                                              9-37

-------
Table 9.4.2   Prevalence of Selected Daily Activities Among the Participating Children, as
             Recorded on Study Questionnaires

Daily Activities During
How often did your child play with
Most of the time
Sometimes
Almost never
Have you ever seen your child eat..
Dirt
Sand
Snow
Did your child use a pacifier?
Yes
No
Did your child ever put their mouth
Yes
No
Don't know
Is your child currently teething?
Yes
No
Don't know

the Previous Month
sand or dirt?


..?





on the floor or lick the floor?





How often did your child put toys in their mouth?
Frequently
Sometimes
Almost never

Did your child put anything3 other than toys or food in their
mouth?
Yes
No
Missing data



Did your child suck or chew their thumb or fingers?
Yes
No

Did your child suck or chew their toe or foot?
Yes
No

When your child was outside the house, how often did he/she walk
barefoot?
Most of the time
Sometimes
Almost never



NC Children
(n=129)
34%
40%
26%

12%
9%
29%
5%
95%
10%
89%
1%
5%
94%
1%
25%
33%
42%
33%
67%
-

42%
58%
5%
95%

8%
21%
71%
OH Children
(n=127)
29%
36%
35%

8%
5%
5%
4%
96%
8%
92%
-
2%
98%
-
18%
31%
51%
25%
74%
1%

15%
85%
1%
99%

22%
24%
54%
                                         9-38

-------
Table 9.4.2   Prevalence of Selected Daily Activities Among the Participating Children, as
              Recorded on Study Questionnaires (cont.)

Daily Activities During the Previous Month
How often did your child take something to eat or drink when
he/she were playing outside the house?
Most of the time
Sometimes
Almost never
When your child was inside the house, how often did he/she walk
barefoot
Most of the time
Sometimes
Almost never
When your child was inside the house, how often did he/she sit or
play on the floor?
Most of the time
Sometimes
Almost never
How often did your child sleep or take a nap on the floor?
Most of the time
Sometimes
Almost never
How often were your child's hand's washed before eating meals?
Most of the time
Sometimes
Almost never
How often were your child's hands washed before eating snacks?
Most of the time
Sometimes
Almost never
Don't know
How often were your child's hands washed after playing outside
the house?
Most of the time
Sometimes
Almost never
How often were their hands washed before going to bed?
Most of the time
Sometimes
Almost never
NC Children
(n=129)


15%
35%
50%


75%
16%
8%


78%
21%
1%

5%
12%
83%

77%
20%
3%

35%
43%
22%
-


67%
24%
9%

83%
8%
9%
OH Children
(n=127)


17%
39%
44%


74%
18%
8%


74%
23%
3%

3%
13%
84%

83%
16%
1%

39%
35%
25%
1%


60%
32%
8%

74%
17%
9%
1 "Anything" refers to objects other than toys or food that could be placed into the mouth.
                                            9-39

-------
Table 9.4.3   Daily Percentage of Time that Participating Children Spent Indoors or
             Outdoors at Homes, Day Care Centers, Or Other Places
Location
#
Children
Percentage of Time Spent at the Given Location
Mean
SD
Median
Minimum
Maximum
North Carolina
Indoors
at Home
at Day Care
Other location
Outdoors
at Home
at Day Care
129
129
63
129
129
129
63
94
72
27
9
6
4
3
4
15
6
7
4
4
2
95
71
26
8
5
3.1
3.0
81
48
14
0
0
0
0
100
100
41
36
19
19
10
Ohio
Indoors
at Home
at Day Care
Other location
Outdoors
at Home
at Day Care
127
127
58
127
127
127
58
90
68
30
8
10
8
5
8
16
12
7
8
8
5
92
68
30
6
8
5
4
58
8
8
0
0
0
0
100
99
89
47
42
42
17
Table 9.4.4    Daily Percentage of Time that Participating Adults Spent Indoors or Outdoors at
             Homes or Other Places
Location
Percentage of Time Spent at the Given Location
Mean
SD
Median
Minimum
Maximum
North Carolina (N=129 adults)
Indoors at Home
Outdoors at Home
Away from Home
73
3
24
15
4
15
72
2
25
48
0
0
100
21
48
Ohio (N=127 adults)
Indoors at Home
Outdoors at Home
Away from Home
69
6
24
17
8
19
69
3
19
8
0
0
100
54
91
                                        9-40

-------
Table 9.4.5   Summary Statistics on the Daily Amount of Solid and Liquid Food Collected
              from Participating Children and Their Primary Caregivers in the Stay-at-
              Home and Day Care Groups"
Food Sample Type
State
N
Mean
SD
Median
Min
Max
Weight of Solid Food (g)
Stay-at-home group
Adults
Stay-at- home group
Children
Day care group
Adults
Day care group
Children
NC
OH
NC
OH
NC
OH
NC
OH
66
69
66
69
63
58
63
58
498.6
577.7
355.4
364.9
342.7
310.4
504.9
432.0
206.6
208.7
151.0
104.1
193.7
149.1
143.6
138.8
509.0
571.6
328.7
353.0
323.4
274.4
511.9
417.1
20.6
221.6
74.7
141.5
6.2
102.5
207.7
188.1
925.9
1102.8
891.3
623.9
1378.5
792.0
773.3
806.0
Volume of Liquid Food (mL)
Stay-at-home group
Adults
Stay-at-home group
Children
Day care group
Adults
Day care group
Children
NC
OH
NC
OH
NC
OH
NC
OH
64
67
65
69
57
55
62
57
723.9
748.6
597.3
559.4
565.4
456.1
777.5
600.8
430.9
392.6
246.6
230.6
320.2
329.3
277.9
226.8
692.5
700.0
600.0
545.0
548.0
370.0
780.0
600.0
69.0
124.0
83.0
144.0
80.0
110.0
237.0
200.0
2326.0
1802.5
1550.0
1655.0
1380.0
1387.5
1351.0
1140.0
1 Solid and liquid food samples were composited separately over a 48-h period.
9.5    Goal 3: To Estimate the Exposures of Participating Preschool Children to CTEPP
       Pollutants that They May Encounter in Their Everyday Environments

       The formulas used to estimate potential exposure level and potential absorbed dose for a
given study participant via the inhalation, dietary ingestion, and indirect ingestion routes were
given in Sections  8.4.1, 8.4.2, and 8.4.3, respectively. For the eight target pollutants specified at
the end of Section 9.2, potential exposure level and potential absorbed dose were estimated for
each exposure route in all study participants.  For the remaining target pollutants specified in
Table 8.3 of Section 8.4 (19 pollutants in NC and 18 pollutants in OH), potential exposure level
and potential absorbed dose via a given exposure route were estimated for study participants
within a given state only when the following criteria were  satisfied:

       Inhalation route: When at least 45% of the state's samples have detected results (i.e., at or
       above the MDL) for indoor air and/or outdoor air
                                           9-41

-------
•      Dietary ingestion route: When at least 45% of the state's samples have detected results
       (i.e., at or above the MDL) for solid food.
•      Indirect ingestion route: When at least 45% of the state's samples have detected results
       (i.e., at or above the MDL) for floor dust.

For target pollutants achieving these criteria within a given exposure route, potential exposure
level and potential absorbed dose results are presented in this section.

9.5.1   Sub-goal 3.1: To Quantify the Distribution of Potential Exposure and Potential
       Absorbed Dose by Exposure Route

       Descriptive statistics of potential exposure level and potential absorbed dose estimates
are presented by exposure route in Appendix L for NC children, Appendix M for OH children,
Appendix N for NC adults, and Appendix O for OH adults. The descriptive statistics are
calculated across all study participants, as well as for study participants within each stratum:
urban, rural, low-income, middle/high-income, stay-at-home children (or adults with stay-at-
home children), and day care children (or  adults with day care children). The descriptive
statistics in these tables are presented and  interpreted in the same way as was discussed in
Section 9.3.1, except the sample size (N) now corresponds to numbers of study participants.

       For the target pollutants, overall median values of estimated potential exposure level and
potential absorbed dose are summarized by exposure route in Table 9.5.1 for NC children, Table
9.5.2 for OH children, Table 9.5.3 for NC  adults,  and Table 9.5.4 for OH adults.  For the eight
pollutants for which potential exposure level and  potential absorbed dose were calculated for
each exposure route, boxplots of the distribution of estimated potential exposure level and
potential absorbed dose are given in Figures 9.5.1 through 9.5.6, with each figure focused on
either children or adults and a specific exposure route:

•      Figure 9.5.1: inhalation route for children
       Figure 9.5.2: dietary ingestion route for children
•      Figure 9.5.3: indirect ingestion route for children
       Figure 9.5.4: inhalation route for adults
•      Figure 9.5.5: dietary ingestion route for adults (3,5,6-TCP and 2,4-D only)
•      Figure 9.5.6: indirect ingestion route for adults.

Each figure contains separate boxplots for potential exposure level and potential absorbed dose,
for each pollutant for which data were available to make these estimates, and for each state.   See
Section 9.3.1 for how to interpret these boxplots.
                                            9-42

-------
Table 9.5.1    Median Values of Estimated Potential Exposure and Potential Absorbed
               Dose for Target Pollutants in Participating NC Preschool Children, by
               Exposure Route
Pollutant/Metabolite
Potential Exposure Level (ng/day)
Inhalation
Dietary
Ingestion
Indirect
Ingestion
Potential Absorbed Dose (ng/kg/day)
Inhalation
Dietary
Ingestion
Indirect
Ingestion
OP Pesticide and Metabolite
Chlorpyrifos
Diazinon
3,5,6-TCP
47
17
14
81

-------
Table 9.5.2    Median Valuesa of Estimated Potential Exposure and Potential Absorbed
                Dose for Target Pollutants in Participating OH Preschool Children, by
                Exposure Route
Pollutant/Metabolite
Potential Exposure Level (ng/day)
Inhalation
Dietary
Ingestion
Indirect
Ingestion
Potential Absorbed Dose (ng/kg/day)
Inhalation
Dietary
Ingestion
Indirect
Ingestion
OP Pesticide and Metabolite
Chlorpyrifos
Diazinon
3,5,6-TCP
15
8.0
5.1
78

-------
Table 9.5.3    Median Valuesa of Estimated Potential Exposure and Potential Absorbed
                Dose for Target Pollutants in Participating NC Adults, by Exposure Route
Pollutant/Metabolite
Potential Exposure Level (ng/day)
Inhalation
Dietary
Ingestion
Indirect
Ingestion
Potential Absorbed Dose (ng/kg/day)
Inhalation
Dietary
Ingestion
Indirect
Ingestion
OP Pesticides and Metabolites
Chlorpyrifos
Diazinon
3,5,6-TCP
69
23
21
b
-
1,200
3.2
0.43
2.3
0.45
0.14
0.14
-
-
7.9
0.021
0.0030
0.016
OC Pesticides
alpha-Chlordane
gamma-Chlordane
p,p'-DDE
Heptachlor
9.5
17

-------
Table 9.5.4    Median Valuesa of Estimated Potential Exposure and Potential Absorbed
                Dose for Target Pollutants in Participating OH Adults, by Exposure Route
Pollutant/Metabolite
Potential Exposure Level (ng/day)
Inhalation
Dietary
Ingestion
Indirect
Ingestion
Potential Absorbed Dose (ng/kg/day)
Inhalation
Dietary
Ingestion
Indirect
Ingestion
OP Pesticides and Metabolites
Chlorpyrifos
Diazinon
3,5,6-TCP
20
11
7.0
b
-
980
1.2
0.48
0.99
0.13
0.076
0.046
-
-
6.1
0.0079
0.0031
0.0068
OC Pesticides
alpha-Chlordane
gamma-Chlordane
p,p'-DDE
3.0
4.1

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                                             9-47

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9-48

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                                             9-50

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                                                           9-51

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9-52

-------
       The shapes of the distributions of potential exposure and potential absorbed dose
estimates that are portrayed in Figures 9.5.1 through 9.5.6 closely resemble those for the
environmental and personal media that are given in Section 9.3.1.  Di-w-butylphthalate estimates
tend to be higher than estimates for the other pollutants, especially for inhalation. In addition,
estimates tend to be higher across the board for NC than for OH under each exposure route.

9.5.2  Sub-goal 3.2: To Quantify the Distribution of Potential Exposure and Potential Dose
       Aggregated over All Exposure Routes

       As discussed in Section 8.4, aggregate potential exposure and aggregate potential
absorbed dose associated with a study participant were defined as the sums of the potential
exposure and potential absorbed dose estimates, respectively, across all three exposure routes
considered in this study (inhalation, dietary ingestion,  and indirect ingestion).  These aggregate
estimates were calculated only for the eight target pollutants mentioned at the end of Section 9.2,
for which potential exposure and potential absorbed dose estimates were calculated for each of
the three exposure routes for each study participant.

       Descriptive statistics of the potential aggregate exposure level and potential aggregate
absorbed dose estimates are presented in Appendix L for NC children, Appendix M for OH
children, Appendix N for NC adults, and Appendix O for OH adults.  They are presented only in
those tables that are associated with the eight target pollutants.  (Note that these tables also
contain route-specific data summaries.) Within these tables and in Table 9.5.5 and Table 9.5.6
forNC and OH, respectively, these descriptive statistics are presented across all study
participants, separately for children and adults. In addition, within the appendix tables,
descriptive statistics  are presented for each stratum: urban, rural, low-income, middle/high-
income, stay-at-home children (or adults with stay-at-home children), and day care children (or
adults with day care  children).

       Boxplots of potential aggregate exposure level  and  potential aggregate absorbed dose
estimates are given in Figure 9.5.7 for participating children and in Figure 9.5.8 for their adult
caregivers. Each figure contains separate boxplots for potential aggregate exposure level and
potential aggregate absorbed dose, for each pollutant for which data were available to make
these estimates, and for each state. The boxplots show that aggregate potential exposure and
dose estimates in the participating children were highest for di-w-butylphthalate and bisphenol-
A, and to a lesser extent, 3,5,6-TCP. See Section 9.3.1  for how to interpret these boxplots.

9.5.3  Sub-goal 3.3: To Quantify the Distribution of Urinary Biomarkers Concentrations as
       an Indicator of Absorbed Dose

       Concentrations of selected acid pollutants and metabolites in urine collected over the 48-
h sampling period were used as biomarkers of exposure in  study participants. These
concentrations were  summarized and analyzed 1) after adjusting for the urine sample's specific
gravity, 2) after adjusting for the urine sample's creatinine  level, and 3) without any adjustment.
                                           9-53

-------
Table 9.5.5    Summary of Aggregate Potential Exposure and Aggregate Potential
                 Absorbed Dose Estimates for Eight Pollutants in NC Study Participants"
Pollutant/
Metabolite
Type of Measure
N
%
Detected
Arith.
Mean
S.D.
Geom.
Mean
Percentiles
25th
50th
75"
95*
Max.
OP Pesticides and Metabolite
Chlorpyrifos
Diazinon
3,5,6-TCP
Children — Aggregate Exposure"
Children — Aggregate Doseb
Adults — Aggregate Exposure
Adults — Aggregate Dose
Children — Aggregate Exposure
Children — Aggregate Dose
Adults — Aggregate Exposure
Adults — Aggregate Dose
Children — Aggregate Exposure
Children — Aggregate Dose
Adults — Aggregate Exposure
Adults — Aggregate Dose
109
109
--c
--
109
109
--
--
113
113
117
117
100
100
--
--
100
100
--
--
100
100
100
100
359
10.6
-
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354
10.2
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--
1,480
43.8
1,660
11.6
801
23.8
--
--
1,720
49.4
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--
1,010
30.9
2,130
15.5
174
5.18
--
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68.1
2.02
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1,110
33.3
1,010
6.81
78.9
2.49
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--
30.4
0.965
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--
804
22.6
596
3.95
152
4.59
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51.6
1.44
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--
1,230
37.7
1,310
8.37
295
8.84
--
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110
2.60
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1,960
57.8
1,770
12.6
1,180
31.7
--
--
544
15.8
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3,780
100
4,390
33.1
7,630
227
--
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15,100
428
--
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5,600
199
14,400
113
Pyrethroid Pesticides
cis-
Permethrin
trans-
Permethrin
Children — Aggregate Exposure
Children — Aggregate Dose
Adults — Aggregate Exposure
Adults -- Aggregate Dose
Children — Aggregate Exposure
Children — Aggregate Dose
Adults — Aggregate Exposure
Adults -- Aggregate Dose
109
109
--
--
106
106
--
--
100
100
--
--
100
100
--
--
3,290
92.5
--
--
1,870
52.4
--
--
15,000
412
--
--
8,720
235
--
--
306
9.08
--
--
252
7.52
--
--
88.9
2.71
--
--
77.9
2.37
--
--
246
6.72
--
--
193
5.82
--
--
656
21.5
--
--
555
19.5
--
--
6,840
243
--
--
4,870
154
--
--
93,300
2,850
--
--
65,300
2,000
--
--
Acid Herbicides
2,4-D
Children — Aggregate Exposure
Children — Aggregate Dose
Adults — Aggregate Exposure
Adults — Aggregate Dose
105
105
110
110
96
96
96
96
279
8.33
318
2.11
302
9.35
441
2.90
188
5.56
183
1.24
96.4
2.95
92.9
0.557
193
4.93
164
1.12
343
9.75
338
2.28
836
22.5
1,310
6.86
2,250
70.8
2,840
16.8
Phthalates
Di-n-
butylphthalate
Children — Aggregate Exposure
Children — Aggregate Dose
Adults — Aggregate Exposure
Adults — Aggregate Dose
78
78
--
--
100
100
--
--
72,900
2,100
--
--
76,600
2,190
--
--
47,100
1,360
--
--
21,600
652
--
--
42,900
1,250
--
--
94,800
2,910
--
--
270,000
7,800
--
--
365,000
11,400
--
--
Phenols
Bisphenol-A
Children — Aggregate Exposure
Children — Aggregate Dose
Adults — Aggregate Exposure
Adults — Aggregate Dose
102
102
--
--
100
100
--
--
4,190
125
--
--
6,190
175
--
--
2,500
75.6
--
--
1,500
42.4
--
--
2,560
71.4
--
--
5,240
153
--
--
11,300
342
--
--
57,200
1,570
--
--
* Aggregate potential exposure level (ng/day)
b Aggregate potential absorbed dose (ng/kg/day)
0 Dashes indicate that insufficient data prevented aggregate potential exposure or aggregate potential absorbed dose from being estimated.
estimate is labeled "detected" if at least one of the sample media levels entering into its calculation is labeled "detected."
An
                                                   9-54

-------
Table 9.5.6    Summary of Aggregate Potential Exposure and Aggregate Potential
                 Absorbed Dose Estimates for Eight Pollutants in OH Study Participants'1
Pollutant/
Metabolite
Type of Measure
N
%
Detected
Arith.
Mean
S.D.
Geoni.
Mean
Percentiles
25th
50th
75"
95th
Max.
OP Pesticides and Metabolite
Chlorpyrifos
Diazinon
3,5,6-TCP
Children — Aggregate Exposure a
Children — Aggregate Dose °
Adults — Aggregate Exposure
Adults — Aggregate Dose
Children — Aggregate Exposure
Children — Aggregate Dose
Adults — Aggregate Exposure
Adults — Aggregate Dose
Children — Aggregate Exposure
Children — Aggregate Dose
Adults — Aggregate Exposure
Adults — Aggregate Dose
96
96
--c
--
112
112
--
--
103
103
108
108
100
100
--
--
100
100
--
--
100
100
100
100
178
5.39
--
--
142
4.62
--
--
1,180
34.1
2,010
14.5
234
8.25
--
--
534
21.3
--
--
1,110
32.9
3,210
23.4
117
3.37
--
--
54.1
1.56
--
--
852
24.4
1,050
7.22
77.7
2.04
--
--
29.9
0.872
--
--
488
15.2
554
3.27
109
3.10
--
--
38.6
1.13
--
--
930
25.4
1,000
6.39
172
5.11
--
--
67.0
1.89
--
--
1,500
42.3
2,170
16.5
491
17.1
--
--
378
11.0
--
--
2,610
80.3
7,080
47.1
1,520
61.8
--
--
5,430
221
--
--
8,700
228
27,300
200
Pyrethroid Pesticides
cis-
Permethrin
trans-
Permethrin
Children — Aggregate Exposure
Children — Aggregate Dose
Adults — Aggregate Exposure
Adults — Aggregate Dose
Children — Aggregate Exposure
Children — Aggregate Dose
Adults — Aggregate Exposure
Adults — Aggregate Dose
111
111
--
--
97
97
--
--
100
100
--
--
100
100
--
--
665
18.3
--
--
280
8.39
--
--
1,960
54.1
--
--
784
25.1
--
--
118
3.40
--
--
87.5
2.52
--
--
38.8
1.29
--
--
36.6
1.07
--
--
90.1
2.22
--
--
72.0
1.78
--
--
167
4.71
--
--
146
4.00
--
--
4,790
151
--
--
1,960
53.1
--
--
9,430
315
--
--
5,790
199
--
--
Acid Herbicides
2,4-D
Children — Aggregate Exposure
Children — Aggregate Dose
Adults — Aggregate Exposure
Adults — Aggregate Dose
95
95
106
106
99
99
99
99
350
10.1
278
1.97
736
23.5
393
2.96
175
5.05
166
1.12
81.0
2.35
92.5
0.589
141
4.13
147
0.978
245
7.48
269
1.83
2,070
39.1
1,140
8.37
6,090
210
2,540
19.3
Phthalates
Di-n-
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Children — Aggregate Exposure
Children — Aggregate Dose
Adults — Aggregate Exposure
Adults — Aggregate Dose
43
43
--
--
100
100
--
--
19,500
539
--
--
27,600
703
--
--
12,200
353
--
--
7,330
205
--
--
8,310
262
--
--
16,900
467
--
--
81,000
2,080
--
--
152,000
3,570
--
--
Phenols
Bisphenol-A
Children — Aggregate Exposure
Children — Aggregate Dose
Adults — Aggregate Exposure
Adults — Aggregate Dose
67
67
--
--
100
100
--
--
3,620
101
--
--
6,310
130
--
--
2,150
63.8
--
--
1,270
34.1
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1,880
60.8
--
--
3,540
93.9
--
--
12,800
328
--
--
48,600
775
--
--
* Aggregate potential exposure level (ng/day)
b Aggregate potential absorbed dose (ng/kg/day)
0 Dashes indicate that insufficient data prevented aggregate potential exposure or aggregate potential absorbed dose from being estimated. An
estimate is labeled "detected" if at least one of the sample media levels entering into its calculation is labeled "detected."
                                                    9-55

-------
          CPS      DZN      TCP
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          CPS      DZN      TCP
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                                                    DBF      BPA
                                             2,4-D     DBF
                                                                     "^  10
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cis-P     trans-P    B.4-D

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                                                                              CPS      DZN     TCP
cis-P     trans-P

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                                                                                                                         DBF      BPA
                                                                                                                 Z.4-Q     DBF
Figure 9.5.7   Boxplots of Estimated Aggregate Potential Exposure and Aggregate Potential Absorbed Dose for Participating
               NC and OH Children, for Eight Pollutants
                                                                9-56

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                    TCP                     2.4-D

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                                                                                           Analyte
Figure 9.5.8  Boxplots of Estimated Aggregate Potential Exposure and Aggregate Potential Absorbed Dose for Participating
             NC and OH Adults, for Eight Pollutants
                                                          9-57

-------
When multiple urine samples were taken for a given study participant during the study, the
geometric mean concentration was used in the summaries and analyses.

       Descriptive statistics of the urine biomarker concentrations are presented in Appendix P
for NC and Appendix Q for OH.  Each appendix contains separate sets of tables for children and
adults, and within each set, each pollutant and metabolite is represented by two tables for ease in
display. The descriptive statistics are presented across all study participants, as well as
separately for each stratum:  urban, rural, low-income, middle/high-income, stay-at-home
children (or adults with stay-at-home children), and day care children (or adults with day care
children).

       For both states, 3,5,6-TCP and 2,4-D were measured in urine samples of study
participants and were considered in estimating aggregate potential exposure level and aggregate
potential absorbed dose  estimates for study participants. For these two target pollutants, along
with pentachlorophenol, the descriptive statistics associated with unadjusted urine concentrations
are also presented in Table 9.5.7 and Table 9.5.8 for NC children and OH children, respectively.

       Boxplots of the unadjusted urine concentrations for 3,5,6-TCP and 2,4-D are presented in
Figure 9.5.9, with separate boxplots for children and adults, as well as by state. These boxplots
show that, in general, levels of 3,5,6-TCP covered a higher range than for 2,4-D, and for both,
similar distributions were observed between children and adults and between NC and OH.
While the  boxplots in Figure 9.5.9 resemble those for  aggregate potential exposure and absorbed
dose that are given in Figure 9.5.8, the urine concentrations have less of a difference between the
two states in the range covered by the distributions. See Section 9.3.1 for how to interpret the
boxplots.

9.5.4  Sub-goal 3.4:  To Determine on Average How These Exposure and Dose Metrics for
       Each Route and Aggregated over Routes Differ Between Children in Urban and Rural
       Settings,  Children in Low- and Middle/High-Income Families, Day Care and Stay-at-
       Home Children, Children and Adults in the Same Household Overall, and Children
       and Adults by Stratum

       To address this sub-goal, a statistical analysis was performed on the (log-transformed)
potential exposure level and potential absorbed dose estimates (by exposure route and
aggregated across routes1) and on urine biomarker concentrations to determine whether these
measures differ significantly 1) between children in urban and rural settings, 2) between children
in low- and middle/high-income families, and 3) between day care and stay-at-home children. In
each case, an analysis of variance using model (8-7) in Section 8.5.2.2 was performed to
calculate a least squares mean of the log-transformed measures for each stratum (i.e., urban,
rural, low-income, middle/high-income, stay-at-home child, day care child).  Then, in the
manner described in
       1  Analysis of aggregated exposures and absorbed dose estimates was performed only for the eight
pollutants mentioned at the end of Section 9.2.
                                           9-58

-------
 Table 9.5.7   Summary of Unadjusted Urinary Biomarker Concentrations (ng/mL) for
                 Three Pollutants and Metabolites Measured in the Urine of Participating NC
                 Children3
Strata
N
%
Detected
Arith.
Mean
Standard
Deviation
Geoni.
Mean
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
3,5,6-TCP
Overall
Urban
Rural
Low-Income
Mid/High-Income
Home Children
Day Care Children
128
107
21
59
65
65
63
98
98
100
98
99
97
100
7.28
7.28
7.28
6.55
8.02
8.12
6.42
10.3
10.9
6.93
7.36
12.7
13.7
4.76
5.22
5.18
5.46
4.90
5.48
5.15
5.31
3.70
3.68
3.95
3.40
3.81
3.68
3.74
5.26
5.22
5.29
5.08
5.22
5.16
5.29
8.18
8.28
6.51
5.86
10.1
8.27
7.82
15.5
13.3
19.9
19.9
14.7
15.5
12.0
104
104
30.9
49.1
104
104
30.9
2,4-D
Overall
Urban
Rural
Low-Income
Mid/High-Income
Home Children
Day Care Children
128
107
21
59
65
65
63
94
94
95
97
91
88
100
0.775
0.812
0.583
0.836
0.707
0.715
0.836
0.561
0.575
0.453
0.558
0.573
0.556
0.565
0.594
0.624
0.465
0.665
0.522
0.519
0.684
0.343
0.349
0.280
0.405
0.276
0.245
0.412
0.652
0.690
0.430
0.736
0.510
0.510
0.707
1.09
1.10
0.656
1.10
0.945
1.07
1.10
1.97
2.11
1.40
1.97
2.11
1.93
2.17
2.64
2.64
1.97
2.64
2.61
2.41
2.64
Pentachlorophenol
Overall
Urban
Rural
Low-Income
Mid/High-Income
Home Children
Day Care Children
128
107
21
59
65
65
63
89
89
91
95
85
80
98
0.605
0.639
0.433
0.659
0.571
0.641
0.567
0.629
0.672
0.280
0.625
0.649
0.734
0.500
0.433
0.447
0.369
0.498
0.388
0.419
0.448
0.262
0.258
0.290
0.296
0.220
0.246
0.281
0.394
0.400
0.328
0.460
0.335
0.370
0.402
0.654
0.694
0.500
0.773
0.564
0.658
0.646
1.92
2.43
0.901
1.92
2.43
2.70
1.38
3.45
3.45
1.33
3.45
3.08
3.45
2.84
a For a given study subject, multiple sample results have been log-transformed (after replacing not detected results by the MDL divided by the
square root of 2), averaged, and exponentiated back to regular units prior to summarizing the data within a stratum.  This result is labeled as
"detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of participants having data entering into
the summaries.
                                                    9-59

-------
Table 9.5.8    Summary of Unadjusted Urinary Biomarker Concentrations (ng/mL) for
                 Three Pollutants and Metabolites Measured in the Urine of Participating OH
                 Children3
Strata
N
%
Detected
Arith.
Mean
Standard
Deviation
Geoni.
Mean
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
3,5,6-TCP
Overall
Urban
Rural
Low-Income
Mid/High-Income
Home Children
Day Care Children
122
107
15
40
70
67
55
100
100
100
100
100
100
100
5.61
5.68
5.08
5.68
5.69
6.05
5.06
3.38
3.43
3.07
3.11
3.59
3.73
2.84
4.64
4.71
4.21
4.89
4.60
4.90
4.34
2.87
2.90
2.08
3.38
2.73
3.01
2.68
5.07
4.79
5.28
5.15
5.12
5.28
4.43
7.33
7.50
6.12
7.42
7.78
9.08
6.88
12.3
12.8
12.3
12.0
13.3
12.9
11.2
15.3
15.3
12.3
14.1
15.3
15.3
12.8
2,4-D
Overall
Urban
Rural
Low-Income
Mid/High-Income
Home Children
Day Care Children
126
109
17
40
73
69
57
98
98
100
100
97
97
100
1.32
1.32
1.30
1.36
1.37
1.50
1.10
1.59
1.68
0.904
1.14
1.90
1.84
1.21
0.927
0.902
1.11
1.03
0.908
1.03
0.816
0.566
0.560
0.857
0.589
0.550
0.710
0.525
1.02
0.994
1.15
1.12
1.02
1.16
0.809
1.35
1.34
1.36
1.60
1.33
1.44
1.17
3.59
3.59
4.35
3.97
7.04
4.35
3.21
12.5
12.5
4.35
5.63
12.5
12.5
7.55
Pentachlorophenol
Overall
Urban
Rural
Low-Income
Mid/High-Income
Home Children
Day Care Children
126
109
17
40
73
69
57
99
99
100
100
99
99
100
1.27
1.23
1.52
1.05
1.47
1.54
0.946
2.20
2.32
1.19
0.884
2.80
2.89
0.638
0.876
0.830
1.25
0.797
0.959
0.993
0.753
0.536
0.520
0.871
0.486
0.640
0.640
0.483
0.835
0.755
1.24
0.769
0.876
0.920
0.738
1.39
1.38
1.52
1.59
1.39
1.39
1.36
2.71
2.47
5.23
2.33
3.56
3.96
2.37
23.8
23.8
5.23
5.02
23.8
23.8
2.71
* For a given study subject, multiple sample results have been log-transformed (after replacing not detected results by the MDL divided by the
square root of 2), averaged, and exponentiated back to regular units prior to summarizing the data within a stratum.  This result is labeled as
"detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of participants having data entering into
the summaries.
                                                    9-60

-------
                              Analyte
                              Analyte

                                                                                              Analyte
                                                                                              Analyte
Figure 9.5.9   Boxplots of Urinary Biomarker Concentrations for Participating NC and OH Children and Adults, for Eight
              Pollutants
                                                            9-61

-------
Section 9.3.2, a ratio of least-squares geometric mean concentrations was calculated between the
above pairs of strata, along with an approximate 95% confidence interval on this ratio.

       For children's potential exposure level and potential absorbed dose estimates, ratios and
confidence intervals are presented by pollutant and exposure route in Appendix R (Table R-l for
NC and Table R-2 for OH).  These ratios are of the least-squares geometric mean for the first
stratum specified in the column heading versus the second specified stratum, and 95%
confidence intervals are shown in parentheses.  The t-test applied to the log-transformed data also
is a test of whether this ratio differs significantly from one; p-values associated with these tests
are also given in Appendix R, within the second, third, and fourth columns in Table R-3 (for NC)
and Table R-4 (for OH).

       Table 9.5.9 has condensed the information presented in Tables R-l and R-2 of Appendix
R by presenting only those ratios which were significantly different from one at the 0.05 level.
Thus, Table 9.5.9 contains one row for each combination of pollutant, parameter, and exposure
route having at least one of the three ratios significantly different from one at the 0.05 level in
either state.  When a ratio  is  not specified in this table and a dash does not appear in its place
(meaning that the criteria placed on the percentage of detected concentrations entering into
calculation of the exposure/dose estimate were met for performing statistical analysis), then the
ratio was not significantly  different from one at the 0.05 level.

       To illustrate how to interpret the numbers in Table 9.5.9 and Tables R-l and R-2,
analysis of 3,5,6-TCP data from OH suggest that potential exposure level via inhalation is about
70% higher in low-income children than in middle/high-income children (ratio=1.70), and
potential exposure level via indirect ingestion is about 81% higher in day care children than in
stay-at-home children (ratio=1.81). Both are significantly different from one at the 0.05 level
but not at the 0.01 level.

       For the urinary biomarker concentrations, ratios between the specified strata and 95%
confidence intervals on these ratios are presented by pollutant in Appendix R (Table R-5 for NC
and Table R-6 for OH). For a given state, these concentrations were statistically  analyzed, and
ratios were reported,  only  for those pollutants in which at least 50% of urine samples had
detected concentrations. P-values associated with t-tests applied to the log-transformed urinary
biomarker concentrations to  test whether these ratios differ significantly from one are also given
in Appendix R, within the  second, third, and fourth columns in Table R-7 (for NC) and Table
R-8 (for OH).  Among all  ratios reported in Table R-5 and R-6 of Appendix R, significant
differences from one were reported only for 2,4-D in OH, where the geometric mean for OH
stay-at-home children was about 65% of the geometric mean for OH day care children under
each form of the urinary concentration (i.e., unadjusted, creatinine-adjusted, specific gravity-
adjusted).
                                           9-62

-------
Table 9.5.9   Estimated Ratios Between Selected Strata of Geometric Mean Potential
             Exposure and Potential Absorbed Dose Estimates in Participating NC and
             OH Children, When These Ratios Were Significantly Different from One at
             the 0.05 Level3
Pollutant/
Metabolite
Exposure/Dose Parameter
and Pathway
Estimated Ratio of Geometric Means
(When Significantly Different from 1 at the 0.05 Level)
North Carolina
Urban
vs.
Rural
Low- vs.
Mid/High-
Income
Day Care
vs. Home
Ohio
Urban
vs.
Rural
Low- vs.
Mid/High-
Income
Day Care
vs. Home
OP Pesticides and Metabolites
Chlorpyrifos
Diazinon
3,5,6-TCP
Exposure/Dietary Ingestionb
Exposure/Indirect Ingestion0
Dose/Dietary Ingestiond
Dose/Indirect Ingestion6
Aggregated Exposure5
Aggregated Dose8
Expo sure/Inhalation11
Exposure/Dietary Ingestion
Exposure/Indirect Ingestion
Dose/Inhalation1
Dose/Dietary Ingestion
Dose/Indirect Ingestion
Aggregated Exposure
Aggregated Dose
Expo sure/Inhalation
Exposure/Dietary Ingestion
Exposure/Indirect Ingestion
Dose/Inhalation
Dose/Dietary Ingestion
Aggregated Exposure
Aggregated Dose



























2.24*


2.14*





0.65*


0.60**
0.61*
0.56**















1.82*



1.76*






















2.00**

2.06**

1.64*
1.66*








1.70*


1.73*




2.52**

2.33*


2.02*
1.37**
3.45**
1.88*
1.28*
3.22*
1.66*
1.52*


1.81*




Pyrethroid Pesticides
Cyfluthrin
cw-Permethrin
Exposure/Indirect Ingestion
Dose/Indirect Ingestion
Expo sure/Inhalation
Exposure/Dietary Ingestion
Exposure/Indirect Ingestion
Dose/Inhalation
Dose/Dietary Ingestion
Aggregated Exposure
Aggregated Dose











2.38**


2.26**












2.47*
2.44*



















3.14**
1.95*

2 92**
2.34*
2.16*
                                        9-63

-------
Table 9.5.9   Estimated Ratios Between Selected Strata of Geometric Mean Potential
             Exposure and Potential Absorbed Dose Estimates in Participating NC and
             OH Children, When These Ratios Were Significantly Different from One at
             the 0.05 Level3 (cont.)
Pollutant/
Metabolite
trans-Permetbnn
Exposure/Dose Parameter
and Pathway
Expo sure/Inhalation
Exposure/Dietary Ingestion
Dose/Inhalation
Dose/Dietary Ingestion
Estimated Ratio of Geometric Means
(When Significantly Different from 1 at the 0.05 Level)
North Carolina
Urban
vs.
Rural




Low- vs.
Mid/High-
Income
2.45**

2.31**

Day Care
vs. Home




Ohio
Urban
vs.
Rural




Low- vs.
Mid/High-
Income




Day Care
vs. Home

2 92**

2.72*
Acid Herbicides
2,4-D
Expo sure/Inhalation
Exposure/Dietary Ingestion
Exposure/Indirect Ingestion
Dose/Inhalation
Dose/Indirect Ingestion


3 39**

3.68**


0.27**

0.25**
2.23**
1.59*
0.54*
1.94*
0.47*


2.80*

2.84*


0.29**

0.29**





PAHs
Benz[a]anthracene
Benzo[fc]fluoranthene
Benzo[fc]fluoranthene
Benzofg/w'Jperylene
Benzo[a]pyrene
Benzo[e]pyrene
Exposure/Indirect Ingestion
Dose/Indirect Ingestion
Expo sure/Inhalation
Exposure/Indirect Ingestion
Dose/Inhalation
Dose/Indirect Ingestion
Expo sure/Inhalation
Exposure/Indirect Ingestion
Dose/Indirect Ingestion
Exposure/Indirect Ingestion
Dose/Indirect Ingestion
Expo sure/Inhalation
Exposure/Indirect Ingestion
Dose/Inhalation
Dose/Indirect Ingestion
Expo sure/Inhalation
Exposure/Indirect Ingestion
Dose/Inhalation
Dose/Indirect Ingestion





















1.58*

1.52*

1.25*




1.57**

1.51*

1.36*

1.31*




1.81*















3.69**
3.65**

3.55**

3.52**

3.18**
3.16**
3.18**
3.16**

3.35**

3.32**

3.23**

3.21**
0.43**
0.43**

0.43**

0.43**

0.43**
0.43**
0.43**
0.43**

0.41**

0.41**

0.43**

0.44**
3.29**
3.08**

3.15**

2.94**

3.16**
2.95**
3.12**
2 92**

3.09**

2.89**

3.04**

2.84**
                                        9-64

-------
Table 9.5.9   Estimated Ratios Between Selected Strata of Geometric Mean Potential
             Exposure and Potential Absorbed Dose Estimates in Participating NC and
             OH Children, When These Ratios Were Significantly Different from One at
             the 0.05 Level3 (cont.)
Pollutant/
Metabolite
Chrysene
Dibenzfa,/!]
anthracene
lndeno[l,2,3-cd]
pyrene
Exposure/Dose Parameter
and Pathway
Expo sure/Inhalation
Exposure/Indirect Ingestion
Dose/Inhalation
Dose/Indirect Ingestion
Exposure/Indirect Ingestion
Dose/Indirect Ingestion
Expo sure/Inhalation
Exposure/Indirect Ingestion
Dose/Inhalation
Dose/Indirect Ingestion
Estimated Ratio of Geometric Means
(When Significantly Different from 1 at the 0.05 Level)
North Carolina
Urban
vs.
Rural










Low- vs.
Mid/High-
Income
1.57**

1.52*



1.48*

1.43*

Day Care
vs. Home










Ohio
Urban
vs.
Rural

3.51**

3.47**
3.50**
3.47**

3.34**

3.31**
Low- vs.
Mid/High-
Income

0.42**

0.42**
0.44**
0.44**

0.43**

0.43**
Day Care
vs. Home

3.24**

3.03**
3.19**
2.98**

3.20**

3.00**
Phthalates
Benzylbutylphthalate
Di-w-butylphthalate
Exposure/Dietary Ingestion
Exposure/Indirect Ingestion
Dose/Dietary Ingestion
Dose/Indirect Ingestion
Expo sure/Inhalation
Exposure/Dietary Ingestion
Exposure/Indirect Ingestion
Dose/Inhalation
Dose/Dietary Ingestion
Dose/Indirect Ingestion
Aggregated Exposure
Aggregated Dose
-

-









-

-





0.58*



-

-

1.77**


1.54**








0.65*


0.63*
















2.83**
2.73**
2.44*
2.54**
1.44*
2.17**
2.02**
1.34*
1.87*
1.88**
2.07**
1.76*
Phenols
Bisphenol-A
Expo sure/Inhalation
Exposure/Dietary Ingestion
Dose/Dietary Ingestion
Aggregated Exposure
Aggregated Dose











2.47**
2.19**
2.12**
1.85**





1.38*









                                        9-65

-------
Table 9.5.9   Estimated Ratios Between Selected Strata of Geometric Mean Potential
               Exposure and Potential Absorbed Dose Estimates in Participating NC and
               OH Children, When These Ratios Were Significantly Different from One at
               the 0.05 Level3 (cont.)
Pollutant/
Metabolite
Exposure/Dose Parameter
and Pathway
Estimated Ratio of Geometric Means
(When Significantly Different from 1 at the 0.05 Level)
North Carolina
Urban
vs.
Rural
Low- vs.
Mid/High-
Income
Day Care
vs. Home
Ohio
Urban
vs.
Rural
Low- vs.
Mid/High-
Income
Day Care
vs. Home
PCBs
PCB101 (Exposure/Inhalation ||

II

1.73*
a Dashed cells indicate that no analysis was performed on the exposure/dose estimates for the given exposure route due to the sample media
entering into their calculation not achieving requirements on the percentage of detected measures. Blank cells indicate that a ratio was estimated
but was not significantly different from one at the 0.05 level. Note that pollutants, or exposure routes for a given pollutant, have been excluded
from this table if all cells within the rows corresponding to these pollutants or exposure routes would have been blank or dashed within this table.
All estimated ratios for each exposure route and each pollutant, along with corresponding 95% confidence intervals on these ratios, are presented
in Table R-l (NC) and Table R-2 (OH) of Appendix R.
b Potential exposure level via dietary ingestion
0 Potential exposure level via indirect ingestion
d Potential absorbed dose via dietary ingestion
' Potential absorbed dose via indirect ingestion
f Aggregated potential exposure level
8 Aggregated potential absorbed dose
h Potential exposure level via inhalation
1 Potential absorbed dose via inhalation

* Statistically significantly different from 1 at the 0.05 level, but not at the 0.01 level.
** Statistically significantly different from 1 at the 0.01 level.
9.5.4.1    Results of Analyses on NC Exposure/Dose Estimates and Urinary Biomarker
           Concentrations

        Between urban and rural NC children, potential exposure level and potential absorbed
dose differed significantly at the 0.01  level in only one instance: for 2,4-D via indirect ingestion.
On average, urban NC children had estimated potential exposure/dose estimates for 2,4-D via
indirect ingestion that exceeded three times that of rural NC children.

        Significant differences between low-income and middle/high-income strata in estimated
potential  exposure and/or absorbed dose via inhalation for NC children were observed at the 0.01
level for cis- and /rara'-permethrin and chrysene, and at the 0.05 level for five other PAHs
(benzo[&]fluoranthene, benzo[A;]fluoranthene, benzo[a]pyrene, benzo[e]pyrene, and
indeno[l,2,3-cJ]pyrene) and diazinon. Via the inhalation route, low-income NC children tended
to have 36% to 58% higher exposure levels and absorbed doses of the PAHs compared to
middle/high-income children, and from 100% to 150% higher exposure levels and absorbed
doses for diazinon, cis- and ^ram'-permethrin. Via the indirect ingestion route, significant
differences existed in potential exposures and absorbed dose at the 0.01 level for 2,4-D, where
low-income NC children experienced only 25% of the potential exposure levels and absorbed
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doses compared to middle/high-income children. For 3,5,6-TCP, significant differences were
observed at the 0.01 level for potential absorbed dose via the dietary ingestion route and for
aggregate potential absorbed dose (and at the 0.05 level for potential exposure level via indirect
ingestion and for aggregate potential exposure), where low-income NC children averaged about
60% of the potential exposures and absorbed doses compared to middle/high-income children.

       Compared to stay-at-home children, NC children who attend day care centers were
associated with 59% to 123% higher estimated potential exposure levels and absorbed doses to
2,4-D via the inhalation and dietary ingestion routes, but approximately 50% lower
exposures/doses via the indirect ingestion route. These differences were statistically significant
at the 0.05 level, with one (exposure via inhalation) significant at the 0.01 level.  These two
groups of children also differed significantly at the 0.01 level in estimated potential exposure
levels and absorbed doses via dietary ingestion for bisphenol-A and via inhalation for di-n-
butylphthalate. In each case, day care children tended to have from 54% to 147% higher
estimated exposure or absorbed dose estimates compared to stay-at-home children. For
bisphenol-A, the estimated aggregated potential exposure and  absorbed dose for day care
children was significantly different from (and approximately twice as high as) stay-at-home
children at the 0.01 level.

       Table R-5 of Appendix R shows that statistical analysis of urinary biomarker
concentration was  limited to 2,4-D, 3,5,6-TCP, and pentachlorophenol, as these were the only
pollutants that were analyzed in urine (out of six) and detected in at least 50% of the samples for
NC children. IMP measurements in NC urine samples were not statistically analyzed because
the analytical method did not provide adequate quantitative recoveries. Urine concentrations for
participating NC children did not differ significantly at the 0.05 level between the three pairs of
strata (urban vs. rural, low-income vs. middle/high-income, day care vs. stay-at-home children)
for these three pollutants, regardless of whether the concentrations were adjusted for specific
gravity or creatinine levels.

9.5.4.2    Results of Analyses on OH Exposure/Dose Estimates and Urinary Biomarker
          Concentrations

       Between urban and rural OH children, estimated potential exposure level  and potential
absorbed dose via the indirect ingestion route differed significantly at the 0.01 level for all nine
target PAHs, where urban OH children had estimated potential exposure/dose estimates that
were from three to four times as high, on average,  than rural OH children, and at  the 0.05 level
for cyfluthrin and 2,4-D, where estimates for urban OH children were from two to three times as
high as rural children.  For di-w-butylphthalate via the inhalation route, estimated potential
exposure/dose estimates for urban OH children differed significantly at the  0.05 level and were
only about 65% of the estimates for rural OH children, on average.  For those pollutants having
aggregate exposure/dose calculated, no significant differences were observed at the 0.05 level
between urban and rural OH children.
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       Significant differences between low-income and middle/high-income OH children in
potential exposure and/or absorbed dose were observed at the 0.01 level for 2,4-D and all target
PAHs via indirect ingestion and for chlorpyrifos via dietary ingestion.  When significant
differences occurred via indirect ingestion, low-income OH children tended to have
exposures/doses that were 30% to 45% lower than middle/high-income OH children. In
contrast, low-income OH children had chlorpyrifos exposures via dietary ingestion that were
twice as high on average as for middle/high-income OH children. Exposures via inhalation to
bisphenol-A and 3,5,6-TCP were 38% and 70% higher, respectively, for low-income children
compared to middle/high-income children, but these were significant only at the 0.05 level. For
those pollutants having aggregate exposure/dose calculated, significant differences in these
aggregated estimates between low-income and middle/high-income OH children were observed
only for chlorpyrifos and at the 0.05 level, with low-income children averaging about 65%
higher estimates for both potential exposure and absorbed dose.

       Significant differences in potential exposure and/or potential absorbed dose estimates
between OH day care children and OH stay-at-home children were observed at the 0.01 level for
chlorpyrifos, the nine target PAHs, benzylbutylphthalate, and c/'s-permethrin via indirect
ingestion; for cis- and fr'am'-permethrin via dietary ingestion; and for diazinon,
benzylbutylphthalate, and di-w-butylphthalate via both exposure routes. In all of these instances,
day care children averaged higher exposures and/or doses compared to stay-at-home children.
The largest differences  occurred with the PAHs and diazinon via indirect ingestion, where
exposure/dose estimates averaged over three times higher for day care children than for stay-at-
home children. Aggregate potential exposure level and/or aggregate potential absorbed dose
differed significantly between day care and stay-at-home  children at the 0.01  level for di-w-
butylphthalate, and at the 0.05 level for diazinon and cis-  and trans-permethnn, with the largest
differences between the two groups occurring for the two permethrins (where day care children
averaged more than double the exposure levels and/or doses  compared to stay-at-home children
when they differed significantly).

       Table R-6 of Appendix R shows that statistical analysis of urinary biomarker
concentration was performed for five pollutants (2,4-D, 3,5,6-TCP, 1-hydroxypyrene,
pentachlorophenol, 3-PBA) that were analyzed in urine for OH and were detected in at least 50%
of the samples for OH children.  Urine concentrations  differed significantly at the 0.05 level
between day care and stay-at-home OH children only for  2,4-D, with this result holding for
unadjusted and adjusted urine concentrations. Here, day care children tended to have 2,4-D
concentrations in urine  samples that were  only about 65% of the concentrations for stay-at-home
children. No other significant differences between strata were observed for any other pollutant,
regardless of whether the concentrations were adjusted for specific gravity  or creatinine levels.

9.5.4.3    Comparing Potential Exposure, Potential Absorbed Dose, and Urine Concentrations
          Between Children and Adults in the  Same Household

       For potential exposure level and potential  absorbed dose, Table R-9 of Appendix R
presents  estimated ratios of geometric means for NC children versus adults in the same

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household for a given exposure route, along with 95% confidence intervals on this ratio. Table
R-10 presents the same results for the urinary biomarker concentrations for NC.  The
corresponding tables for the OH portion of the study are Table R-l 1 (potential exposure level
and potential absorbed dose) and Table R-12 (urinary biomarker) of Appendix R. In Tables R-9
through R-12, a ratio of greater than one implies that the given exposure or dose measurement
tended to be higher for the monitored child than for the child's adult caregiver in the same
household. The columns of these tables specify the strata for which the ratio represents, with the
first of these columns representing the entire set of study households within the given state. P-
values for the statistical tests which were below 0.05 (indicating significant differences at the
0.05 level) are found in the last four columns of Table R-3 (for NC potential exposure and
absorbed dose), Table R-4 (for OH potential exposure and absorbed dose),  Table R-7 (for NC
urinary biomarker concentrations) and Table R-8 (for OH urinary biomarker concentrations) in
Appendix R.

       For both states and for nearly all exposure routes, statistically significant differences
were observed at the 0.01 level in potential exposure/dose estimates for each target pollutant
between participating children and their adult caregivers living in the same households.  The
nature of the differences between children and adults was heavily influenced by the
physiological and behavioral differences between them.  For example, via the inhalation route,
children tended to have lower potential exposures to these pollutants than their adult caregivers,
but this was primarily due to their lower ventilation rates. In contrast, potential absorbed doses
were higher for children than for adults because of their smaller body weights. Via the indirect
ingestion route, children tended to have higher potential exposure/dose levels than adults, partly
because children tend to have higher soil and dust ingestion rates than adults due to their
different activity patterns. For the dietary ingestion route, statistical analyses to compare children
and adult exposures could be performed only on 2,4-D, PCP, and 3,5,6-TCP data, due to neutral
pollutants not being measured in adult food samples.  When significant differences were present
between children  and adults for potential exposure/dose via dietary ingestion, children tended to
have higher estimates than adults. For both states, estimated aggregate potential absorbed  dose
levels for 2,4-D and 3,5,6-TCP differed significantly at the 0.01 level between children and their
adult caregivers within the same household, with children having roughly 4 to 5 times the
potential absorbed dose compared to adults.

       The estimates in Table R-10  of Appendix R indicate that there is no statistically
significant difference in urinary 2,4-D concentrations (ng/mL) at the 0.05 level between
participating NC children and adults in the same household when the concentrations are either
unadjusted or adjusted for specific gravity. However,  if adjusted for creatinine (|imole/mole),
2,4-D concentrations averaged about 80% higher in children samples versus adult samples. This
difference was statistically significant at the 0.01  level, as were differences associated with
children in NC urban areas, from low-income families, or who attended day care centers. When
either unadjusted  or adjusted for  specific gravity, urinary concentrations in children were from
30% to 40% higher than their adult caregivers for PCP and 3,5,6-TCP, with the differences being
statistically significant at the 0.05 level.  However, when urinary concentrations were adjusted
for creatinine levels, these differences became considerably larger and significant at the 0.01

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level. This trend (i.e., children having higher concentrations of 2,4-D, PCP, and 3,5,6-TCP
compared to their adult caregivers) agreed with that seen for estimated aggregate potential
absorbed dose in Table R-9.

       The descriptive statistics of NC urinary biomarker concentrations, found in Appendix P,
show that two hydroxy-PAHs were detected in fewer children's urine samples than adults' urine
samples. These two pollutants were detected in less than 3% of all children's urine samples
(n=128). In contrast, detectable levels of l-hydroxybenz[a]anthracene and 3-hydroxychrysene
were found in approximately 31% and 8%, respectively, of adults' urine samples (n=128). In the
previous pilot study (7), these two hydroxy-PAHs were detected in more than 70% of the urine
samples (24 children and 24 adults).  This greater detection in the earlier study  is primarily due
to the analytical method used in the previous study, which was targeted at PAH metabolites and
had a lower estimated detection limits (-0.01 ng/mL). The method used for the CTEPP study
was modified in order to include metabolites from other pollutant classes such as 2,4-D, PCP,
and 3,5,6-TCP, which increased the estimated detection limit for hydroxy-PAHs to -0.2 ng/mL.

       For all five pollutants included in the analysis of OH urine data and in Table R-12, urine
concentrations adjusted for creatinine levels differed significantly at the  0.01 level between OH
children and adults in the same household, both overall and  separately within each stratum.
These creatinine-adjusted concentrations were higher in children samples by factors of 2 or 3
compared to adult samples.  If no adjustment is made or when adjusting  for specific gravity,
urine concentrations differed significantly between children and adults at the 0.01 level for only
three of the five pollutants (i.e., all but 1-hydroxypyrene and 3-phenoxybenzoic acid), and the
extent to which children's concentrations were higher than adults was less than when a
creatinine adjustment was made.  Selected strata (rural, middle/high-income, day care children)
did not see  a significant difference at the 0.05 level between children and adults for 2,4-D urine
concentrations that were either unadjusted or adjusted for specific gravity.

       The descriptive statistics of OH urinary biomarker concentrations, found in Appendix Q,
show that seven hydroxy-PAHs, 2,4-D, 3,5,6-TCP, 3-phenoxybenzoic acid, and PCP were
measured in OH children and adults' urine samples. While IMP was also measured, the
analytical method employed in this study could not provide quantitative  recoveries for IMP,
which contributed to  less than 10% of urine  samples having measurable  levels of IMP.
Detectable concentrations for 2,4-D, 3,5,6-TCP, 3-phenoxybenzoic acid, and PCP were found in
most urine samples. While most OH children and adult urine samples had detectable
concentrations for 1-hydroxypyrene, fewer urine samples had detectable levels of 1- and 3-
hydroxybenz[a]anthracene and 3- and 6-hydroxy chrysene.

9.6    Goal 4: To Apportion Exposures among the Inhalation, Dietary Ingestion, and
       Indirect Ingestion Routes

       For the eight pollutants and metabolites listed at the end of Section 9.2,  aggregate
potential exposure level and aggregate potential absorbed dose were estimated by summing the
route-specific exposure/dose estimates across the three  exposure routes characterized in this

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study (inhalation, dietary ingestion, and indirect ingestion).  The statistical analyses performed in
support of Goal 4 characterized how these aggregate exposure/dose estimates were apportioned
across the three exposure routes, so that the routes could be evaluated based on their contribution
to total exposure/dose.

9.6.1   Sub-goal 4.1:  To Estimate the Proportion of Aggregated Exposure and Dose that is
       Associated with a Given Exposure Route for Participating Children, Overall and by
       Stratum

       Analysis #1 under Goal 4 involved calculating the proportion of aggregate potential
exposure level and absorbed dose under each exposure route for each child participant, then
fitting the logistic regression model (8-8) in Section 8.5.2.3 to these proportions to estimate
mean proportions as a function of urbanicity, income category, and day care status. Table 9.6.1
contains estimates of the mean proportions that are attributable to each exposure route,
calculated separately by pollutant and state across all participating children. Tables 9.6.2 and
9.6.3 contain mean proportions by stratum for NC and OH children, respectively, when the test
for significance of the given strata (i.e., urban and rural  strata, low-income and middle/high-
income strata, or stay-at-home and day care strata) on the  overall proportion was significant at
the 0.05 level. Tables S-l and S-2 of Appendix S  contain estimates of mean proportions for each
stratum and exposure route and 95% confidence intervals  on these mean proportions, for
participating  children in NC and OH, respectively. Results presented in these tables represent
mean proportions of both aggregate potential exposure level and aggregate potential absorbed
dose.

       Note that in some cases, the outcome of the statistical analysis presented in Tables 9.6.2
and 9.6.3, as well as Tables S-l through S-4 in Appendix  S,  suggested that a significant stratum
effect was present when, in fact, the estimated mean proportions within the different strata were
either each very  large or very small. Such an outcome does  not necessarily suggest that the
difference in  the estimated proportion between the strata was significant from a practical
standpoint. Thus, caution should be taken in making inferences from the results in these tables
when the overall mean percentages for certain exposure routes were either very small (e.g., less
than 5%) or very large (e.g., greater than 95%).

       Among the adults in this study, exposure and dose estimates for all three exposure routes,
and therefore aggregate exposure/dose estimates, could  be characterized for only two of the eight
pollutants (2,4-D and 3,5,6-TCP). This is because adult food samples were not analyzed for the
other six pollutants, and therefore, dietary exposure/dose estimates could not be calculated for
them. For these  two pollutants, Table 9.6.4 contains estimates of the mean proportions
attributable to each exposure route as calculated over all participating adult caregivers, by
pollutant and state.  Tables S-3 and S-4 of Appendix S contain estimates of mean proportions for
each stratum  and exposure route, as well as  95% confidence intervals on these mean proportions,
for participating adults in NC and OH, respectively.  Note from these two tables that for NC and
OH adults, the stratum effect on the overall  proportion was not significant at the 0.05 level for
either of the two pollutants or for any of the exposure routes.

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Table 9.6.1.   Estimated Mean Proportion of Aggregate Potential Exposure Level and
               Potential Absorbed Dose in Participating NC and OH Children That is
               Attributable to Each Exposure Route, Calculated Across All Children"
Pollutant/Metabolite
Estimate of the Overall Mean Proportion of Aggregate Exposure/Dose
in Participating Children
North Carolina
Inhalation
Dietary
Ingestion
Indirect
Ingestion
Ohio
Inhalation
Dietary
Ingestion
Indirect
Ingestion
OP Pesticides and Metabolite
Chlorpyrifos
Diazinon
3,5,6-TCP
0.39
0.40
0.03
0.54
0.55
0.95
0.06
0.05
0.02
Pyrethroid Pesticides
c/5-Permethrin
/raws-Permethrin
0.05
0.04
0.55
0.57
0.39
0.37
0.19
0.33
0.02
0.76
0.62
0.98
0.04
0.05
0.01

0.04
0.04
0.56
0.58
0.39
0.37
Acid Herbicides
2,4-D
0.03
0.95
0.02
0.03
0.92
0.03
Phthalates
Di-w-butylphthalate
0.06
0.93
0.01
0.18
0.80
0.02
Phenols
Bisphenol-A
0.01
0.99
<0.01
0.01
0.99
O.01
* Estimates of mean proportions are based on a logistic regression analysis fitted to the mean proportions calculated for each participating child.
Estimated 95% confidence intervals on these mean proportions are given in the second column of Table S-l (NC) and Table S-2 (OH) of
Appendix S.
                                               9-72

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Table 9.6.2    Estimated Mean Proportion of Aggregate Potential Exposure Level and
                Potential Absorbed Dose in Participating NC Children That is Attributable
                to Each Exposure Route, Calculated by Stratum, When Differences Between
                Pairs of Strata Were Significant at the 0.05 Level"
Pollutant/
Metabolite
Exposure Route
Stratum
Estimate of
Stratum Mean
Proportion
P-value of Test
for Significant
Stratum Effect
OP Pesticides and Metabolite
Diazinon
3,5,6-TCP
Inhalation
Indirect Ingestion
Inhalation
Low-Income Children
Middle/High-Income Children
Low-Income Children
Middle/High-Income Children
Low-Income Children
Middle/High-Income Children
Non-Day Care Children
Day Care Children
0.46
0.34
0.04
0.06
0.04
0.02
0.03
0.01
0.008**
0.049*
0.018*
0.019*
Pyrethroid Pesticides
cw-Permethrin
/raws-Permethrin
Inhalation
Inhalation
Low-Income Children
Middle/High-Income Children
Low-Income Children
Middle/High-Income Children
Non-Day Care Children
Day Care Children
0.07
0.03
0.07
0.03
0.06
0.03
0.020*
0.004**
0.048*
Acid Herbicides
2,4-D
Dietary Ingestion
Inhalation
Indirect Ingestion
Urban Children
Rural Children
Urban Children
Rural Children
Low-Income Children
Middle/High-Income Children
0.92
0.96
0.04
0.02
0.01
0.03
0.038*
0.021*
0.009**
Phthalates
Di-w-butylphthalate
Dietary Ingestion
Inhalation
Urban Children
Rural Children
Urban Children
Rural Children
0.91
0.94
0.08
0.05
0.014*
0.010*
Phenols
Bisphenol-A
Dietary Ingestion
Inhalation
Non-Daycare Children
Daycare Children
Non-Daycare Children
Daycare Children
0.98
0.99
0.02
0.01
0.001**
0.001**
a Estimates of mean proportions for specific strata are based on a logistic regression analysis fitted to the mean proportions calculated for each
participating child. Estimated 95% confidence intervals on these mean proportions are given in the fourth column of Table S-1 of Appendix S.
* Statistically significant at the 0.05 level, but not at the 0.01 level.
** Statistically significant at the 0.01 level.
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Table 9.6.3    Estimated Mean Proportion of Aggregate Potential Exposure Level and
                Potential Absorbed Dose in Participating OH Children That is Attributable
                to Each Exposure Route, Calculated by Stratum, When Differences Between
                Pairs of Strata Were Significant at the 0.05 Level"
Pollutant/
Metabolite
Exposure Route
Stratum
Estimate of
Stratum Mean
Proportion
P-value of Test
for Significant
Stratum Effect
OP Pesticides and Metabolite
Chlorpyrifos
Diazinon
3,5,6-TCP
Indirect Ingestion
Indirect Ingestion
Dietary Ingestion
Inhalation
Low-Income Children
Middle/High-Income Children
Non-Day Care Children
Day Care Children
Low-Income Children
Middle/High-Income Children
Low-Income Children
Middle/High-Income Children
Low-Income Children
Middle/High-Income Children
0.03
0.05
0.03
0.06
0.03
0.07
0.97
0.99
0.03
0.01
0.001**
0.038*
0.009**
0.023*
0.010**
Pyrethroid Pesticides
cw-Permethrin
/raws-Permethrin
Inhalation
Inhalation
Urban Children
Rural Children
Low-Income Children
Middle/High-Income Children
Urban Children
Rural Children
0.06
0.03
0.02
0.06
0.05
0.03
0.010*
0.001**
0.015*
Acid Herbicides
2,4-D
Dietary Ingestion
Indirect Ingestion
Low-Income Children
Middle/High-Income Children
Urban Children
Rural Children
0.95
0.89
0.07
0.02
0.040*
O.001**
Phthalates
Di-w-butylphthalate
Dietary Ingestion
Inhalation
Indirect Ingestion
Non-Day Care Children
Day Care Children
Non-Day Care Children
Day Care Children
Non-Day Care Children
Day Care Children
0.76
0.84
0.22
0.15
0.02
0.01
0.017*
0.047*
0.008**
Phenols
Bisphenol-A
Dietary Ingestion
Inhalation
Non-Daycare Children
Daycare Children
Urban Children
Rural Children
0.99
0.99
0.01
0.00
0.015*
0.039*
a Estimates of mean proportions for specific strata are based on a logistic regression analysis fitted to the mean proportions calculated for each
participating child. Estimated 95% confidence intervals on these mean proportions are given in the fourth column of Table S-2 of Appendix S.
* Statistically significant at the 0.05 level, but not at the 0.01 level.
** Statistically significant at the 0.01 level.
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Table 9.6.4   Estimated Mean Proportion of Aggregate Potential Exposure Level and
              Potential Absorbed Dose in Participating NC and OH Adults That is
              Attributable to Each Exposure Route, Calculated Across All Adults"
Pollutant/Metabolite
3,5,6-TCP
2,4-D
Estimate of the Overall Mean Proportion in Participating Adults
North Carolina
Inhalation
0.05
0.05
Dietary
Ingestion
0.94
0.93
Indirect
Ingestion
0.01
0.01
Ohio
Inhalation
0.02
0.04
Dietary
Ingestion
0.98
0.93
Indirect
Ingestion
<0.01
0.03
* Estimates of mean proportions are based on a logistic regression analysis fitted to the mean proportions calculated for each participating adult.
Estimated 95% confidence intervals on these mean proportions are given in the second column of Table S-3 (NC) and Table S-4 (OH) of
Appendix S.
       For NC children, the dietary ingestion exposure route was the dominant of the three
routes for each of the eight pollutants, with the mean proportion exceeding 85% for 3,5,6-TCP,
2,4-D, di-w-butylphthalate, and bisphenol-A (Table 9.6.1). Similar results were observed for
3,5,6-TCP and 2,4-D in NC adults (Table 9.6.4). For the two OP pesticides (chlorpyrifos and
diazinon), the mean proportion for the inhalation route in NC children was approximately 40%;
this proportion was the highest seen for the inhalation route among the eight pollutants. (The
estimated mean proportion for inhalation was less than  10% for each of the other six pollutants.)
The mean percentage for the indirect ingestion route in NC children was below 10% for each
pollutant except cis- and ^ram'-permethrin, where the estimated percentages were 39% and 37%,
respectively.

       For OH children, the dietary ingestion exposure route was also the dominant of the three
routes for each of the eight pollutants (Table 9.6.1).  The mean proportion for the dietary
ingestion route exceeded 90% for 3,5,6-TCP and 2,4-D (as it also did for OH adults), equaled
99% for bisphenol-A, equaled 80% for di-w-butylphthalate, exceeded 60% for the two  OP
pesticides (chlorpyrifos and diazinon),  and exceeded 50% for cis- and /ram'-permethrin.  The
mean proportion for the inhalation route was largest for diazinon at 33%. The mean percentage
for the indirect ingestion route was below 10% for most pollutants except for cis- and trans-
permethrin, where the estimated percentages were 39% and 37%, respectively.

       Because the two OP pesticides are more volatile than the two pyrethroid pesticides, this
could partly contribute to differences in the level of importance of the exposure routes
(inhalation vs. indirect ingestion) to total exposure/dose that was seen for both states.
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9.6.2   Sub-goal 4.2:  For Each Exposure Route, Determine if This Proportion Differs for
       Children in Urban and Rural Settings, from Low-and Middle/High-Income Families,
       and Who Attend Day Care or Stay at Home

       The last column in Tables S-l through S-4 of Appendix S contains p-values of tests
performed in the logistic regression model fitting, with the tests determining whether the
estimated mean proportion of total exposure/dose differs significantly between two strata for a
given exposure route and pollutant. These tests were performed for three pairs of strata:  low-
income and middle/high-income level, urban and rural strata, and day care and stay-at-home
children. For proportions of total exposure/dose associated with participating NC and OH
children, those p-values falling below 0.05 were documented in the last columns of Tables 9.6.2
and 9.6.3, respectively. (For adults in both NC and OH, none of these p-values in Tables S-3
and S-4 of Appendix S are below 0.05 for either 3,5,6-TCP or 2,4-D.)

       For NC children (Table 9.6.2), significant differences in the mean proportion were
observed at the 0.05 level between low-income and middle/high-income strata for diazinon via
the inhalation and indirect ingestion routes, for 3,5,6-TCP and for cis- and ^ram'-permethrin via
the inhalation route, and for 2,4-D via the indirect ingestion route.  Significant differences
between urban and rural children were observed at the 0.05 level for 2,4-D and di-n-
butylphthalate via the dietary ingestion and inhalation routes. Significant differences between
day care and non-day  care children were observed at the 0.05 level for 3,5,6-TCP via the indirect
ingestion route, for ^ram'-permethrin via the inhalation route, and for bisphenol-A via each route.
However, the estimated proportion of total exposure/dose of bisphenol-A attributed to indirect
ingestion was virtually zero, implying that any difference among strata was  not significant from
a practical standpoint.

       For OH children (Table 9.6.3), significant differences in the mean proportion were
observed at the 0.05 level between low-income and middle/high-income strata for the two OP
pesticides (chlorpyrifos and diazinon) via the indirect ingestion route, for 3,5,6-TCP via the
dietary and inhalation routes, for ^ram'-permethrin via the inhalation route, and for 2,4-D via the
dietary ingestion route. Significant differences between OH urban and rural children were
observed at the 0.05 level for bisphenol-A and cis- and trans-permethrin via the inhalation route
and for 2,4-D via the indirect ingestion route.  Significant differences between OH stay-at-home
and day care children  were observed at the 0.05 level for chlorpyrifos via the indirect ingestion
route, for di-w-butylphthalate in each  route, and for bisphenol-A via the dietary ingestion and
inhalation routes.

9.6.3   Sub-goal 4.3:  Determine Whether Significant Differences Exist Between Exposure
       Routes

       Analysis #2 in Section 8.5.2.3 was used to compare average log-transformed potential
exposure level and potential absorbed dose measures between exposure routes. This analysis
involved fitting model (8-9) of Section 8.5.2.3 to log-transformed measures (represented as a
vector of measures for the three exposure routes) within a multivariate analysis of variance

                                           9-76

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(ANOVA).  This analysis was performed separately for each pollutant addressed under Goal 4,
as well as separately for potential exposure level and potential absorbed dose, for children and
adults, and for each state.

       Results of the multivariate ANOVAs indicated that for each pollutant, highly significant
differences existed between exposure routes for both potential exposure level and potential
absorbed dose (p<0.0001).  This result held for both children and adults in NC and OH.  This
result was apparent by reviewing the tables in Section 9.6.1, where one exposure route typically
dominated the other two for each pollutant in each state. Note that the model was unable to
converge when being fitted to potential exposure level estimates of c/'s-permethrin in OH
children, and therefore, comparisons between exposure routes could not be performed in this
instance.

9.6.4  Sub-goal 4.4:  Characterize How These Estimates Differ Overall Between Pairs of
       Exposure Routes

       For each pair of exposure routes, each multivariate ANOVA performed in Section 9.6.3
produced estimates of the ratio of geometric mean potential exposure level or potential absorbed
dose between the two routes,  along with a 95% confidence interval on the ratio.  Tables S-5 and
S-6 of Appendix S present these ratios and confidence intervals for participating children in NC
and OH, respectively.  Similarly, Tables S-7  and S-8 present ratios and confidence  intervals for
participating adult caregivers in NC and OH, respectively. Each row of these tables corresponds
to a particular fit of the multivariate ANOVA.  Those ratios that are significantly different from
one at the 0.05 level are summarized in Table 9.6.5 forNC children, Table 9.6.6 for OH
children, Table 9.6.7 forNC adults, and Table 9.6.8 for OH adults; further discussion of
significant differences from one is found in Section 9.6.5.

       For NC children, Table S-5 of Appendix S shows that for all eight pollutants and for both
potential exposure level and potential absorbed dose, ratios of the dietary ingestion route versus
either the inhalation route or the indirect ingestion route exceeded one. This implies that the
estimated geometric mean exposure/dose estimate via dietary ingestion was larger than the
geometric mean  for either inhalation or indirect ingestion.  Ratios of the inhalation  route to the
indirect ingestion route were greater than one for all pollutants but cis- and /ram'-permethrin,
where the indirect ingestion route was more dominant than the inhalation route. For the two
pollutants that were also included in the data analysis for NC adults (3,5,6-TCP and 2,4-D), the
same conclusions held for both adults and children (Tables 9.6.5 and 9.6.6).
                                           9-77

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Table 9.6.5.   Estimated Ratios Between Two Exposure Routes of Geometric Mean
               Potential Exposure Level and Potential Absorbed Dose Estimates in
               Participating NC Children, When These Ratios Were Significantly Different
               From One at the 0.05 Level3
Pollutant/
Metabolite
Parameter
Ratio of Geometric Means
Dietary Ingestion
Route vs. Inhalation
Route
Dietary Ingestion
Route vs. Indirect
Ingestion Route
Inhalation Route vs.
Indirect Ingestion
Route
OP Pesticides and Metabolite
Chlorpyrifos
Diazinon
3,5,6-TCP
Potential Exposure Level
Potential Absorbed Dose
Potential Exposure Level
Potential Absorbed Dose
Potential Exposure Level
Potential Absorbed Dose




72.58**
72.84**
12.60**
12.61**
20.70**
20.68**
229.05**
230.39**
8.92**
8.93**
14.58**
14.62**
3.16**
3.16**
Pyrethroid Pesticides
cw-Permethrin
trans-Permetbnn
Potential Exposure Level
Potential Absorbed Dose
Potential Exposure Level
Potential Absorbed Dose
22.18**
22.17**
22.02**
21.81**




0.09**
0.09**
0.08**
0.08**
Acid Herbicides
2,4-D
Potential Exposure Level
Potential Absorbed Dose
48.67**
48.63**
194.41**
193.78**
3 99**
3.98**
Phthalates
Di-w-butylphthalate
Potential Exposure Level
Potential Absorbed Dose
22.92**
22.61**
126.17**
124.38**
5.50**
5.50**
Phenols
Bisphenol-A
Potential Exposure Level
Potential Absorbed Dose
207.17**
207.37**
2235.24**
2212.20**
10.79**
10.67**
a Blank cells correspond to ratios that were not significantly different from one at the 0.05 level. All ratios are presented, regardless of their
significance, along with 95% confidence intervals on these ratios, within Table S-5 of Appendix S.

** Significantly different from 1 at the 0.01 level.
                                               9-78

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Table 9.6.6.   Estimated Ratios Between Two Exposure Routes of Geometric Mean
                Potential Exposure Level and Potential Absorbed Dose Estimates in
                Participating OH Children, When These Ratios Were Significantly Different
                From One at the 0.05 Level3
Pollutant/
Metabolite
Parameter
Ratio of Geometric Means
Dietary Ingestion
Route vs. Inhalation
Route
Dietary Ingestion
Route vs. Indirect
Ingestion Route
Inhalation Route vs.
Indirect Ingestion
Route
OP Pesticides and Metabolite
Chlorpyrifos
Diazinon
3,5,6-TCP
Potential Exposure Level
Potential Absorbed Dose
Potential Exposure Level
Potential Absorbed Dose
Potential Exposure Level
Potential Absorbed Dose
6.03**
6.06**
2.04**
2.04**
132.32**
129.55**
30.88**
31.03**
20.68**
20.78**
546.95**
541.95**
5.12**
5.12**
10.15**
10.19**
4.13**
4.18**
Pyrethroid Pesticides
cw-Permethrin
trans-Permetbnn
Potential Exposure Level
Potential Absorbed Dose
Potential Exposure Level
Potential Absorbed Dose
b
22.00**
24.32**
24.29**
--
2.60*
3.52**
3.38**
--
0.12**
0.14**
0.14**
Acid Herbicides
2,4-D
Potential Exposure Level
Potential Absorbed Dose
52.25**
51.75**
47.52**
47.22**


Phthalates
Di-w-butylphthalate
Potential Exposure Level
Potential Absorbed Dose
4.68**
4.63**
53.07**
51.94**
11.34**
11.21**
Phenols
Bisphenol-A
Potential Exposure Level
Potential Absorbed Dose
181.33**
183.70**
1853.99**
1851.10**
10.22**
10.08**
a Blank cells correspond to ratios that were not significantly different from one at the 0.05 level.  All ratios are presented, regardless of their
significance, along with 95% confidence intervals on these ratios, within Table S-6 of Appendix S.
b No ratios were estimated due to the model being unable to converge when fitted to the data.

* Significantly different from 1 at the 0.05 level, but not at the 0.01 level.
** Significantly different from  1 at the 0.01 level.
                                                  9-79

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Table 9.6.7.   Estimated Ratios Between Two Exposure Routes of Geometric Mean
              Potential Exposure Level and Potential Absorbed Dose Estimates in
              Participating NC Adults, When These Ratios Were Significantly Different
              From One at the 0.05 Level3
Parameter
Ratio of Geometric Means
Dietary Ingestion
Route vs. Inhalation
Route
Dietary Ingestion
Route vs. Indirect
Ingestion Route
Inhalation Route
vs. Indirect
Ingestion Route
3,5,6-TCP(3,5,6-trichloro-2-pyridinol)
Potential Exposure Level
Potential Absorbed Dose
41.76**
41.74**
358.70**
358.31**
8.59**
8.58**
2,4-D (2,4-dichlorophenoxyacetic acid)
Potential Exposure Level
Potential Absorbed Dose
40.74**
40.88**
379.85**
379.64**
9.32**
9 29**
       * Ratios are presented, along with 95% confidence intervals on these ratios, within Table S-7 of Appendix S.
       ** Significantly different from 1 at the 0.01 level.
Table 9.6.8.   Estimated Ratios Between Two Exposure Routes of Geometric Mean
              Potential Exposure Level and Potential Absorbed Dose Estimates in
              Participating OH Adults, When These Ratios Were Significantly Different
              From One at the 0.05 Level3
Parameter
Ratio of Geometric Means (95%CI)
Dietary Ingestion
Route vs. Inhalation
Route
Dietary Ingestion
Route vs. Indirect
Ingestion Route
Inhalation Route
vs. Indirect
Ingestion Route
3,5,6-TCP(3,5,6-trichloro-2-pyridinol)
Potential Exposure Level
Potential Absorbed Dose
102.37**
102.51**
907.46**
907.69**
8.86**
8.85**
2,4-D (2,4-dichlorophenoxyacetic acid)
Potential Exposure Level
Potential Absorbed Dose
49.33**
49.32**
78.75**
78.63**


       a Ratios are presented, along with 95% confidence intervals on these ratios, within Table S-8 of Appendix S.
       ** Significantly different from 1 at the 0.01 level.
                                            9-80

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       For OH children, Table S-6 of Appendix S shows that for all eight pollutants and for both
potential exposure level and potential absorbed dose, ratios of the dietary ingestion route versus
either the inhalation route or the indirect ingestion route exceeded one in all instances, indicating
that dietary ingestion was the dominant exposure route.  The ratios of the inhalation route to the
indirect ingestion route were greater than one for all pollutants but 2,4-D and cis- and trans-
permethrin.  For the two permethrins, Table 9.6.1 showed that the indirect ingestion route was
more dominant than the inhalation route with regard to exposure/dose, while the two routes were
equally inferior to dietary ingestion  for 2,4-D. Although the ratio of 2,4-D exposure/dose
estimates between the inhalation route and the indirect ingestion route exceeded one for OH
adults (Table S-8 of Appendix S), implying larger exposure/dose estimates for the inhalation
route in adults, the ratio was not significantly different from one at the 0.05 level for either
children or adults in OH. Note that  although the multivariate ANOVA model could not
converge to solutions for potential exposure level in OH children for c/s-permethrin, it is
expected (upon viewing the results for the other pollutants) that the outcome would have been
very similar to that given for potential absorbed dose for this pollutant.

       The magnitudes  of the ratios presented in the tables in this section, as well  as the
conclusions made by these ratios, are consistent with the findings found in the tables within
Section 9.6.1. Note that in Tables S-5 through S-8, the second column presents the p-values of
the tests of significant differences among exposure routes.  As mentioned in Section  9.6.3, these
p-values were all less than 0.0001 across all model fits for  both NC and OH.

9.6.5  Sub-goal 4.5:  Identify Which Pairs of Exposure Routes Differ Significantly in These
       Estimates

       Within the multivariate ANOVA model fits discussed in Section 9.6.3 and  Section 9.6.4,
statistical tests were performed to determine whether the estimated ratios reported  in Tables  S-5
through S-8 of Appendix S were significantly different from one, thereby indicating that the pair
of exposure routes had significantly different geometric mean exposure/dose measures.  Those
ratios that were significantly different from one at the 0.05 are presented in Tables 9.6.5 through
9.6.8, with each ratio followed by either one or two asterisks. One asterisk implies that the ratio
is significantly different from one at the 0.05 level, while two asterisks indicate significance at
the 0.01 level.

       For NC children, Table 9.6.5 shows that the ratios of exposure/dose estimates between
dietary ingestion and inhalation were significantly different from (and greater than) one at the
0.01 level for all pollutants but the two OP pesticides (chlorpyrifos and diazinon).  Similarly, the
ratios between dietary ingestion and indirect ingestion were significantly different from (and
greater than) one at the 0.01 level for all pollutants but cis- and /ram'-permethrin.  For all eight
pollutants, the ratio of inhalation to  indirect ingestion was  significantly different from one at the
0.01 level, but these ratios were smaller than one for cis- and ^ram'-permethrin and larger than
one for the other six pollutants. Thus, these findings indicate that the ordering of the exposure
routes for NC children based upon their relative importance to potential exposure/dose is as
follows:
                                           9-81

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•      cis- and ^ram'-permethrin:    dietary ingestion ~ indirect ingestion > inhalation.
•      chlorpyrifos and diazinon:    dietary ingestion ~ inhalation > indirect ingestion
       2,4-D, 3,5,6-TCP, di-w-butylphthalate, bisphenol-A:
                                   dietary ingestion > inhalation > indirect ingestion

where "«" indicates statistical equivalence. For 2,4-D and 3,5,6-TCP, the same ordering of the
exposure routes occurred for NC adults as for children (Table 9.6.7).

       For OH children, Table 9.6.6 shows that the ratios of exposure/dose estimates between
dietary ingestion and either inhalation or indirect ingestion were significantly different from (and
greater than) one for all eight pollutants, where significance was at the 0.05 level for potential
absorbed dose of c/'s-permethrin (for dietary versus indirect ingestion routes) and at the 0.01
level in all other instances. For seven of the eight pollutants (i.e., all pollutants except 2,4-D),
the ratio of inhalation to indirect ingestion was significantly different from one at the 0.01 level,
but these ratios were smaller than one for cis- and /ram'-permethrin and larger than one for the
other five pollutants.  This ratio was not significantly different from one for 2,4-D.  Thus, these
findings, along with the magnitude of the reported ratios, indicate that the ordering of the
exposure routes for OH children based upon their relative importance to potential exposure/dose
is as follows:

•      cis- and ^ram'-permethrin:    dietary ingestion > indirect ingestion > inhalation.
•      2,4-D:                      dietary ingestion > indirect ingestion ~ inhalation
       chlorpyrifos, diazinon, 3,5,6-TCP, di-w-butylphthalate, bisphenol-A:
                                   dietary ingestion > inhalation > indirect ingestion.

For OH adults, the ordering of exposure routes was similar (Table 9.6.8):

•      2,4-D:        dietary ingestion > inhalation  ~ indirect ingestion
•      3,5,6-TCP:    dietary ingestion > inhalation > indirect ingestion.

       The findings in this section indicate that dietary ingestion and inhalation are the two most
important exposure routes for children's exposure to the two OP pesticides (chlorpyrifos and
diazinon). This finding is in agreement with the previous pilot study (10). For the less volatile
pyrethroids (cis- and fram'-permethrin), dietary and indirect ingestion were the two most
important exposure routes.
                                            9-82

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                                     References
1.      Chuang, J. C., Callahan, P. J., Menton, R. G., Gordon, S. M., Lewis, R. G., Wilson, N. K.
       Monitoring methods for polycyclic aromatic hydrocarbons and their distribution in house
       dust and track-in soil. Environ. Sci. Technol. 29(2): 494-500 (1995).

2.      Nishioka, M. G., Burkholder, H. M., Brinkman, M. C., Gordon, S. M., Lewis, R. G.
       Measuring transport of lawn-applied herbicide acids from turf to home: correlation of
       dislodgeable 2,4-D turf residues with carpet dust and carpet surface residues. Environ.
       Sci. Technol. 30: 3313-3320(1996).

3.      Wania, F. and MacKay,  D.  Tracking the distribution of persistent organic pollutants.
       Environ. Sci. Technol. 30(9):  390A-396A (1996).

4.      Morgan, M. K.,  Stout II, D. M., and Wilson, N. K.  A feasibility study of the potential for
       human exposure to pet-borne diazinon residues following lawn applications. Bull.
       Environ. Contam. Toxicol. 66: 295-300 (2000).

5.      Chuang, J. C., Callahan, P. J., Lyu, C. W., Pennybacker, M. R. Characterization of
       polycyclic aromatic hydrocarbon exposure among children of low income families from
       inner city and rural areas. Final  Report on Cooperative Agreement CR 822073, EPA
       600/R-98/163a,  163b, and 163c (1998).

6.      Chuang, J. C., Callahan, P. J., and Lyu, C. W.  Field method evaluation of total exposure
       of children from low-income families that include smokers to polycyclic aromatic
       hydrocarbons. Final Report to U.S. EPA, Contract Number 68-D4-0023, Work
       Assignment No. 9, July  1996.

7.      Chuang, J. C., Callahan, P. J., Lyu, C. W., and Wilson, N. K. Polycyclic aromatic
       hydrocarbon exposures of children in low-income families. J.  Expo. Anal. Environ.
       Epidemiol. 2:  85-98 (1999).

8.      Wilson, N. K., Chuang, J. C., and Lyu, C. Levels of persistent organic pollutants in
       several child day care centers. J. Expo. Anal. Environ. Epidemiol. 11: 419-458 (2001).

9.      Chuang, J. C., Lyu, C., Chou, Y.-L.,  Callahan, P. J., Nishioka, M., Andrews, K., Pollard,
       M. A., Brackney, L., Hines, C., Davis, D. B., and Menton, R.  Evaluation and application
       of methods for estimating children's exposure to persistent organic pollutants in multiple
       media. EPA 600/R-98/164a, 164b, and 164c, (1998).
                                          R-l

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10.    Wilson, N. K., Chuang, J. C., Lyu, C. and Morgan, M. K.  Aggregate exposures of nine
      preschool children to persistent organic pollutants at day care and at home. J. Expo.
      Anal. Environ. Epidemiol. 13: 187-202 (2003).

11.    Wilson, N. K., Chuang, J. C., lachen, R., Lyu, C., Gordon, S. M., Morgan, M. K.,
      Ozkaynak, H., and Sheldon, L. S. Design and sampling methodology for a large study of
      preschool children's aggregate exposures to persistent organic pollutants in their
      everyday environments.  J. Expo. Anal. Environ. Epidemiol. 14, 260-274 (2004).

12.    Roberts, J. W., Budd, W. T., Ruby, M. G., Bond, A. E., Lewis, R. G., Weiner, R. W., and
      Camann, D. E.  Development and Field Testing of a High Volume Sampler for Pesticides
      and Toxics in Dust.  J. Exposure Anal. Environ. Epidemiol.  1, 143-155 (1991).

13.    Lewis, R.G., Fortmann. R.C., and Camann, D.E., Evaluation of methods for monitoring
      the potential exposure of small children to pesticides in the residential environment.
      Archives of Environmental Contamination and Toxicology, 26:37-46, (1994).

14.    Gordon, S.M., Callahan, P.J., Nishioka, M.G., Brinkman, M.C., O'Rourke, M.K.,
      Lebowitz, M.D., and Moschandreas, D.J. Residential environmental measurements in the
      National Human Exposure Assessment Survey (NHEXAS) Pilot Study in Arizona:
      Multimedia results for pesticides and VOCs. J. Expo. Anal. Environ. Epidemiol. 9: 456-
      470, (1999).

15.    Stanek III, E.J., and Calabrese, E.J., Daily estimates of soil ingestion in children.
      Environ. Health Per sped. 103:276-285, (1995).

16.    Stanek III, E.J., and Calabrese, E.J., Soil ingestion estimates for use in site evaluations
      based on the best tracer method. Hum. Ecol. Risk Assess. 1(2): 133-156, (1995).

17.    Ross, J.H., Driver, J.H., Cochran, R.C., Thongsinthusak, T., and Krieger, R.I. Could
      pesticide toxicology studies be more relevant to occupational risk assessment? Ann.
      Occup. Hyg. 2001: 45 (1001): S5-S17.
                                          R-2

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                A Pilot Study of
 Children's Total Exposure
to Persistent Pesticides and
   Other Persistent Organic
          Pollutants (CTEPP)
    M.K. Morgan, L.S. Sheldon, and C.W. Croghan.
          U.S. Environmental Protection Agency
                  Research Triangle Park, NC

    J.C. Chuang, R.A. Lordo, N.K. Wilson, C. Lyu,
            M. Brinkman, N. Morse, Y.L. Chou,
            C. Hamilton, J.K. Finegold, K. Hand,
       and S.M. Gordon. Battelle, Columbus, Ohio
                    PB2006-101286
                    Volume II: Appendices A-S
                    EPA/600/R-04/193

               Contract Number 68-D-99-011
                          Task Order 0002
                  Task Order Project Officer
                         Marsha K. Morgan
          U.S. Environmental Protection Agency
          National Exposure Research Laboratory
          Research Triangle Park, North Carolina
            Office of Research and Development
          National Exposure Research Laboratory
Human Exposure and Atmospheric Sciences Division
                  Research Triangle Park, NC

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                                 List of Appendices
Appendix A  Summary of CTEPP Standard Operating Procedures (SOPs)   	  A-l
Appendix B  CTEPP North Carolina and Ohio Field Study Recruitment Reports	B-l
Appendix C  Summary of Analytical Methods for Determining Target Pollutants in Multimedia
             Samples  	C-l
Appendix D  Quality Assurance/Quality Control Summary for CTEPP North Carolina and
             Ohio Data Collection	  D-l
Appendix E  EPA SAS Program for QA/QC  	E-l
Appendix F  Median Indoor Air Sample Concentrations (ng/m3) in the NC and OH Portions of
             the CTEPP study  	F-l
Appendix G  Algorithms for Estimating Daily Ingestion Rate of Dust and Soil in Children
             Participants	  G-l
Appendix H  Percentages of NC and OH Multimedia Samples with Pollutant Levels At or
             Above the MQL	  H-l
Appendix I   Descriptive Statistics of CTEPP Pollutant/Metabolite Measurements in NC
             Multimedia Samples  	 1-1
Appendix J   Descriptive Statistics of CTEPP Pollutant/Metabolite Measurements in OH
             Multimedia Samples  	J-l
Appendix K  Detailed Results of Statistical Analyses to Test for Significant Differences in
             Multimedia Pollutant Measurements Between Selected Strata, by State and Media
             Type	  K-l
Appendix L  Descriptive Statistics of Potential Exposure Level and Potential Absorbed Dose
             Estimates for Target Pollutants in Participating NC Children	L-l
Appendix M  Descriptive Statistics of Potential Exposure Level and Potential Absorbed Dose
             Estimates for Target Pollutants in Participating OH Children   	M-l
Appendix N  Descriptive Statistics of Potential Exposure Level and Potential Absorbed Dose
             Estimates for Target Pollutants in Participating NC Adults 	  N-l
Appendix O  Descriptive Statistics of Potential Exposure Level and Potential Absorbed Dose
             Estimates for Target Pollutants in Participating OH Adults 	  O-l
Appendix P  Descriptive Statistics of Urinary Biomarker Concentrations for Target Pollutants
             in NC Study Participants	P-l
Appendix Q  Descriptive Statistics of Urinary Biomarker Concentrations for Target Pollutants
             in OH Study Participants	  Q-l
Appendix R  Detailed Results of Statistical Analyses Performed on Potential Exposure Level
             and Potential Absorbed Dose Estimates and on Urinary Biomarker Concentrations
             for the Study Participants	R-l
Appendix S  Detailed Results of Statistical Analyses to Investigate the Apportioning of
             Aggregated Potential Exposure Level and Aggregated Potential Absorbed Dose
             Estimates for the Study Participants Across Exposure Routes  	S-l

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                    Appendix A







Summary of CTEPP Standard Operating Procedures (SOPs)
                        A-l

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Summary of CTEPP Standard Operating Procedures (SOPs)
CTEPP SOP Number

CTEPP-SOP-1.10
CTEPP-SOP-1.11
CTEPP-SOP-1.12
CTEPP-SOP-1.13
CTEPP-SOP-1.14

CTEPP-SOP-2.10
CTEPP-SOP-2.11
CTEPP-SOP-2.12
CTEPP-SOP-2.13
CTEPP-SOP-2.14
CTEPP-SOP-2.15
CTEPP-SOP-2.16
CTEPP-SOP-2.17
CTEPP-SOP-2.18
CTEPP-SOP-2.19
CTEPP-SOP-2.20
CTEPP-SOP-2.21
CTEPP-SOP-2.22
CTEPP-SOP-2.23
CTEPP-SOP-2.24
CTEPP-SOP-2.25
CTEPP-SOP-2.26
CTEPP-SOP-2.27

CTEPP-SOP-3.10
CTEPP-SOP-3.11
CTEPP SOPs
1. Subject Recruitment
Sample Selection Procedures
Day care Centers Recruitment Procedures
Telephone Sample Households Recruitment Procedures
Informed Consent Procedures
Assigning ID Numbers Procedures
2. Field Sampling
Household Sampling Schedule Procedures
Field Operations Procedures
Collection of Fixed Site Indoor and Outdoor Air Samples for Persistent Organic
Pollutants Procedures
Collection of Food and Drinking Water Samples Procedures
Collection of Urine Samples Procedures
Collection of Dermal Hand Wipe Samples for Persistent Organic Pollutants
Procedures
Collection of Hard Floor Wipe Samples for Persistent Organic Pollutants
Procedures
Collection of Food Preparation Surface Wipe Samples for Persistent Organic
Pollutants Procedures
Collection of Dislodgeable Residues - PUF Roller Samples for Persistent
Pollutants Procedures
Organic
Collection of Floor Dust Samples for Persistent Organic Pollutants Procedures
Collection of Soil Samples for Persistent Organic Pollutants Procedures
Collection of Personal Interview Data Procedures
Recording Data Collection Forms Procedures
Video Taping Child Activities Procedures
Handling Missing Samples/Data Procedures
Conducting Internal Field Audit/Quality Control Procedures
Handling Sample/Data Custody Procedures
Conducting Staff and Participant Training Procedures
3. Storing and Shipping Samples & Data Collection Forms
Storing Study Samples Procedures
Packing and Shipping Study Samples Procedures
                                     A-2

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CTEPP SOP Number
CTEPP-SOP-3.12

CTEPP-SOP-4.10
CTEPP-SOP-4.11
CTEPP-SOP-4.12
CTEPP-SOP-4.13

CTEPP-SOP-5.10
CTEPP-SOP-5.11
CTEPP-SOP-5.12
CTEPP-SOP-5.13
CTEPP-SOP-5.14
CTEPP-SOP-5.15
CTEPP-SOP-5.16
CTEPP-SOP-5.17
CTEPP-SOP-5.18
CTEPP-SOP-5.19
CTEPP-SOP-5.20
CTEPP-SOP-5.21
CTEPP-SOP-5.22
CTEPP-SOP-5.23
CTEPP-SOP-5.24
CTEPP-SOP-5.25
CTEPP-SOP-5.26
CTEPP SOPs
Shipping and Storing Data Collection Forms Procedures
4. Data Processing
Processing Completed Data Forms Procedures
Maintaining/Recording Electronic Chain of Custody Procedures
Entering or Importing Electronic Data Into CTEPP Data Bases Procedures
Translating Videotapes of Child Activities Procedures
5. Laboratory Procedures
Pre-cleaning Filter and XAD-2 Procedures
Pre-cleaning Filter and PUF Procedures
Extracting and Preparing Air Samples for Analysis of Neutral Persistent Organic
Pollutants Pre-cleaning Procedures
Extracting and Preparing Air Samples for Analysis of Polar Persistent Organic
Pollutants Procedures
Extracting and Preparing Dust and Soil Samples for Analysis of Neutral Persistent
Organic Pollutants Procedures
Extracting and Preparing Dust and Soil Samples for Analysis of Polar Persistent
Organic Pollutants Procedures
Extracting and Preparing Dermal Wipe Samples for Analysis of Neutral Persistent
Organic Pollutants Procedures
Extracting and Preparing Surface Wipe Samples for Analysis of Neutral Persistent
Organic Pollutants Procedures
Extracting and Preparing PUF Roller Samples for Analysis of Neutral Persistent
Organic Pollutants Procedures
Extracting and Preparing Liquid Food Samples for Analysis of Persistent Organic
Pollutants Procedures
Extracting and Preparing Solid Food Samples for Analysis of Persistent Organic
Pollutants Procedures
Extracting and Preparing Urine Samples for Analysis of Hydroxy-PAH,
Pentachlorophenol, and 2,4-D Procedures
Extracting and Preparing Urine Samples for Analysis of 3,5,6-Trichloro-2-pyridinol
Procedures
Extracting and Preparing Drinking Water Samples for Analysis of Persistent Organic
Pollutants Procedures
Detection and Quantification of Target Analytes by Gas Chromatography/Mass
Spectrometry (GC/MS) Procedures
Preparation of Surrogate Recovery Standard and Internal Standard Solutions for
Neutral Target Analytes
Preparation of Surrogate Recovery Standard and Internal Standard Solutions for Polar
Target Analytes
A-3

-------
CTEPP SOP Number
CTEPP-SOP-5.27
CTEPP-SOP-5.28
CTEPP-SOP-5.29
CTEPP SOPs
Extracting and Preparing Dermal Wipe and Surface Wipe Samples for Analysis of
Polar Organic Pollutants
Extracting and Preparing Solid Food Samples for Analysis of Polar Organic Pollutants
Extracting and Preparing Liquid Food Samples for Analysis of Polar Organic
Pollutants
A-4

-------
                       Appendix B







CTEPP North Caroline and Ohio Field Study Recruitment Reports

-------

-------
                                                        CTEPP Recruitment Report - North Carolina
                                                                                   Page 1
I.      Introduction

The research study, "Children's Total Exposure to PersistentPesticides and Other Persistent Organic
Pollutants," (CTEPP) is a pilot-scale project involving about 260 children, which investigates the
possible exposures that young children may have to common  contaminants in their everyday
surroundings. These contaminants include several pesticides, phenols, polychlorinated biphenyls,
polycyclic aromatic hydrocarbons, some of which are suspected of being endocrine disrupters. The
targeted compounds are persistent in the indoor and sometimes the outdoor environments, so that
very low levels may exist in the children's surrounding microenvironments and provide a source of
chronic, non-acute exposure.   The  primary purposes  of the research are  to  increase our
understanding of children's exposures to persistent pollutants,  to gain information on the various
activities,  environmental media,  and pollutant characteristics that may  influence children's
exposures,  and to generate further questions and hypotheses for future research.
II      Daycare Center Sample Subjects Recruitment

Detailed subjects recruitment procedures and sample selection methods are documented in CTEPP
SOP 1.10 and SOP1.11.  NC subjects recruitment was conducted in two phases. Phase I daycare
center subj ects recruitment in four NC counties (Durham, Buncombe, Lee, and Mecklenburg) began
in February 2000 and stopped on February 29, 2000 due to the OMB Y2K Census requirement.
Subjects recruitment resumed  in July 2000 and continued through December 2000.  Phase I
recruitment achieved 80% of the target subjects recruitment (enrolled 51 of 64 target subjects).

Phase II recruitment was conducted for the two eastern NC counties affected by the flooding that
resulted from Hurricane Floyd (Edgecombe and Jones). Phase II recruitment began on February
26,2001 and was completed on March 30,2001. Twelve additional subjects were enrolled in phase
II.  The project has achieved 98% of the NC daycare center subject recruitment target (enrolled 63
of 64 target subjects).
III.    Telephone Sample Subjects Recruitment

The sample design utilized for the CTEPP telephone component is intended to fulfill the objectives
of:

   •   Efficiently identifying telephone households having one or more children in the eligible age
       range and meeting the sampling targets in the high and low income domains

   •   Providing coverage of households with unlisted telephone numbers

With respect to the first obj ective, the Marketing Systems Group (MSG) uses Census data, marketing
research data,  and other sources to classify directory-listed households as having one or more
children in the age range of one to five years or no children in that age group. The same data is used
to assign the directory-listed households to an income range. While not all households classified as

-------
                                                         CTEPP Recruitment Report - North Carolina
                                                                                   Page 2


having children in the target age range will indeed have eligible children, the eligibility rate will still
be much higher than a simple random sample of households.

The counts of directory-listed households having children in the target age group for the counties
provided by MSG are considerably less than the Census demographic estimates. A portion of the
eligible households in a study county will be in the group of households that MSG has classified as
having no children in the target age range, but the eligibility rate will  still be very small. We  must
allocate some percentage of our sample to this group of directory-listed households. To allocate a
greater proportion of our total sample to the first group of households we stratified the directory-
listed households.

All directory-listed households in each of the six study counties were assigned to one of the 4 strata:

       1.  Directory-listed households with income above $25,000 and having one or more children
          in the target age range

       2.  Directory-listed households with income below or equal to $25,000  and having one or
          more children in the target age range

       3.  Directory-listed households with income above $25,000 and having no children in the
          target age range

       4.  Directory-listed households  with  income below  or equal to $25,000 and  having  no
          children in the target age range

With respect to the second objective, some counties may have as many as 30% of households with
unlisted telephone numbers, therefore some of the eligible households in a study county will  have
unlisted telephone numbers.  Trying to estimate the eligibility rate for households having unlisted
telephone numbers is difficult. We use a random digit dialing (RDD) approach to give these unlisted
telephone households some chance  of selection.

To implement the RDD approach, MSG first identifies all telephone exchanges in the study county.
Telephone exchanges having very low percentages of directory-listed households in the study county
are deleted. From the remaining exchanges, MSG draws a systematic sample of telephone numbers.
Some of these telephone numbers are residential and some are business and nonworking. To prevent
a directory-listed telephone number from being  sampled in both the RDD frame and the directory-
listed frame, MSG selects the RDD sample  of telephone numbers first. The sampled telephone
numbers are matched to the database of directory-listed telephone numbers. Those telephone numbers
identified as directory-listed  are removed from the directory-listed frame prior to the stratification
described above.

Trying to determine the percentage of the total  sample that should be allocated  to the RDD frame
based is difficult. First, the proportion of working residential telephones can vary considerably  from
county to county  so trying to estimate the total number of telephone households in this frame is
imprecise. Second, the estimation of the eligibility rate in this frame is imprecise. Since the contact

-------
                                                         CTEPP Recruitment Report - North Carolina
                                                                                   Page3

rate in this frame is substantially lower than any of the four directory-listed strata, the primary
determinant of our allocation is dialing efficiency.

Telephone subjects recruitment for four NC counties (Durham, Buncombe, Lee, and Mecklenburg)
began in July 2000 and completed in November 2000. The proj ect achieved 54% response rate (using
the response rate calculation method suggested by EPA) in Phase I recruitment and screened a total
of 244 potentially eligible households for the project. As of the end of December 2000, the  project
completed field sampling activities with 75% of the target participants (enrolled 48 of 64 target
subjects). Phase II telephone subjects recruitment for the two eastern NC counties (Edgecombe and
Jones) began in January 2001.  A total of 28  potentially eligible  subjects were identified. The
telephone subjects recruitment was completed on March 30,2001; a total of 67 subjects participated
in the study, which is 105% of the recruitment target.
IV     Summary

Table 1 provides detailed outcomes for telephone subjects recruitment.  A total of 12,262 phone
numbers were called. The project achieved 58% response rate. The method for calculating response
rates is also described in Table 1. Recruitment results for daycare centers and daycare parents are
provided in Tables 2 and 3. We used the same method suggested by EPA to calculate the response
rates. The project achieved 53% response rate for daycare centers and 50% response rate for daycare
parents.  The field  sampling activities were conducted in 23 weeks (Table 4).  The number of
participants in each county is summarized in Table 5. The participant's income status is summarized
in Table 6. The distribution of low and mid-to-high income among telephone (RDD) subjects is very
close to the original sampling plan. However, for daycare center subjects, low income subjects were
over enrolled, which was due to many of the subjects from the regular daycare centers being low
income subjects.

The  distribution of participants by NC counties is illustrated in Figure 1.   Figure 2  shows the
distribution of daycare center participants by urban and rural locations.  Figure 3  shows the
distribution of telephone (RDD) subjects by urban and rural locations.   Figure 4  shows the
distribution of daycare center participants by counties.  Figure 5 shows the distribution of RDD
telephone participants by counties.

V     References
CTEPP-SOP-1.10
CTEPP-SOP-1.11
CTEPP-SOP-1.12
CTEPP-SOP-1.13
Sample Selection Procedures
Daycare Center Sample Subjects Recruitment Procedures
Telephone Sample Subjects Recruitment Procedures
Informed Consent Procedures

-------
Table 1. CTEPP Call Ourcomes Report
CTEPP
Call Outcomes Report
3/30/2001
A. Agree to Participate/Eligible:
B. Ineligible subjects:
(1 ) not a private residence
(2) no children in the household
(3) cannot communicate
(4) no child in the age range
(5) not stay with child 3 consec days
(6) child attends a day care
(7) child is not potty-trained
(8) child is still being breast-fed
C. Refused Screening:
C1. Eligible subjects/Refused:
C2. Eligibility Unknown:
D. Non-Working Numbers:
E. Cannot be reached
Total Cases With Final Outcome:
Total Cases Loaded in CATI
Cases Still Active in CATI
Calculate Response Rates
A. Eligible and Completed
B. Total Eligible
C. Total Ineligible
D. Eligibility Unknown
E. Final Response Rate
Buncombe
15
643
95
386
15
105
1
30
11

143
3
140
245
62
1108
1108
0

15
18
643
202
64%
Mecklenburg
118
1882
352
669
83
341
11
348
68
10
526
29
497
693
613
3832
3832
0

118
147
1882
1110
52%
Durham
85
1480
153
585
95
257
11
325
52
2
369
18
351
721
489
3144
3144
0

85
103
1480
840
54%
Lee
26
642
62
312
22
143
5
77
21

174
8
166
218
128
1188
1188
0

26
34
642
294
53%
Edgecombe
18
970
67
516
25
233
5
106
18

83
1
82
297
122
1490
1490
0

18
19
970
204
79%
Jones
10
930
39
576
25
241
5
35
9

84
2
82
401
75
1500
1500
0

10
12
930
157
71%
Overall
Total
272
6547
768
3044
265
1320

921
179
12
1379
61
1318
2575
1489
12262
12262
0

272
333
6547
2807
58%
RR =
A
CJj


n x
j

-------
Table 2.  CTEPP Day Care Center Recruitment Results
CTEPP
ID
1
2
3
4
23
24
5
6
7
8
21
22
9
10
11
12
13
14
15
16
17
25
26
27
28
29
19
31
18
30
20
32
County
Durham
Durham
Durham
Durham
Durham
Durham
Buncombe
Buncombe
Buncombe
Buncombe
Buncombe
Buncombe
Lee
Lee
Mecklenburg
Mecklenburg
Mecklenburg
Mecklenburg
Mecklenburg
Mecklenburg
Mecklenburg
Mecklenburg
Mecklenburg
Mecklenburg
Mecklenburg
Mecklenburg
Edgecombe
Edgecombe
Edgecombe
Edgecombe
Jones
Jones
Day Care Centers
Head Start
Day Care Center
Day Care Center
Day Care Center
HEAD START
Day Care Center
Day Care Center
Day Care Center
HEAD START
Day Care Center
HEAD START
Day Care Center
Day Care Center
Day Care Center
HEAD START
Day Care Center
Day Care Center
Day Care Center
Day Care Center
Day Care Center
HEAD START
HEAD START
Day Care Center
Day Care Center
Day Care Center
Day Care Center
Day Care Center
Day Care Center
Day Care Center *
HEAD START
HEAD START
Day Care Center
Day Care Center
AGREE
13
1
1

1

1
1



1

1
1




1
1




1



1
1


REFUSED
4








1






1

1




1









-|\IU
CONTACT
10




1




1

1


1

1




1

1

1
1




1
INELIGIBLE
5


1




1












1






1


1

Total
32
































Calculate Response Rates
A. Eligible and Completed
B. Total Eligible
C. Total Ineligible
D. Eligibility Unknown
E. Final Response Rate
Summary
13
17
5
10
53%
                                                                                             RR
B
                                                                                                                     B+C
                                                                                                                                 X  D
                                                                                         Still dealing with flooding problems
                                                                                         Still dealing with flooding problems, Director agreed, but no parents.
" NO CONTACT = Cannot reach the day care director or the director cannot make a decision within the data collection period.

-------
Table 3.  CTEPP Day Care Parent Response Rate
Wk#
1
2
3
4
6
9
11
12
14
15
18
22
23





CTEPP
ID#
1
2
5
15
9
4
10
16
21
24
28
18
30





County
Durham
Durham
Buncombe
Mecklenburg
Lee
Durham
Lee
Mecklenburg
Buncombe
Durham
Mecklenburg
Edgecombe
Edgecombe




TOTAL
Sampling Date
Day-1
7/17/2000
7/24/2000
7/31/2000
8/7/2000
8/28/2000
10/2/2000
10/16/2000
10/23/2000
11/6/2000
11/13/2000
12/11/2000
3/19/2001
3/26/2001





iMumoer or
Parents
Attempted
10
17
16
19
15
16
14
14
9
10
14
14
14




182
Responded
Agreed
4
5
6
3
4
5
6
6
4
5
9
6
6




69
Responded
Refused
0
0
0
3
8
0
1
0
2
0
0
0
2




16
Responded
Ineligible
0
3
5
10
1
4
1
1
1
0
0
0
0




26
No Contact*
6
9
5
3
2
7
6
7
2
5
5
8
6




71
Total
10
17
16
19
15
16
14
14
9
10
14
14
14




182
* NO CONTACT = Cannot reach the selected parents or the parents cannot make a decision within the contact window.
Calculate Response Rates
A. Eligible and Completed
B. Total Eligible
C. Total Ineligible
D. Eligibility Unknown
E. Final Response Rate
Summary
69
85
26
71
50%
            RR
                                  A
                                  B+C
-]
                                            X  D

-------
Table 4. Field Data Collection Summary by Sampling Week
Field Data Collection
Summary by Sampling Week
Target
Week#


1
2
3
4
5
5
6
6
7
8
8
9
10
11
12
13
14
15

16
17
18
19
20
20
21
22
23
As of 3/30/2001
County
Durham
Durham
Buncombe
Mecklenburg
Buncombe
Lee
Lee
Durham
Durham
Mecklenburg
Durham
Durham
Mecklenburg
Lee
Mecklenburg
Durham
Buncombe
Durham
Holidays
Lee
Mecklenburg
Mecklenburg
Jones
Edgecombe
Durham
Durham
Edgecombe
Edgecombe
Date/Day-1
7/17/2000
7/24/2000
7/31/2000
8/7/2000
8/21/2000
8/21/2000
8/28/2000
8/30/2000
9/11/2000
9/18/2000
9/19/2000
10/2/2000
10/9/2000
10/16/2000
10/23/2000
10/30/2000
11/6/2000
11/13/2000
11/20/2000
11/27/2000
12/4/2000
12/11/2000
2/26/2001
3/5/2001
3/5/2001
3/12/2001
3/19/2001
3/26/2001
Data Collection Completed
Day Care
Participant
64
63
% of Target
98%
3
5
6
3


4




5

5
6

4
4



6




6
6
ROD
Participants
64
67
% of Target
105%




6
1

1
1
5
1

7


8
1
3

6
7
1
5
2
4
8


Total
128
130

102%
3
5
6
3
6
1
4
1
1
5
1
5
7
5
6
8
5
7

6
7
7
5
2
4
8
6
6
Remarks


*was 4, 1 last minute dropout


*was 4, 1 last minute dropout

























-------
Table 5. Field Data collection Summary by County
Field Data Collection
Summary by County


Week*
3
5
14

1
2
6
7
8
9
13
15
20
21

5
6
11
16

4
8
10
12
17
18

19


20
22
23


County
Buncombe
Buncombe
Buncombe
Subtotal
Durham
Durham
Durham
Durham
Durham
Durham
Durham
Durham
Durham
Durham
Subtotal
Lee
Lee
Lee
Lee
Subtotal
Mecklenburg
Mecklenburg
Mecklenburg
Mecklenburg
Mecklenburg
Mecklenburg
Subtotal
Jones
Jones
Subtotal
Edgecombe
Edgecombe
Edgecombe
Subtotal


Target
As of 3/30/2001
Date/Day-1
7/31/2000
8/21/2000
11/6/2000
Buncombe
7/17/2000
7/24/2000
8/30/2000
9/11/2000
9/19/2000
10/2/2000
10/30/2000
11/13/2000
3/5/2001
3/12/2001
Durham
8/21/2000
8/28/2000
10/16/2000
11/27/2000
Lee
8/7/2000
9/18/2000
10/9/2000
10/23/2000
12/4/2000
12/11/2000
Mecklenburg
2/26/2001

Jones
3/5/2001
3/19/2001
3/26/2001
Edgecombe
% of Target


































Data Collection Completed
Day Care
Participant
64
63
987o
6

4
10
3
5



5

4


17

4
5

9
3


6

6
15


0

6
6
12
ROD
Participants
64
67
1057o

6
1
7


1
1
1

8
3
4
8
26
1


6
7

5
7

7
1
20
5

5
2


2
Total
128
130
1U27o
6
6
5
17
3
5
1
1
1
5
8
7
4
8
43
1
4
5
6
16
3
5
7
6
7
7
35
5
0
5
2
6
6
14
Remarks





*was 4, 1 last minute dropout















*was 4, 1 last minute dropout









* Was 3, 1 did not show up.




-------
Table 6.  Summary of CTEPP NC Participants
Final NC Results
Urban
Rural


Buncombe
Durham
Mecklenburg
Edgecombe
Total Urban
Lee
Jones
Total Rural
Total NC
% of Total
Telephone Sample
Unknown


3

3

1
1
4
6%
Low-income
6
5
2
1
14
4
3
7
21
31%
Mid-income
1
21
15
1
38
3
1
4
42
63%
Subtotal
7
26
20
2
55
7
5
12
67
100%
Day Care Sample
Unknown


1
1
2
1

1
3
5%
Low-income
6
5
11
11
33
5
0
5
38
60%
Mid-income
4
12
3
0
19
3
0
3
22
35%
Subtotal
10
17
15
12
54
9
0
9
63
100%

Total
17
43
35
14
109
16
5
21
130


-------
                            Figure 1. NC Final Data Collection
Durham
          Mecklenburg
                      Buncombe
                                     Lee
                                              Edgecombe
                                                             Jones

-------
        Figure 2. CTEPP NC DayCare
14%
                                      86%
               DUrban • Rural

-------
             Figure 3. CTEPP NC ROD
18%
                                             82%
                  DUrban • Rural

-------
            Figure 4. CTEPP NC Day Care Centers
Edgecombe
   19%
Jones
 0%
                              Durham
                               27%
   Buncombe
     16%
                          Mecklenburg
                             24%
    DDurham • Mecklenburg DBuncombe DLee •Edgecombe DJones

-------
                                 Figure 5. CTEPP NC ROD
           Lee
           10%
                Edgecombe
                   3%
Buncombe
  10%
                                                                                Durham
                                                                                 40%
                            Mecklenburg
                               30%
                  DDurham • Mecklenburg DBuncombe DLee •Edgecombe  DJones

-------
                                                                CTEPP Recruitment Report - Ohio
                                                                                   Page 1
I.      Introduction

The research study, "Children's Total Exposure to PersistentPesticides and Other Persistent Organic
Pollutants," (CTEPP) is a pilot-scale project involving about 260 children, which investigates the
possible exposures that  young children may have to common contaminants in their everyday
surroundings. These contaminants include several pesticides, phenols, polychlorinated biphenyls,
polycyclic aromatic hydrocarbons, some of which are suspected of being endocrine disrupters. The
targeted compounds are persistent in the indoor and sometimes the outdoor environments, so that
very low levels may exist in the children's surrounding microenvironments and provide a source of
chronic, non-acute exposure.   The primary purposes  of the research are to  increase  our
understanding of children's exposures to persistent pollutants, to gain information on the various
activities,  environmental  media,  and pollutant  characteristics that may influence children's
exposures,  and to generate further questions and hypotheses for future research.
II.     Daycare Center Sample Subjects Recruitment

Detailed subjects recruitment procedures and sample selection methods are documented in CTEPP
SOP 1.10 and SOP1.11.  Ohio daycare subjects recruitment began in January 2001 and completed
in November 2001. The project enrolled 16 child care centers (12 regular daycare and 4 Head Start),
completed sampling activities with 58 households, and achieved 91% of the planned target (64). The
daycare center response rate is 58% and the daycare parents response rate is 31% (using the response
rate calculation method suggested by EPA).
III.    Telephone Sample Subjects Recruitment

The sample design utilized for the CTEPP telephone component is intended to fulfill the objectives
of:

   •   Efficiently identifying telephone households having one or more children in the eligible age
       range and meeting the sampling targets in the high and low income domains

   •   Providing coverage of households with unlisted telephone numbers

With respect to the first obj ective, the Marketing Systems Group (MSG) uses Census data, marketing
research data,  and other sources to classify  directory-listed households as having one or more
children in the age range of one to five years or no children in that age group. The same data is used
to assign the directory-listed households to an income range. While not all households classified as
having children in the target age range will indeed have eligible children, the eligibility rate will still
be much higher than a simple random sample of households.

-------
                                                               CTEPP Recruitment Report - Ohio
                                                                                   Page 2
The counts of directory-listed households having children in the target age group for the counties
provided by MSG are considerably less than the Census demographic estimates. A portion of the
eligible households in a study county will be in the group of households that MSG has classified as
having no children in the target age range, but the eligibility rate will still be very small. We must
allocate some percentage of our sample to this group of directory-listed households. To allocate a
greater proportion of our total sample to the first group of households we stratified the directory-
listed households.

 All directory-listed households in each of the six OH study counties were assigned to one of the 4
strata:

       1.  Directory-listed households with income above $25,000 and having one or more children
          in the target age range

       2.  Directory-listed households with income below or equal to $25,000 and having one or
          more children in the target age range

       3.  Directory-listed households with income above $25,000 and having no children in the
          target age range

       4.  Directory-listed households  with income below or equal to  $25,000 and having no
          children in the target age range

With respect to the second objective, some counties may have as many as 30% of households with
unlisted telephone numbers, therefore some of the eligible households in a study county will have
unlisted telephone numbers.  Trying to estimate the eligibility rate for households having unlisted
telephone numbers is difficult. We use a random digit dialing (RDD) approach to give these unlisted
telephone households some chance of selection.

To implement the RDD approach, MSG first identifies all telephone exchanges in the study county.
Telephone exchanges having very low percentages of directory-listed households in the study county
are deleted. From the remaining exchanges, MSG draws a systematic sample of telephone numbers.
Some of these telephone numbers are residential and some are business and nonworking. To prevent
a directory-listed telephone number from being sampled in both the RDD frame and the directory-
listed frame, MSG selects the RDD sample of telephone  numbers first. The sampled telephone
numbers are matched to the database of directory-listed telephone numbers. Those telephone numbers
identified as directory-listed are removed from the directory-listed frame prior to the stratification
described above.

-------
                                                                CTEPP Recruitment Report - Ohio
                                                                                    Page 3
Trying to determine the percentage of the total sample that should be allocated to the RDD frame
based is difficult. First, the proportion of working residential telephones can vary considerably from
county to county  so trying to estimate the total number of telephone households in this frame is
imprecise. Second, the estimation of the eligibility rate in this frame is imprecise. Since the contact
rate in this frame is substantially lower than any of the four directory-listed strata, the primary
determinant of our allocation is dialing efficiency.

Telephone subjects recruitment for OH counties began in March 2001 and completed in November
2001. The project achieved an overall 57% response rate (using the response rate calculation method
suggested by EPA) and screened a total of 165 potentially eligible households for the proj ect. A total
of 69 subjects participated in the study, which is 108% of the recruitment target (64).
IV     Summary

Table 1 provides detailed outcomes for telephone subjects recruitment. A total of 10,179 phone
numbers were called. The proj ect achieved an overall 57% response rate. The method for calculating
response rates is also described in Table 1. Recruitment results for daycare centers and daycare
parents are provided in Tables 2 and 3. We used the same method suggested by EPA to calculate the
response rates. The project achieved 57% response rate for daycare centers and 31% response rate
for  daycare parents.  The field sampling activities were conducted in 27 weeks (Table 4).  The
number of participants in each county is summarized in Table 5. The participant's income status is
summarized in Table 6.

The distribution of participants by  OH counties is illustrated in Figure 1. Figure 2 shows the
distribution of daycare  center participants by urban and  rural locations. Figure  3  shows  the
distribution of telephone (RDD)  subjects by urban  and rural  locations. Figure  4  shows  the
distribution of daycare center participants  by  counties.  Figure 5 shows the distribution of RDD
telephone participants by counties.

V     References
CTEPP-SOP-1.10
CTEPP-SOP-1.11
CTEPP-SOP-1.12
CTEPP-SOP-1.13
Sample Selection Procedures
Daycare Center Sample Subjects Recruitment Procedures
Telephone Sample Subjects Recruitment Procedures
Informed Consent Procedures

-------
Table 1. CTEPP Call Outcomes Report
CTEPP Ohio
Call Outcomes Report
11/30/2001
A. Agree to Participate/Eligible:
B. Ineligible subjects:
(1 ) not a private residence
(2) no children in the household
(3) cannot communicate
(4) no child in the age range
(5) not stay with child 3 consec days
(6) child attends a day care
(7) child is not potty-trained
(8) child is still being breast-fed
C. Refused Screening:
C1 . Eligible subjects/Refused:
C2. Eligibility Unknown:
D. Non-Working Numbers:
E. Cannot be reached
Total Cases With Final Outcome:
Total Cases Loaded in CATI
Cases Still Active in CATI
Calculate Response Rates
A. Eligible and Completed
B. Total Eligible
C. Total Ineligible
D. Eligibility Unknown
E. Final Response Rate
Cuyahoga
40
1022
78
583
15
266
1
57
21
1
90
6
84
551
517
2220
2220
0

40
46
1022
601
56%
Defiance
15
476
22
315
1
122
2
10
4

41
3
38
388
231
1151
1151
0

15
18
476
269
54%
Fayette
12
677
23
450
19
140
4
29
12

43
4
39
437
175
1344
1344
0

12
16
677
214
57%
Franklin
34
740
56
412
9
194
1
47
18
3
70
7
63
497
459
1800
1800
0

34
41
740
522
50%
Hamilton
44
1033
58
669

240
4
38
22
2
55
4
51
538
405
2075
2075
0

44
48
1033
456
64%
Licking
20
650
33
388
4
187

27
10
1
58
2
56
530
331
1589
1589
0

20
22
650
387
58%
Overall
Total
165
4598
270
2817
48
1149
12
208
87
7
357
26
331
2941
2118
10179
10179
0

165
191
4598
2449
57%
  RR =
                A
+
[-
                B+C
                      X D

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Table 2.  CTEPP Day Care Center Recruitment results
CTEPP
ID

Ohio
County
Day care Centers
Head Start
As of 11/30/2001

49
50
51
52
53
54
63
62
60
61
40
41
42
43
44
45
46
64
65
66
67
68
47
69
55
56
57
58
59
72
48
70
71
Franklin
Franklin
Franklin
Franklin
Franklin
Franklin
Franklin
Franklin
Licking
Licking
Cuyahoga
Cuyahoga
Cuyahoga
Cuyahoga
Cuyahoga
Cuyahoga
Cuyahoga
Cuyahoga
Cuyahoga
Cuyahoga
Cuyahoga
Cuyahoga
Defiance
Defiance
Hamilton
Hamilton
Hamilton
Hamilton
Hamilton
Hamilton
Fayette
Fayette
Fayette
Day Care Center
Day Care Center
Day Care Center
Day Care Center
Head Start
Head Start
Day Care Center
Day Care Center
Day Care Center
Head Start
Day Care Center
Day Care Center
Day Care Center
Day Care Center
Day Care Center
Head Start
Head Start
Day Care Center
Day Care Center
Day Care Center
Day Care Center
Day Care Center
Day Care Center
Day Care Center
Day Care Center
Day Care Center
Day Care Center
Head Start
Head Start
Head Start
Head Start
Day Care Center
Day Care Center
AGREE
16
67%


1
1


1
1

1

1


1
1
1
1

1



1
1
1



1

1

REFUSED
8
33%
1




1






1
1






1

1



1





1
*NO
CONTACT
5


1






1

1







1


1











INELIGIBLE
4





1






















1
1

1


Total
33


































* NO CONTACT = Cannot reach the daycare director or the director cannot make a decision within the data collection period.
Calculate Response Rates
A. Eligible and Completed
B. Total Eligible
C. Total Ineligible
D. Eligibility Unknown
E. Final Response Rate
Summary
16
24
4
5
57%
                                                                    RR =
                                                                                    A
                                                                             B
-]

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Table 3. CTEPP Day Care Parent Response Rate
Wk#
1
3
4
7
8
10
11
12
15
17
18
21
22
24
25
27


CTEPP
ID#
51
52
61
62
63
44
41
66
69
55
56
72
70
46
45
64


County
Franklin
Franklin
Licking
Franklin
Franklin
Cuyahoga
Cuyahoga
Cuyahoga
Defiance
Hamilton
Hamilton
Hamilton
Fayette
Cuyahoga
Cuyahoga
Cuyahoga

Total
Sampling
Date
Day-1
4/23/2001
5/7/2001
5/14/2001
6/4/2001
6/11/2001
6/25/2001
7/9/2001
7/16/2001
8/6/2001
8/20/2001
8/27/2001
9/24/2001
10/1/2001
10/15/2001
10/22/2001
11/5/2001


iMumDer or
Parents
Attempted
16
15
14
19
14
14
14
16
11
12
14
15
14
14
14
33

249
Responded
Agreed
5
6
5
7
6
6
2
4
4
3
3
4
4
4
4
4

71
Responded
Refused
1
0
0
0
0
0
5
2
1
3
1
4
0
2
5
5

29
Responded
Ineligible
0
0
0
0
3
0
0
0
0
2
0
0
1
0
0
2

8
No Contact*
10
9
9
12
5
8
7
10
6
4
10
7
9
8
5
22

141
Total
16
15
14
19
14
14
14
16
11
12
14
15
14
14
14
33

249
* NO CONTACT = Cannot reach the selected parents or the parents cannot make a decision within the contact window.
Calculate Response Rates
A. Eligible and Completed
B. Total Eligible
C. Total Ineligible
D. Eligibility Unknown
E. Final Response Rate
Summary
71
100
8
141
31%
        RR
                     A
               B
                      B
-].n

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Table 4. Field Data Collection Summary by Sampling Week
Field Data Collection
Summary by Sampling Week
Target
Week#


1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
26
27
As of 11/30/2001
County
Franklin
Franklin
Franklin
Licking
Franklin
Franklin
Franklin
Franklin
Licking
Cuyahoga
Cuyahoga
Cuyahoga
Cuyahoga
Cuyahoga
Defiance
Defiance
Hamilton
Hamilton
Hamilton
Hamilton
Hamilton
Fayette
Fayette
Cuyahoga
Cuyahoga
Franklin
Cuyahoga
Date/Day-1
4/23/2001
4/30/2001
5/7/2001
5/14/2001
5/21/2001
5/28/2001
6/4/2001
6/11/2001
6/18/2001
1/0/1900
7/9/2001
7/16/2001
7/23/2001
7/30/2001
8/6/2001
8/13/2001
8/20/2001
8/27/2001
9/10/2001
9/17/2001
9/24/2001
10/1/2001
10/8/2001
10/15/2001
10/22/2001
10/29/2001
11/5/2001
Data Collection Completed
Daycare
Participant
64
58
% of Target
91%
4

4
4


4
4

4
2
4


4

3
3


4
4

4
3

3
ROD
Participants
64
69
% of Target
108%

7
1

7
1


7



8
8

6

1
8
8


3


4

Total
128
127

99%
4
7
5
4
7
1
4
4
7
4
2
4
8
8
4
6
3
4
8
8
4
4
3
4
3
4
3
Remarks






























-------
Table 5. Field Data Collection by County
Field Data Collection
Summary by County

As of 11/30/2001
Week*
1
2
3
5
6
7
8
26

4
9

10
11
12
13
14
24
25
27

15
16

17
18
19
20
21

22
23

County
Franklin
Franklin
Franklin
Franklin
Franklin
Franklin
Franklin
Franklin
Subtotal
Licking
Licking
Subtotal
Cuyahoga
Cuyahoga
Cuyahoga
Cuyahoga
Cuyahoga
Cuyahoga
Cuyahoga
Cuyahoga
Subtotal
Defiance
Defiance
Subtotal
Hamilton
Hamilton
Hamilton
Hamilton
Hamilton
Subtotal
Fayette
Fayette
Subtotal
Target
Actual Total
Date/Day-1
4/23/2001
4/30/2001
5/7/2001
5/21/2001
5/28/2001
6/4/2001
6/11/2001
10/29/2001
Franklin
5/14/2001
6/18/2001
Licking
6/25/2001
7/9/2001
7/16/2001
7/23/2001
7/30/2001
10/15/2001
10/22/2001
11/5/2001
Cuyahoga
8/6/2001
8/13/2001
Defiance
8/20/2001
8/27/2001
9/10/2001
9/17/2001
9/24/2001
Hamilton
10/1/2001
10/8/2001
Fayette
Data Collection Completed
Daycare
Participant
64
58

4

4


4
4

16
4

4
4
2
4


4
3
3
20
4

4
3
3


4
10
4

4
ROD
Participants
64
69


7
1
7
1


4
20

7
7



8
8



16

6
6

1
8
8

17

3
3
Total
128
127

4
7
5
7
1
4
4
4
36
4
7
11
4
2
4
8
8



36
4
6
10
3
4
8
8
4
27
4
3
7
Remarks


































-------
Table 6.  Summary of CTEPP OH Participants
Final OH Results
Urban
Rural


Cuyahoga
Licking
Franklin
Hamilton
Total Urban
Defiance
Fayette
Total Rural
Total OH
% of Total
Telephone Sample
Unknown
1



1


0
1
1%
Low-income
4

7
2
13
2
3
5
18
26%
Mid-income
11
7
13
15
46
4

4
50
72%
Subtotal
16
7
20
17
60
6
3
9
69
100%
Daycare Sample
Unknown


2
1
3
2

2
5
9%
Low-income
10
4
6
9
29


0
29
50%
Mid-income
10

8
0
18
2
4
6
24
41%
Subtotal
20
4
16
10
50
4
4
8
58
100%

Total
36
11
36
27
110
10
7
17
127


-------
                               Figure 1. OH Final Data Collection
Cuyahoga
              Licking
                          Franklin
                                      Hamilton
                                                    Defiance
                                                                  Fayette

-------
        Figure 2. CTEPP OH Daycare
14%
                                      86%
              DUrban • Rural

-------
        Figure 3. CTEPP OH ROD
13%
                                   87%
             DUrban • Rural

-------
                              Figure 4. CTEPP OH Daycare Centers
Hamilton
  17%
                Defiance
                  7%
Fayette
  7%
                             Franklin
                              28%
                                                                                      Cuyahoga
                                                                                        34%
                                                                              Licking
                                                                               7%
                      DCuyahoga • Licking DFranklin DHamilton •Defiance DFayette

-------
                                     Figure 5. CTEPP OH ROD
                    Defiance
                      9%
Fayette
  4%
                                      Cuyahoga
                                        23%
Hamilton
  25%
                                                    Licking
                                                     10%
                                                     Franklin
                                                       29%
                      DCuyahoga • Licking DFranklin DHamilton •Defiance DFayette

-------
                                   Appendix C







Summary of Analytical Methods for Determining Target Pollutants in Multimedia Samples
                                       C-l

-------
  Flow Chart of Analytical Methods for Neutral Analytes in PUF, Air, Wipes,
                Dust, Soil, Liquid Food, and Liquid Food
    Analytical Methods for Neutrals
                                                   Liquid/Solid Food
                    Air, Wipes
                                                     ASE with DCM or

                                                    Reflux with 39%KOH
 Soxhlet Extraction
With 10% EE/hexane
Soxhlet Extraction
  With DCM
Sonication with
10 % EE/hexane
                                                      Concentrate
                                                     DCM Extract
                   Concentrate
                 Extract using KD
                                                      Fractionate
                                                     DCM Extract
                                                      Using GPC
                     Flonsil
                      SPE
Concentrate SPE
 Fraction Using
     KD
                                                      Concentrate
                                                     GPC Fraction
                               C-2

-------
  Flow Chart of Analytical Methods for Atrazine in Drinking Water

Analytical Method for Atrazine in
             Drinking Water
              Condition CIS SPE Column with
             DCM, MEOH. And Distilled Water
              Apply lOOmL Water Sample to
                 Conditioned CIS SPE
               Dilute Cartridge with 12mLof
                   50% DCM/hexane
               Concentrate Fraction; Add IS
                      GC/MS
                       C-3

-------
Flow Chart of Analytical Methods for Acidic Analytes in Air, Dust, Soil,
            Wipe, Liquid Food, and Solid Food
   Analytical Methods for Acids
Liquid and
Solid Food
ASEwithMEOH

Dust, Soil
ASE
With acetone

Air, Wipes
Soxhlet Extraction
With ACN







Concentrate MEOH Extract
Adjust PH to < 12 with Hexane
1
i 1
Acidify Aqueous Discard
Layer to PH < 2 Hexane


^ Split Extract*
Concentrate r
* Extract; Add IS l Iucm3lanon
» II - Silylation



Yes ^^SPE^r No
Fraction Using 1 GC/MS |
KD
1 '
                                GC/MS
                      C-4

-------
Flow Chart of Analytical Methods for 3,5,6-TCP, 2,4-D, PCP, and OH-PAH in Urine
          Analytical Method for 3,5,6-TCP in
                               Urine
                         Hydrolyze ImLUrine with HC1;
                           Heat at 80°C for 1 Hour
                        Add20%NaCl, Chlorobutane (CB)
                               and IS; mix
                         Centrifuge Sample; Transfer CB
                        Extract to Clean Vial; Add Na2SO4
                         Remove CB Extract; Silylate the
                           Extract with MTBSTFA
                                 GC/MS
                    ical Method for 2,4-D, PCP
                      OH-PAH in Urine
                     Hydrolyze 10 mL Urine with HC1 and DCM
                           Heat at 80°C for 1 Hour
                              Add 20% NaCl;
                             Extract with DCM
                          Concentrate DCM Extract;
                             Add IS and MEOH
                          Methylate DCM Extract with
                              Diazomethane
                               Florisil SPE;
                       Concentrate SPE Fraction Using KD
                                GC/MS
                                   C-5

-------

-------
                               Appendix D
Quality Assurance/Quality Control Summary for CTEPP North Carolina and Ohio
                             Data Collection

-------

-------
CTEPP NC Data Collection QA/QC Report                                02/17/2004
QA/QC Summary Report for CTEPP North Carolina Data Collection
I.      Introduction

The  research  study, "Children's  Total  Exposure  to  Persistent  Pesticides and  Other
Persistent Organic Pollutants," (CTEPP) is a pilot-scale project involving about 260
children, which  investigates the possible exposures that young  children may have to
common contaminants in their everyday  surroundings.  These contaminants include
several pesticides, phenols, polychlorinated biphenyls, polycyclic aromatic hydrocarbons,
some of which are suspected of being endocrine disrupters. The targeted compounds are
persistent in the indoor and sometimes the outdoor environments,  so that very low levels
may exist in the children's surrounding microenvironments  and provide a source of
chronic, non-acute exposure.  The primary  purposes of the research are to increase our
understanding of children's exposures to persistent pollutants,  to gain information on the
various activities, environmental media, and pollutant characteristics that may  influence
children's exposures,   and  to generate further  questions and  hypotheses for  future
research. This document provides  a summary of the quality assurance (QA) and quality
control (QC) procedures conducted for the CTEPP project. In the  following sections, we
describe the study activities and the QA/QC procedures. The relevant standard  operating
procedures (SOPs) are listed in the Reference Section at the end of this document.

II.     CTEPP Study Activities

As illustrated in Exhibit 1 (CTEPP Study Activities Flow Chart), CTEPP study activities
are conducted in three phases: Pre-Data Collection,  Field Data Collection, and Post-Data
Collection. To ensure data quality, standard operating procedures (SOPs) were developed
and project team members were trained according to the SOPs. All project activities were
conducted by trained project staff members, who were divided into the following project
teams:  1) recruitment team (including RDD and field teams), 2) field support team,  and
3) field data collection team.

The recruitment team was responsible for recruiting daycare and RDD home participants.
It was  supported by a team of telephone  interviewers and some field staff members.
During the pre-data collection phase,  the following  key activities were conducted by the
recruitment team and field support team.

   a  Recruit/Train Participants, Present T-shirts, Pay $25, Remind Food Samples
       Collection
   a  Label Sample Containers
   a  Compile Field Notebooks
   a  Pack Van, Check items  on the  check lists

The field support team conducted  QA/QC checks before and  after the preparation of all
field supplies, sample  containers, and data forms.  They  ensured that  all the  materials
needed for the field data collection activities were complete and accurate.
C:\MYDATA FILE\CTEPPFinalReport91604\CTEPP QA_QCReportNC.doc

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CTEPP NC Data Collection QA/QC Report                              02/17/2004
After the field support team completed the preparation work, the field data collection
team did a final check on all needed field supplies, sample containers, and data forms for
the scheduled  sampling appointments. After loading the van and completing the final
checks,  the  field data collection team drove to the  sampling site for the scheduled
sampling appointment with the  study  subject. The following key  activities were
conducted by the field data collection team during the field data collection phase.

    a Field Data Collection Activities
    a Record Sample/Data Condition on Sample/Data Check Lists
    a Put Samples in ZipLoc Bags
    a Put Samples in Freezers
    a Record problems/issues on Daily Check List
    a Leave Field Notebooks in the CTEPP Workroom

Once the field  data collection team returned to the Battelle office, the field support team
received the field samples and data from the field data collection team. The following key
activities were  conducted by the field support team during the post-data collection phase.

    a Update Sample/Data Check Lists in the CTEPP  Tracking System (TS)
    a Verify Sample Conditions
    a Check Field Notebooks (data forms)
    a File Field Notebooks in the participant folders
    a Ship Samples
    a Conduct Data Entry
    a Update Progress Reports
    a Update QC Reports

In the following Sections, we describe specific QA/QC  procedures relevant to the CTEPP
data forms and database preparation.

III.   CTEPP QA/QC Procedures for Preparing the Data Forms and Database

Battelle  is  always committed  to the production of  highest quality  data.  A key  to
accomplish this objective is to implement standardized QA/QC procedures. QA/QC is a
continuous process.  As illustrated in Exhibit 2 (CTEPP QA/QC Procedures for Preparing
Data Forms and Database), Battelle implemented a comprehensive QA/QC plan to ensure
data quality in all phases of the CTEPP project, from pre-data collection to post-data
collection phase.

A.    Pre-Data Collection Phase:

Developed and Tested Data Forms, CA TI Programs
During the pre-data collection phase, the following data forms were developed.

•   Recruitment Survey  (Form #1)
C:\MYDATA FILE\CTEPPFinalReport91604\CTEPP QA_QCReportNC.doc

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CTEPP NC Data Collection QA/QC Report                               02/17/2004


•  House/Building Characteristics Observation Survey - Home (Form #2)
•  House/Building Characteristics Observation Survey - Child Day Care Center (Form
   #3)
•  Pre-Monitoring Questionnaire - Parent (Form #4)
•  Pre-Monitoring Questionnaire - Child Day Care Center (Form #5)
•  Post-Monitoring Questionnaire - Parent (Form #6)
•  Post-Monitoring Questionnaire - Child Day Care Center (Form #7)
•  Child Activity Diary/Parent - Children Don't Attend Day Care (Form #8)
•  Child Activity Diary/Parent - Children Attend Day Care (Form #9)
•  Child Activity Diary - Day Care Teacher (Form #10)

All the data forms were tested by trained project staff for consistency and accuracy. In
addition, mock interviews and field  data  collection  simulations were  conducted to
evaluate the effectiveness of the data forms.  The data forms were finally reviewed and
approved by 1KB and OMB. Form #1 (Recruitment Survey) was modified into computer-
assisted telephone interviewing programs (CATI) for  recruiting the RDD participants
(children who did not attend daycares). The CATI programs automatically performed QC
checks during data  entry, which included range checks, consistency checks,  and skip
pattern checks. Before the CATI programs  were approved for actual RDD recruitment
and data collection, it also went through rigid QA/QC checks for programming errors.
Exhibit 3 provides an example of the QA/QC test document.

Conducted Staff Training on Data Collection SOPs
To ensure the consistency and high quality of data collection,  a comprehensive training
plan  was implemented.  The recruitment  team  members  received  training in the
implementation of the recruitment  SOPs before  subject recruitment activities began.
Standardized scripts and materials (e.g., CATI system and Interviewer's Manual) were
developed. The Interviewer's Manual provided information on the background  and aims
of this study, the standard interviewing  procedures,  confidentiality  requirements, and
question-by-question specifications for the  recruitment survey.  Interviewers  must be
certified for the study before they can  initiate any contact with the  study subjects.  In
order to be certified as a CATI interviewer for the study, an interviewer must pass the
following two tests:

       1.  CATI Operation Test:     The interviewer must demonstrate that he/she is
                                  familiar with the CATI instrument and the
                                  computer-working environment.
       2.  CATI Interview Test:     The interviewer must conduct at least two mock
                                  CATI interviews and receive a satisfactory
                                  evaluation from the CATI supervisor.

Training  for the  field data collection team  members included  a  five-day (40-hour)
training session and additional self-practice time  was provided to the field staff. The
following is  a brief summary of the training topics.
C:\MYDATA FILE\CTEPPFinalReport91604\CTEPP QA_QCReportNC.doc

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CTEPP NC Data Collection QA/QC Report                                02/17/2004


       Day 1:        Training covered study background, recruitment SOPs,
                     confidentiality issues, informed consent procedures, and the
                     interviewing protocol.

       Day 2:        The field staff members were trained to administer all the data
                     collection forms.

       Day 3:        The training included field sampling procedures, i.e., the use of
                     field notebooks and the collection of air, food, urine, dermal hand
                     wipes, hard floor wipes, food preparation surface wipes, the
                     polyurethane foam (PUF) roller for dislodgeable residues, indoor
                     floor dust, and soil samples. Internal field audits and QC
                     procedures were also discussed.

       Days 4/5:      A mock field sampling exercise (with 2 volunteers) was conducted
                     during the last two days of training. The field team visited the
                     volunteer's  home and conduct actual  field sampling activities. The
                     field staff members were also certified during these two days (i.e.,
                     they were required to pass the tests set for the field sampling
                     procedures).

       Day 5:        Training in  packing and shipping procedures were given on the
                     final day. The training ended with a final review of all SOPs.

Before field data collection began, the field  support team members also went through
training for data form tracking and processing procedures, coding procedures, and quality
control procedures.

Conducted Participant Orientation/Training
Due to the unique features of the  CTEPP study, some key information and samples were
collected by the study participants  themselves.  Keeping the participants involved  and
well informed was critical to the  success of the study. All participants  (i.e.,  parents  and
daycare staff) were  trained (i.e., received project orientation)  prior to the scheduled
sampling  appointment (normally one  week  before the actual  sampling).  During  the
orientation/training, our project staff went through the  SOPs for collecting samples of
food,  urine, and dermal hand wipes and recording the Child  Activity Diary with the
participants.

B.     Data Collection Phase:

Conducted CATI Monitoring
As a standard procedure to ensure data quality, Battelle routinely verifies data collection
activities.  For  monitoring CATI interviews  (Form  #1 RDD), Battelle employed  a
sophisticated computer  software  (i.e., PROXY) and a telephone monitoring system to
validate CATI interview data. With the monitoring system,  the CATI  supervisor could
actually "watch" and "listen" an  interview in progress.  A  standardized  monitoring
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CTEPP NC Data Collection QA/QC Report                               02/17/2004


procedure  was developed  and used  for CATI monitoring.  The  supervisor randomly
selected an interview for monitoring. The monitoring system transferred the interviewer's
computer screen and telephone conversation in real time to the supervisor's workstation.
The interviewer being monitored or the study respondent could not notice any difference
while the monitoring was in progress.  To ensure the participant's right, a statement about
the interview that might be monitored by a project supervisor for quality assurance was
read to the respondent before the interview began. The monitoring results were recorded
in a CATI Interview Monitoring Form (See Exhibit 4).

Conducted Staff Field Edit
All field data collection team  members were trained to  conduct  field edit for  all
completed  data forms.  During data collection, the field staff conducted field edits to
identify  missing  data  items  or questionable information at the sampling  site.  Any
identified issues or problems were resolved at the sampling site  before the field data
collection team returned to Battelle whenever the  field conditions allowed.  A  Daily
Activity  Check List was developed to assist the field staff in conducting data collection
activities and field  edit.  The field edits ensured  that  any data collection issues  or
problems were resolved early at the sampling site with the study participant.

Conducted Internal Field Audits
According  to  CTEPP SOP 2.25, Battelle conducted  periodical internal field audits to
ensure high quality of data collection. The  internal field audits were conducted by the
Field Team Leader and/or field auditors. The field data collection team was not notified
of the field audit  visit. The field audit schedule was  randomly selected by the  field
auditor/Field Team Leader. During a field audit visit, the field auditor observed all field
sampling activities according to the SOPs.  The field auditor recorded  any findings or
observations about the field staffs work that was not consistent with the SOPs. Before
the end of each field audit visit, the field auditor  discussed the findings or observations
with the  field staff. A field audit report was prepared by the field auditor after each field
audit to document the field audit visit.

Conducted External Field Audits
In addition to Battelle internal field audits, some external field audits were conducted by
EPA auditor and project officer. On September 12 and 13, 2000, EPA audited the North
Carolina data collection teams. On June 5,  2001, EPA project officer  conducted  field
observation visit with the Ohio data  collection teams. There was  no finding in all the
external field audits and observation visits.

C.     Post-Data Collection Phase:

Applied Chain of Custody Procedures
In order to protect the  study  samples and data forms, a standardized chain-of-custody
procedure was developed and implemented for the CTEPP  study (See SOP 2.26). In
addition, Battelle  developed a sophisticated CTEPP  Tracking System to monitor the
status of data collection. As soon as the field team returned to the office, the field support
(receiving) team checked the samples/data  condition and updated the data collection
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CTEPP NC Data Collection QA/QC Report                               02/17/2004


status in the CTEPP Tracking System (See Exhibit 5). The following information was
recorded for each study participant.

          •   Sample/Data Description
          •   Sample Type
          •   Sample ID#
          •   Staff s Name Who Collected the Sample/Data
          •   Date of Collection
          •   Sample Condition
          •   Number of Floor Dust Sampling Areas
          •   Sample Explanation (if Sample Condition = Explain)
          •   Staff s Name Who Received the Sample/Data from the Field Team
          •   Date Received Sample/Data
          •   Time Received Sample/Data

If the samples/data need to be shipped to another location, the CTEPP Tracking System
automatically generates a Chain-of-Custody record for the staff to sign.

Receiving Team Conducted QC Checks
After checking and storing the environmental and biological samples, the receiving team
conducted QC checks on all the participant's data forms and study materials. A CTEPP
Participant Data QC Check List was developed to track the QC status of each data item
(See Exhibit 6). The staff carefully reviewed each data form for missing or questionable
data items. After the staff completed the QC review, she/he put her/his initial and date of
review on the back of the data form. Any pending issues  (e.g., missing materials or
information) identified through the QC review were recorded in the  Check Notes of the
CTEPP Participant Data QC Check List. The field support staff resolved each pending
issue by checking with the field data collection staffer contacting the participant.

Developed and Tested Data Entry Programs
After the data forms went through the QC  checks and received a "complete" status, the
form was ready for data entry. Battelle programming team developed a double data entry
program to allow two separate data entry  teams to conduct data entry.  The data entry
program was  designed  to  perform additional QC checks during  data entry,  which
included range checks, consistency checks,  and skip pattern checks. Before the data entry
program was  used for actual data entry, it was fully tested by trained project staff. An
example of the testing document is illustrated in Exhibit 7 (CTEPP Data Entry Program
Test). Examples of data entry program screens are illustrated in Exhibits 8, 9, and 10.

Conducted Double-Data Entry
All data forms were entered twice and verified, using the CTEPP  Double Data Entry
Program.  Two data entry teams (Teams A and B) performed the data entry work and
entered the data into  two separate databases. All the data  entry team  members were
trained before they were allowed to conduct data entry work. Each staff was assigned to
only one data entry  team and was not allowed to switch team. This  ensured that a data
form was entered twice by 2 different people. As a standard procedure for entering the
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CTEPP NC Data Collection QA/QC Report                               02/17/2004


open text fields, the data entry teams were instructed to entered participant's responses
verbatim.

Conducted Computer Program Checks for Data Entry Errors
A computer verification program was developed for checking the accuracy of the entered
data and every  record in  the two databases was  crosschecked.  An  example of the
crosschecks computer  reports is illustrated in Exhibit  11  (CTEPP Double Data Entry
Crosschecks). The crosscheck computer reports identified any discrepancies between the
two databases. The reports displayed the Participant ID (PID), variable (data field) name,
data value in each database (Base vs. Compare), the difference between the 2 databases
(numeric fields only), and % difference (if applicable).

Correct Data Entry Errors
For each data item detected by the computer program, the data entry  staff verified the
information with the original  participant data form and made corrections as needed. The
crosscheck computer reports made it easy for the staff to identify data entry problems and
to verify the information. This program also kept a log of all changes  made, including
original data value, date/time of data change, and name  of the  staff who made the
changes.

Prepare Final Master Database
A final master database  for  each data form was  prepared after all QC  checks  were
completed  and data entry  discrepancies were corrected. Backup  data files were also
created to protect the CTEPP data. All CTEPP data files and document  are protected by
password. Only  authorized project staff members have access to the restricted project
folders.

Prepare and Verify Data Dictionary and Document
After the completion of master database preparation, the programming team prepared the
updated data  dictionary for each data form database. The project staff verified the data
dictionaries by comparing the hard copy manuals, the electronic files,  and the  database
structures.

Final Data Verification Checks
After completing all the tasks described in the earlier sections, the project staff conducted
a final  QA/QC check by verifying randomly selected participant files. Data items in the
database  were checked against the data documentation manual (i.e., data variables in the
data dictionary) and the actual participant data in the original data form. The results of the
random checks showed 100% accuracy. The  data in the original participant data form
were correctly recorded in the CTEPP database, and the data variables were accurately
documented in the data dictionary.  Before Battelle delivered the database to EPA, the
data variables containing personal identifiers (i.e., names, street address, GPS, etc.) were
removed from the database to ensure participant confidentiality. The results of the final
data verification checks are  shown in the following Table.
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CTEPP NC Data Collection QA/QC Report
02/17/2004
                 Final Data Verification Checks for NC Database
PID
15-001-1
21-000-3
97-109-1
09-003-1
97-079-1
18-000-3
Data Forms Checked
1, 2, 4, 6, 9
3,5,7,10
8, Air Data Log
1,2, 4, 6, 9, Air Data Log
2, 4, 6, 8, Air Data Log
3, 5, 7, 10, Air Data Log
QA/QC Checks Status
Complete Checks:
Checked all variables of
each data form
Complete Checks:
Checked all variables of
each data form
Complete Checks:
Checked all variables of
each data form
Partial Checks: Checked
some randomly selected
variables of each data form
Partial Checks: Checked
some randomly selected
variables of each data form
Partial Checks: Checked
some randomly selected
variables of each data form
Results
No problem
No problem
No problem
No problem
No problem
No problem
IV.    CTEPP QA/QC Procedures for the Analytical Database

Analytical data were electronically imported into the database according to CTEPP SOP
4.12.  The analytical raw data (QUAN report) were generated from each instrument by a
qualified analyst (the first data reviewer). The QUAN report was then reviewed by the
TOL (the second data reviewer) for all the identified analytes.  The QUAN report was
then electronically transferred into a custom report and saved as a "crd" file.  The "crd"
file was then electronically parsed into an Excel spreadsheet template, pertinent data such
as sample extraction weight and quality assurance codes were added and saved as an
Excel file with an extension of ".xls" by the first data reviewer. The TOL reviewed all
the Excel files before importing into the analytical database. If any anomalous results
were observed in the data, every effort was made to identify any problems in the sample
collection, sample preparation,  and/or analysis, which could have contributed to the
anomaly. Data dictionaries and code sets for core analytical data, QA/QC data, and
ancillary data were developed for the analytical  database.  The completed Excel
spreadsheets were then electronically imported into the analytical database by the
database staff.

Database queries were developed to perform QA/QC  checks. The QA/QC checks
performed for the Ohio analytical database include (1) sample ID checks, (2) missing
data checks, (3) duplication data checks, (4) out-of-range checks, (5) upper- and lower-
concentrations checks, and (6) calculation checks.
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CTEPP NC Data Collection QA/QC Report                               02/17/2004
Sample ID checks
The sample ID checks were performed to verify that all Sample IDs with reported data
were valid Sample IDs, i.e., they were logged in as received from the field. If invalid
sample IDs were detected, the database staff traced back to the original raw data,
including laboratory record books and GC/MS logbooks, to identify the transcription
error and to make the corrections accordingly. All corrections were documented in the
database importing logbook.

Missing data checks
The missing data checks were performed to verify that all Sample IDs received from the
field had a full set of analytical data reported.  Samples that were received but that did not
have a complete set of analytical data and/or ancillary data, other than for a stated reason
in the electronic CoC data, were identified, and one of the following correction actions
was taken (as appropriate): analytical data was found and imported into the database, or
samples were located, processed, analyzed, reviewed, and the analytical data was
imported into the database.  Samples that were lost or damaged during laboratory
processing were identified and imported into the QA  Action table with an explanation
regarding their disqualification.

Duplicate data checks
Duplicate data checks were performed to verify that the same analytical data was not
imported into the database twice for a given sample.  The database staff traced the sample
results back to the laboratory record books, the GC/MS sequence logs, and/or the QUAN
reports to confirm that duplicate data was the result of a double import, and not a QA/QC
re-analysis (e.g. duplicate sample or duplicate injection). Once the duplicate data was
identified as a double import, the set of results for the sample having the oldest sample
import date were eliminated from the analytical database. If the duplicate  data was
identified as a QA/QC re-analysis, the proper QCC code was added to the QC_Code data
field, and the data for the first duplicate (only) remained in the Core_Analytical_Results
table, and the data for the first and second  duplicates  were reported in the
QA_QC_Results table.

Out of range checks
Out-of-range checks were performed to verify that all data for data fields limited to a
codeset did not violate that codeset.  For data fields that were limited to a codeset of
values, queries were performed to identify data within those fields that did not belong to,
or "violated", the codeset. Once identified, the database staff traced the sample results
back to the laboratory record books to identify the transcription error.  The data in the
database was corrected, and that correction was documented.

Upper- and lower- concentration checks
Upper- and lower-level concentrations checks were performed on approximately 5% of
the results that were plus or minus three standard deviations from the mean.  Database
queries were performed to identify those calculated results (Resultl and Result2) greater
than or less than three standard deviations  from the domain mean. Five percent of these
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CTEPP NC Data Collection QA/QC Report                                02/17/2004


data were reviewed again by the data reviewer. The data reviewer checked the QUAN
report, all the parameters used for the results calculation, and the result calculation itself
to make sure that identification and quantification were performed correctly.  If the data
reviewers detected any mis-identification and/or mis-quantification, corrections were
made accordingly. The TOL approved the corrected data and the database manager made
the changes in the database.  All activities were documented in the laboratory record
books and database importing logbook.

Several additional checks were performed to:

       (1) review the SRS and MSS recoveries data greater than 150% and less than
       50%;
       (2) review the %D data that are greater than 50%;
       (3) add more flag codes to explain these QC data from items 1 and 2;
       (4) review all nonzero method blanks and field method blanks; and

Calculation Checks
Calculation checks were performed in  Excel spreadsheets for selected samples to verify
that the calculations performed on Excel spreadsheet agreed with the calculations
performed on the analytical database.  Hand calculations, using a calculator, were
performed on select data to verify the calculated data agreed with the database calculated
data.

For those data requiring calculation of results,  a random subset (approximately 5%) of the
raw data was calculated using an independent calculation source (Excel) for validation.
In addition, hand calculations were performed on random data for each sample matrix
using a calculator.
C:\MYDATAFILE\CTEPPFinalReport91604\CTEPPQA_QCReportNC.doc

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CTEPP NC Data Collection QA/QC Report
                                                           02/17/2004
References:
CTEPP-
CTEPP-
CTEPP-
CTEPP-
CTEPP-
CTEPP-
CTEPP-
SOP-2.22
SOP-2.24
SOP-2.25
SOP-2.26
SOP-2.27
SOP-4.10
SOP-4.12
Procedures for Recording Data Collection Forms
Procedures for Handling Missing Samples/Data
Internal Field Audit/Quality Control Procedures
Sample/Data Custody Procedures
Staff and Participant Training
Procedures for Processing Completed Data Forms
Entering or Importing Electronic Data Into CTEPP Data Bases
Procedures
Attachments:

Exhibit 1
Exhibit 2
Exhibit 3
Exhibit 4
Exhibit 5
Exhibit 6
Exhibit 7
Exhibit 8
Exhibit 9
Exhibit 10
Exhibit 11
      CTEPP Study Activities Flow Chart
      CTEPP QA/QC Procedures for Preparing Data Forms and Database
      ROD CATI Tests Document
      CATI Interview Monitoring Form
      CTEPP Tracking System
      CTEPP Participant Data QC Check List
      CTEPP Data Entry Program Test
      CTEPP Double Data Entry Program - Initial Screen
      CTEPP Double Data Entry Program - Data Entry Screen
      CTEPP Double Data Entry Program - Status Screen
      CTEPP Double Data Entry Crosschecks
C:\MYDATA FILE\CTEPPFinalReport91604\CTEPP QA_QCReportNC.doc
                                                                          11

-------
 o

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 w
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Field Data
Collection


a Field Data Collection
a Record Sample/Data Condi
on Sample/Data Check List
Q Put Samples in ZipLoc Bag
Q Put Samples in Freezers
Q Record problems/issues on
Daily Check List
a Leave Field Notebooks in t
CTEPP Workroom
^


CTEPP Field Data
Collection Team
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Exhibit 2. CTEPP QA/QC Procedures for Preparing Data Forms and Database
Pre-Data Collection
Phase
 •   Developed and Tested Data Forms, CATI
    Programs
 •   Conducted Staff Training on Data Collection
    SOPs
 •   Conducted Participant Orientation/Training
Data Collection Phase
•  Conducted CATI Monitoring
•  Conducted Staff Field Edit
•  Conducted Internal Field Audits
•  Conducted External Field Audits
Post-Data Collection
Phase
    Applied Chain of Custody Procedures
    Receiving Team Conducted QC Checks
    Developed and Tested Data Entry Programs
    Conducted Double-Data Entry
    Conducted Computer Program Checks for
    Data Entry Errors
    Correct Data Entry Errors
    Prepare Final Master Database
    Prepare and Verify Data Dictionary and
    Document
    Final Data Verification Checks

-------
                          Exhibit 3. KDD CATI Tests Document
                                   RDD CATI Tests
                                     Carey Aselage
                                   December 8, 1999

  1.     Add the following interviewer instructions to this question:  May I speak to the
        parent or guardian of the children in this household (OR NAME OF
        RESPONDENT IF OBTAINED THE NAME FROM PREVIOUS CALL)?-fixed
        EB 12/99

  2.     Skip pattern for answer #1 goes to Q3.  However, this question is numbered as Q2 in CATI. I
        combined question 2 and 3 into 1 question and called it Q2_3. Since it is really the same question
        with a little different wording depending on whether the parent answered the phone or had to be
        called to the phone. CWL - is that ok or do you want 2 separate questions? [CWL: Please
        program as 2 separate questions]  Fixed EB 12/99

        I did the same thing with questions 4a & c and 4 b & d. [CWL: Please follow the hard copy]. -
        Fixed EB 12/99

        ** Add Contact Information in the first screen (Subject's Name, Address, ID#, Phone #.) or
        create a Sub Form for this information and revise the instruction in Exit 4 accordingly. - cwl
        Sub form created EB 12/99

  3.     According to the HC, answer #4 (Refused, No Information) should go to Exit #1. CATI does skip
        to Exit #1, however, the skip also includes Exit #4. This makes sense, I just want to confirm since
        the HC doesn't mention Exit 4 in the skip pattern for response #4. Since Exit 1 didn't have any
        instructions in the hard copy, I added what I thought were reasonable instructions. CWL - Let me
        know if this is ok as is, or if I need to make changes.

  4.     Exit #1 script contains the following information that doesn't appear on HC:  IF
        CORRECT NUMBER: Thank you very much.  Goodbye. PRESS CTL/S  AND
        CHOOSE NONRESPONSE. See above comments.

  5.     Currently, the only month an appointment can be set is December 1999.1 set that
        up for testing purposes. CWL will need to look at the survey definition and let me
        know what changes need  to be made. EB  12/99
C:\MY DATA FILE\CTEPPFinalReport91604\QAQCExhibit_3.doc

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                   Exhibit 4. CATI Interview Monitoring Form
Interview Monitoring Form
Study:
Interviewer:
Monitor:
Date:



Time
Begin/End:
Study Manager:



Total Number of Calls Monitored: Number of Contact-Calls:
[RECORD THE RESULTS OF MONITORING FOR EACH CONTACT-CALL]
Subject ID#:
1. Identify self and read introduction clearly
2. Record the dial result correctly
3. Record appropriate interviewer comments
4. Make appointment correctly
5. Read questions clearly and follow
instructions
6. Use appropriate probing when necessary
7. Record responses correctly
8. Record appropriate remarks when
necessary
9. Maintain neutrality and control of interview
10. Maintain a courteous, professional manner
1 1 . Answer respondents questions
appropriately
12. Refrain from giving personal
remarks/opinions
1=YES
2=NO
3=NA












Comments:












 Did the Supervisor discuss any problems with the interviewer? Yes
 Questions # and Problems Identified:
• No

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                     Exhibit 5. CTEPP Tracking System
Collection Checklist



>








<
Item*
1
2
3
1
5
6
7
8
9
10
11
1?
Sample / Data
Indoor Air-;\AD1 -Room#1
Indoor Air-XAD 2-Room#1
Outdoor Air-XAD 3
Outdoor Air-XAD A
Indoor Air - XAD 5 - Room #2
Indoor Air-XAD 6 -Room #2
1 Solid Food container -Room
1 Liquid Food container- Room
1 Water container per Center
1 Solid Food container Room
1 Liquid Food container Room
Hnrrt-Flnnr Winfi- 1 npr rpntpr
Sample
Type
IAN
IAA
OAN
OM
IAN
IAA
SFC
LFC
DRW
SFC
LFC
FRW
Sample I
IAN1 051E
IAA10676
OAN1 073
OAA1091
IAN10547
IAA10678
SFC1205
LFC12171
DRW126
SFC1205
LFC12172
FSW1 37?
i
-











r^



t








<
Collected By
JMcDonell
J McDonell
J McDonell
J McDonell
L Lantz
L Lantz
T Branch
T Branch
T Branch
CDagnino
CDagnino

Collected Date
07/1 9/2000
07/19/2000
07/20/2000
07/20/2000
07/20/2000
07/20/2000
07/19/2000
07/19/2000
07/19/2000
07/20/2000
07/20/2000

Sample
Conditior1
Good
Good
Good
Good
Good
Good
Good
Good
Good
Good
Good
Fynlnin
HVS3
Ss.rnp












Sample
Explanati











SRmnle
Received
Bv
CLyu
CLyu
CLyu
CLyu
CLyu
CLyu
CLyu
CLyu
CLyu
CLyu
CLyu

Received Date —
07/20/2000
07/20/2000
07/21/2000
07/21/2000
07/21/2000
07/21/2000
07/20/2000
07/20/2000
07/20/2000
07/21/2000
07/21/2000
>|~

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               Exhibit 6. CTEPP Participant Data QC Check List
CTEPP ID: 09-004-1
Data Item
1. Daily Checklists
2. Form #1
3. Consent Forms (2)
4. Receipts (2)
5. Air Log
6. Premonitoring
7. Postmonitoring
8. Chemical Table
9. Observation Survey
10. Sketches
11. Diary
12.


Check Notes
Complete
Complete
Participation consent: Complete
Future consent: Complete
$25 and $75
Complete
Complete
Complete
Complete
Complete
Complete (to be entered electronically)
Non-marked clothing items on page 8, (F1.4) on page 9, (F9) on page 16.


C:\MY DATA FILE\CTEPPFinalReport91604\QAQCExhibit_6.doc

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                      Exhibit 7. CTEPP Data Entry Program Test
                                DATA ENTRY TEST
                                 SUZANNE BENNY
                                       8/21/00
 Form 4:

 1.   No place for cooperation/quality of interviewer - need this info?
     Fixed 08/28/00 ER
 2.   A3 - asks for to identify room - include # only, or verbal description too?
     Verbal description too. 08/31/00 ER
 3.   A3 & A7 - include instructions on how to advance from these (i.e., leave blank)?
     Fixed 08/28/00 ER
 4.   A12 j & k - include instructions to leave blank if n/a, and not to put "2" for "No"
     Fixed 08/28/00 ER
 5.   B17 - no place for "n/a" - this is the farm income question
     Fixed 08/28/00 ER
 6.   C1&C10- assume minutes = 0 if blank? Yes (added instructions on screen) 08/31/00
     ER
 7.   C6 - no place for "none"
     Fixed 08/28/00 ER
 8.   C26- no option for "never"
     Fixed 08/28/00 ER
C:\MY DATA FILE\CTEPPFinalReport91604\QAQCExhibit_7.doc

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    Exhibit 8. CTEPP Double Data Entry Program

                   Initial Screen
Form 1
Form 2
Form 3
Form A
Form 5
Form 6
Form 7
Form 3
Form 9
Form 10

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                  Exhibit 9. CTEPP Double Data Entry Program

                                Data Entry Screen
IS Blaise Data Entry - K:\Projects\CATI\Ctepp\DataForm\Real\TeamA\Form04\form04
Forms  Answer  Navigate  Options  Help
 D 1 H H X
FORM04 I
0  B
CARPET INFORMATION

(A2) Is there any carpet (including area rugs) in your home?
  1. Yes
  2. No
C 7. Refused
                           8. Don't Know
                           9. Missing
                                                J2/YR
                                                |7DA/WK
 Old   , 3/26   Modified by rules , Clean  Navigate FORM04

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            Exhibit 10. CTEPP Double Data Entry Program




                            Status Screen
Data Entry Forms

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                 Exhibit 11. CTEPP Double Data Entry Crosschecks
                             COMPARE Procedure
             Comparison of TEAMA.FORM04A with TEAMB.FORM04A
                              (Method=EXACT)

                  Comparison Results  for Observations
PID=010011:
Variable    Base Value
   A12ad
May_Note
Oct_Note
A16
                     0
          2 WKS IN SPR
          2 WKS IN FAL
          8:00-8:3 0AM
                                  Compare
                                 98.000000
                              8:00-8:3 0AM
                                   Diff .
                               98.000000
                                                          % Diff
     PID=010031
     Variable
         A6_l
         A6_4
         A7_l
          A16
  Base Value
      I/WEEK
      I/WEEK
KITCHEN/DINI
  6:30AM/5PM
     PID=010041:
        Variable
            A3 1
                             Compare
                             I/ WEEK
                             I/ WEEK
                        KITCHEN/ DIN
                        6:30 AM/ 5PM
     Base Value
      LIVING RM
                                Compare
                            LIVING ROOM
C:\MY DATA FILE\CTEPPFinalReport91604\QAQCExhibit_l l.doc

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CTEPP OH QA/QC Report                                             02/17/2004
QA/QC Summary Report for CTEPP Ohio Data Collection
I.      Introduction

The research study, "Children's Total Exposure to Persistent Pesticides and Other Persistent
Organic Pollutants" (CTEPP), is a pilot-scale project involving about 260 children, which
investigates the possible exposures that young children may have to common contaminants in
their everyday surroundings.  These contaminants include several pesticides, phenols,
poly chlorinated biphenyls, and poly cyclic aromatic hydrocarbons, some of which are suspected
of being endocrine disrupters. The targeted compounds are persistent in the indoor and
sometimes the outdoor environments, so that very low levels may exist in the children's
surrounding microenvironments and provide a source of chronic, non-acute exposure.  The
primary purposes of the research are to increase our understanding of children's exposures to
persistent pollutants, to gain information on the various activities, environmental media, and
pollutant characteristics that may influence children's exposures, and to generate further
questions and hypotheses for future research. This document provides a summary of the quality
assurance (QA) and quality control (QC) procedures conducted for the CTEPP project. In the
following sections, we describe the study activities and the QA/QC procedures. The relevant
standard operating procedures (SOPs) are listed in the Reference Section at the end of this
document.

II.     CTEPP Data Collection Activities

As illustrated in Exhibit 1  (CTEPP Study Activities Flow Chart), CTEPP data collection
activities are conducted in three phases: Pre-Data Collection, Field Data Collection, and Post-
Data Collection.  To ensure data quality, standard operating procedures (SOPs) were developed
and project team members were trained according to the SOPs. All project activities were
conducted by trained project staff members, who were divided into the following project teams:
1) recruitment team (including RDD and field teams), 2) field support team, and 3) field data
collection team.

The recruitment team was responsible for recruiting daycare and RDD home participants. It was
supported by a team of telephone interviewers and some field staff members.  During the pre-
data collection phase, the following key activities were conducted by the recruitment team and
field support team.

       •  Recruit/Train  Participants, Present  T-shirts,  Pay  $25, Remind  Food  Samples
          Collection
       •  Label Sample Containers
       •  Compile Field Notebooks
       •  Pack Van, Check items on the check lists

The field support team conducted QA/QC checks before and after the preparation of all field
supplies, sample containers, and data forms. They ensured that all the materials needed for the
field data collection activities were complete and accurate.

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CTEPP OH QA/QC Report                                             02/17/2004
After the field support team completed the preparation work, the field data collection team did a
final check on all needed field supplies, sample containers, and data forms for the scheduled
sampling appointments. After loading the van and completing the final checks, the field data
collection team drove to the sampling site for the scheduled sampling appointment with the study
subject. The following key activities were conducted by the field data collection team during the
field data collection phase.

       •  Field Data Collection Activities
       •  Record Sample/Data Condition on Sample/Data Check Lists
       •  Put Samples in ZipLoc Bags
       •  Put Samples in Freezers
       •  Record problems/issues on Daily Check List
       •  Leave Field Notebooks in the CTEPP Workroom

Once the field data collection team returned to the Battelle office, the field support team received
the field samples and data from the field data collection team. The following key activities were
conducted by the field support team during the post-data collection phase.

       •  Update Sample/Data Check Lists in the CTEPP Tracking System (TS)
       •  Verify Sample Conditions
       •  Check Field Notebooks (data forms)
       •  File Field Notebooks in the participant folders
       •  Ship Samples
       •  Conduct Data Entry
       •  Update Progress Reports
       •  Update QC Check List

In the following Sections, we describe specific QA/QC procedures relevant to the CTEPP data
forms and database preparation.

III.    CTEPP QA/QC Procedures for Preparing the Questionnaire Data Forms and
       Questionnaire Database

Battelle is always committed to the production of highest quality data.  A key to accomplish this
objective is to implement standardized QA/QC procedures. QA/QC is a continuous process.  As
illustrated in Exhibit 2 (CTEPP QA/QC Procedures for Preparing Data Forms and Database),
Battelle implemented a comprehensive QA/QC plan to ensure data quality in all phases of the
CTEPP project, from pre-data collection to post-data collection phase.

A.     Pre-Data Collection Phase:

Developed and Tested Data Forms, CA TI Programs
During the pre-data collection phase, the following data forms were developed.

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CTEPP OH QA/QC Report                                             02/17/2004


       •   Recruitment Survey (Form #1)
       •   House/Building Characteristics Observation Survey - Home (Form #2)
       •   House/Building Characteristics Observation Survey - Child Daycare Center (Form
          #3)
       •   Pre-Monitoring Questionnaire - Parent (Form #4)
       •   Pre-Monitoring Questionnaire - Child Daycare Center (Form #5)
       •   Post-Monitoring Questionnaire - Parent (Form #6)
       •   Post-Monitoring Questionnaire - Child Daycare Center (Form #7)
       •   Child Activity Diary/Parent - Children Don't Attend Daycare (Form #8)
       •   Child Activity Diary/Parent - Children Attend Daycare (Form #9)
       •   Child Activity Diary - Daycare Teacher (Form #10)

All the data forms were tested by trained project staff for consistency and accuracy. In addition,
mock interviews and field data collection simulations were conducted to evaluate the
effectiveness of the data forms. The data forms were finally reviewed and approved by IRB and
OMB. Form #1  (Recruitment Survey) was modified into computer-assisted telephone
interviewing programs (CATI) for recruiting the ROD participants (children who did not attend
daycares). The CATI programs automatically performed QC checks during data entry, which
included range checks, consistency checks, and skip pattern checks. Before the CATI programs
were approved for actual ROD recruitment and data collection, it also went through rigid QA/QC
checks for programming errors. Exhibit 3 provides an example of the QA/QC test document.

Conducted Staff Training on Data Collection SOPs
To ensure the consistency and high quality of data collection, a comprehensive training plan was
implemented. The recruitment team members received training in the implementation of the
recruitment SOPs before subject recruitment activities began.  Standardized scripts and materials
(e.g., CATI system and Interviewer's Manual) were developed. The Interviewer's Manual
provided information on the background and aims of this study, the standard interviewing
procedures, confidentiality requirements, and question-by-question specifications for the
recruitment survey. Interviewers must be certified for the study before they can initiate any
contact with the study subjects. In order to be certified as a CATI interviewer for the study,  an
interviewer must pass the following two tests:

       1. CATI Operation Test:    The interviewer must demonstrate that  he/she is  familiar
                                 with the CATI  instrument and  the  computer-working
                                 environment.
       2. CATI Interview Test:     The interviewer must conduct  at least two mock CATI
                                 interviews and receive a satisfactory evaluation from the
                                 CATI supervisor.

Training for the field data collection team members included a five-day (40-hour) training
session and additional self-practice time was provided to the field staff.  The following is a brief
summary of the training topics.

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CTEPP OH QA/QC Report                                              02/17/2004


       Day 1:       Training covered study background, recruitment SOPs, confidentiality
                    issues, informed consent procedures, and the interviewing protocol.

       Day 2:       The field staff members were trained to administer all the data collection
                    forms.

       Day 3:       The training included field sampling procedures, i.e., the use of field
                    notebooks and the collection of air, food, urine, dermal hand wipes, hard
                    floor wipes, food preparation surface wipes, the polyurethane foam (PUF)
                    roller for dislodgeable residues, indoor floor dust,  and soil samples.
                    Internal field audits and QC procedures were also  discussed.

       Days 4/5:     A mock field sampling exercise (with 2 volunteers) was conducted during
                    the last two days of training. The field team visited the volunteer's home
                    and conduct actual field sampling activities. The field staff members were
                    also certified during these two days (i.e., they were required to pass the
                    tests set for the field sampling procedures).

       Day 5:       Training in packing and shipping procedures was given on the final day.
                    The training ended with a final review of all SOPs.

Before field data collection began, the field support team members also went through training for
data form tracking and processing procedures, coding procedures, and quality control
procedures.

Conducted Participant Orientation/Training
Due to the unique features of the CTEPP study, some key information and  samples were
collected by the study participants themselves. Keeping the  participants  involved and well
informed was critical to the success of the study.  All participants (i.e., parents and daycare staff)
were trained (i.e., received project orientation) prior to the scheduled sampling appointment
(normally one week before the  actual sampling).  During the orientation/training, our project
staff went through the SOPs for collecting samples of food, urine, and dermal hand wipes and
recording the Child Activity Diary with the participants.

B.     Data Collection Phase:

Conducted CATI Monitoring
As a standard procedure to ensure data quality, Battelle routinely verifies data collection
activities. For monitoring CATI interviews (Form #1 RDD), Battelle employed sophisticated
computer software (i.e., PROXY) and a telephone monitoring system to validate CATI interview
data. With the monitoring system, the CATI supervisor could actually "watch" and "listen" to an
interview in progress. A standardized monitoring procedure was developed and used for CATI
monitoring. The supervisor randomly selected an interview  for monitoring. The monitoring
system transferred the interviewer's computer screen and telephone conversation in real time to
the  supervisor's workstation. The interviewer being monitored or the study respondent could not
notice any difference while the monitoring was in progress.  To ensure the  participant's  right, a

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CTEPP OH QA/QC Report                                               02/17/2004


statement that the interview might be monitored by a project supervisor for quality assurance was
read to the respondent before the interview began. The monitoring results were recorded in a
CATI Interview Monitoring Form (See Exhibit 4).

Conducted Staff Field Edit
All field data collection team members were trained to conduct field edit for all completed data
forms. During data collection, the field staff conducted field edits to identify missing data items
or questionable information at the sampling site.  Any identified issues or problems were
resolved at the sampling site before the field data collection team returned to Battelle whenever
the field conditions allowed. A Daily Activity Check List was developed to assist the field staff
in conducting data collection activities and field edit.  The field edits ensured that any data
collection issues or problems were resolved early at the sampling site with the study participant.

Conducted Internal Field Audits
According to CTEPP SOP 2.25, Battelle conducted periodic internal field audits to ensure high
quality of data collection. The internal field audits were conducted by the Field Team Leader
and/or designated field auditors.  The field data collection team was not notified of the field audit
visit. The field audit schedule was randomly selected by the field auditor/Field Team Leader.
During a field audit visit, the field auditor observed all field sampling activities according to the
SOPs.  The field auditor recorded any findings or observations about the field staffs work that
was not consistent with the SOPs. Before the end of each field audit visit, the field auditor
discussed the findings or observations with the field staff. A field audit report was prepared by
the field auditor after each field audit to document the field audit visit.

Conducted External Field Audits
In addition to Battelle internal field audits, some external field audits were conducted by an EPA
auditor and project officer.  On September 12 and 13, 2000, EPA audited the North Carolina data
collection teams.  On June 5, 2001, an EPA project officer conducted a field observation visit
with the Ohio data collection teams. There were no findings in all the external field audits and
observation visits.

C.     Post-Data  Collection Phase:

Applied Chain of Custody Procedures
In order to protect  the study samples and data forms, a standardized chain-of-custody procedure
was developed and implemented for the CTEPP study (See SOP 2.26).  In addition, Battelle
developed a sophisticated CTEPP Tracking System to monitor the status of data collection. As
soon as the field team returned to the office, the field support (receiving) team checked the
samples/data condition and updated the data collection status in the CTEPP Tracking System
(See Exhibit 5).  The following information was recorded for each study participant.

       •   Sample/Data Description
       •   Sample Type
       •   Sample ID#
       •   Staff s Name Who Collected the Sample/Data
       •  Date of Collection

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CTEPP OH QA/QC Report                                              02/17/2004


       •   Sample Condition
       •   Number of Floor Dust Sampling Areas
       •   Sample Explanation (if Sample Condition = Explain)
       •   Staff s Name Who Received the Sample/Data from the Field Team
       •   Date Received Sample/Data
       •   Time Received Sample/Data

If the  samples/data need to be shipped to another location,  the  CTEPP  Tracking  System
automatically generates a Chain-of-Custody record for the staff to sign.

Receiving Team Conducted QC Checks
After checking and storing the environmental and biological samples, the receiving team
conducted QC checks on all the participant's data forms  and study materials. A CTEPP
Participant Data QC Check List was developed to track the QC status of each data item (See
Exhibit 6). The staff carefully reviewed each data form for missing or questionable data items.
After the staff completed the QC review, she/he put her/his initial and date of review on the back
of the data form. Any pending issues (e.g., missing materials or information) identified through
the QC review were recorded in the Check Notes of the CTEPP Participant Data QC  Check List.
The field support staff resolved each pending issue by checking with the field data collection
staff or contacting the participant.

Developed and Tested Data Entry Programs
After the data forms went through the QC checks and received a "complete" status, the forms
were ready for data entry.  The Battelle programming team developed a double data entry
program to allow two separate data entry teams to conduct data entry.  The data entry program
was designed to perform additional QC checks during data entry, which included range checks,
consistency checks, and skip pattern checks. Before the  data entry program was used for actual
data entry, it was fully tested by trained project staff.  An example of the testing document is
illustrated in Exhibit 7 (CTEPP Data Entry Program Test).  Examples of data entry program
screens are illustrated in Exhibits 8, 9, and 10.

Conducted Double-Data Entry
All data forms were entered twice and verified, using the CTEPP Double Data Entry  Program.
Two data entry teams (Teams A and B) performed the data entry work and entered the data into
two separate databases.  All the data entry team members were trained before they were allowed
to conduct data entry work. Each data form was entered twice by 2 different people.  As a
standard procedure for entering the open text fields, the data entry teams were instructed to enter
participant's responses verbatim. [Note: Some of the participant reported information contained
typos or spelling errors. Per EPA's instructions (2/7/02 conference call), we have corrected
those spelling errors.]

Conducted Computer Program Checks for Data Entry Errors
A computer verification program was developed for checking the accuracy of the entered data
and every record in the two databases was crosschecked. An example of the crosschecks
computer program is illustrated in Exhibit 11  (CTEPP Double Keying Crosschecks &

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CTEPP OH QA/QC Report                                              02/17/2004


Corrections). The crosscheck computer program identified any discrepancies between the two
databases and the results were displayed on screen.

Corrected Data Entry Errors
For each data item detected by the computer program, the data entry staff verified the
information with the original participant data form and made corrections as needed.  The
crosscheck computer program made it easy for the staff to identify data entry problems and to
verify the information. This program also kept a log of all changes made, including original and
new data, date/time of data changed, and name of the staff that made the changes.

Prepared Final Master Database
A final master database for each data form was prepared after all QC checks were completed and
data entry discrepancies were corrected. Backup data files were also created to protect the
CTEPP data. All CTEPP data files and document are  protected by password. Only  authorized
project staff members have access to the restricted project folders.

Prepared and Verified Data Dictionary and Document
After the completion of master database preparation, the programming team prepared the
updated data dictionary for each data form database.  The project staff verified the data
dictionaries by comparing the hard copy manuals, the  electronic files, and the database
structures.

Final Data Verification Checks
After completing all the tasks described in the earlier sections, the project staff conducted final
QA/QC checks by reviewing data frequency reports and verifying (about 10%) randomly
selected participant files.  Data items in the database were checked against the data
documentation manual (i.e., data variables in the data dictionary) and the actual participant data
in the original data form.  The results of the random checks showed 100% accuracy. The data in
the original participant data form were correctly recorded in the CTEPP database, and the data
variables were accurately documented in the data dictionary. Before Battelle delivered the
database to EPA, the data variables containing personal identifiers (i.e., names, street address,
GPS, etc.) were removed from the database or the information was modified to ensure participant
confidentiality. The results of the final data verification checks are shown in Table 1.  A list of
data variables removed or modified for ensuring participant confidentiality is included in Table
2.

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CTEPP OH QA/QC Report
                                                                   02/17/2004
        a
        a
        a
                                          Exhibit 1.  CTEPP Study Activities Flow Chart
               Pre-Data
              Collection
Recruit/Train Participants,
Present T-shirts, Pay $25,
Remind Food Samples
Collection
Label Sample Containers
Compile Field Notebooks
Pack Van, Check items on
the check lists
           CTEPP Field
           Support Team
                                               Field Data
                                               Collection
a   Field Data Collection
Q   Record Sample/Data Condition
    on Sample/Data Check Lists
Q   Put Samples in ZipLoc Bags
Q   Put Samples in Freezers
Q   Record problems/issues on
    Daily Check List
a   Leave Field Notebooks in the
    CTEPP Workroom
                                        CTEPP Field Data
                                        Collection Team
                                                  Post-Data
                                                  Collection
a   Update Sample/Data Check
    Lists in the CTEPP TS
Q   Verify Sample Conditions
Q   Check Field Notebooks
a   File Field Notebooks
a   Ship Samples
Q   Data Entry
Q   Progress Reports
a   QC Reports
                                                                                                         7
                                                CTEPP Field
                                                  Support
                                              (Receiving) Team

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CTEPP OH QA/QC Report
                                02/17/2004
  Exhibit 2. CTEPP QA/QC Procedures for Preparing Data Forms and Database
   Pre-Data Collection
   Phase
•  Developed and Tested Data Forms, CATI
   Programs
•  Conducted Staff Training on Data Collection
   SOPs
•  Conducted Participant Orientation/Training
   Data Collection Phase
•  Conducted CATI Monitoring
•  Conducted Staff Field Edit
•  Conducted Internal Field Audits
•  Conducted External Field Audits
   Post-Data Collection
   Phase
   Applied Chain of Custody Procedures
   Receiving Team Conducted QC Checks
   Developed and Tested Data Entry Programs
   Conducted Double-Data Entry
   Conducted Computer Program Checks for
   Data Entry Errors
   Corrected Data Entry Errors
   Prepared Final Master Database
   Prepared and Verified Data Dictionary and
   Document
   Final Data Verification Checks

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CTEPP OH QA/QC Report                                                    02/17/2004
                        Exhibit 3.  KDD CATI Tests Document
                                      ROD CATI Tests
                                       Carey Aselage
                                      December 8, 1999

  1.      Add the following interviewer instructions to this question: May I speak to the parent or guardian
         of the children in this household (OR NAME OF RESPONDENT IF OBTAINED THE NAME
         FROM PREVIOUS CALL)?-fixed EB 12/99

  2.      Skip pattern for answer #1 goes to Q3. However, this question is numbered as Q2 in CATI. I
         combined question 2 and 3 into 1  question and called it Q2_3. Since it is really the same question
         with a little different wording depending on whether the parent answered the phone or had to be
         called to the phone. CWL - is that ok or do you want 2 separate questions? [CWL: Please
         program as 2 separate questions] Fixed EB 12/99
                        I did the same thing with questions 4a & c and 4 b & d. [CWL: Please follow
                        the hard copy]. -Fixed EB 12/99
                        ** Add Contact Information in the first screen (Subject's Name, Address,
                        ID#, Phone #.)  or create a Sub Form for this information and revise the
                        instruction in Exit 4 accordingly. - cwl Sub form created EB 12/99
  3.      According to the HC, answer #4 (Refused, No Information) should go to Exit #1. CATI does skip
         to Exit #1, however, the skip also  includes Exit #4.  This makes sense, I just want to confirm since
         the HC doesn't mention Exit 4 in  the skip pattern for response #4. Since Exit 1 didn't have any
         instructions in the hard copy, I added what I thought were reasonable instructions. CWL - Let me
         know if this is ok as is, or if I need to make changes.
  4.      Exit #1 script contains the following information that doesn't appear on HC: IF CORRECT
         NUMBER:  Thank you very much. Goodbye.  PRESS CTL/S AND CHOOSE NONRESPONSE.
         See above comments.

  5.      Currently, the only month an appointment can be set is December 1999.1 set that up for testing
         purposes. CWL will need to look  at the survey definition and let me know what changes need to be
         made. EB 12/99
                                                                                        10

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CTEPP OH QA/QC Report
                        02/17/2004
Exhibit 4. CATI Interview Monitoring Form
Interview Monitoring Form
Study:
Interviewer:
Monitor:
Date:



Time Begin/End:
Study Manager:
1

Total Number of Calls Monitored:
Number of Contact-Calls:
[RECORD THE RESULTS OF MONITORING FOR EACH CONTACT-CALL]
Subject ID#:
1. Identify self and read introduction clearly
2. Record the dial result correctly
3. Record appropriate interviewer comments
4. Make appointment correctly
5. Read questions clearly and follow instructions
6. Use appropriate probing when necessary
7. Record responses correctly
8. Record appropriate remarks when necessary
9. Maintain neutrality and control of interview
10. Maintain a courteous, professional manner
11. Answer respondent's questions appropriately
12. Refrain from giving personal remarks/opinions
1=YES
2=NO
3=NA












Comments:












 Did the Supervisor discuss any problems with the interviewer? Yes •
 Questions # and Problems Identified:
    •— No
                                                                                       11

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CTEPP OH QA/QC Report
02/17/2004
                        Exhibit 5.  CTEPP Tracking System
   Collection Checklist



>








N
Item*
1
2
3
1
5
6
7
8
9
10
11
1?
Sample / Data
Indoor Air-XAD 1 -Room#l
indoor Air-XAD 2- Room #1
OutdoorAir-XAD3
OutdoorAir-XADI
IndoorAir-XAD 5-Room#2
indoor Air-XAD 6 -Room #2
1 Solid Food container- Room
1 Liquid Food container- Room
1 Water container percenter
1 Solid Food container Room
1 Liquid Food container Room
HRrd-Flnnr Wine - 1 nerrFnter
Sample
Type
IAN
IAA
OAN
OAA
IAN
IAA
SFC
LFC
DRW
SFC
LFC
FRW '
Sample l[-
IAN10546"
IAA10676
OAN1079
OAA1091!
IAN1054?
IAA10678
SFC1205C
LFC12171
DRW126:
SFC12D51
LFC12172
FSW1 17?
>r



>








<
Collected By
JMcDonell
JMcDonell
J McDonell
J McDonell
L Lantz
L Lanlz
T Branch
T Branch
T Branch
CDagnino
CDsgnino

Collected Date
07/19/2000
07/19/2000
07/20/2000
07/20/2000
07/20/2000
07/20/2000
07/19/2000
07/19/2000
07/19/2000
07/20/2000
07/20/2000

Sample
Conditior
Good
Good
Good
Good
Good
Good
Good
Good
Good
Good
Good
FvnlRin
HVS3
Samp












Sample Received
ExplanstilBy











fiamnlp
CLyu
CLyu
CLyu
CLyu
CLyu
CLyu
CLyu
CLyu
CLyu
CLyu
CLyu

Received Date —
07/20/2000
07/20/2000
07/21/2000
07/21/2000
07/21/2000
07/21/2000
07/20/2000
07/20/2000
07/20/2000
07/21/2000
07/21/2000
>r~
                Collected By   Received By   Clear Record
                                                                                    12

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CTEPP OH QA/QC Report
02/17/2004
              Exhibit 6. CTEPP Participant Data QC Check List
CTEPP ID: 09-004-1
Data Item
1. Daily Checklists
2. Form #1
3. Consent Forms (2)
4. Receipts (2)
5. Air Log
6. Premonitoring
7. Postmonitoring
8. Chemical Table
9. Observation Survey
10. Sketches
11. Diary
12.


Check Notes
Complete
Complete
Participation consent: Complete
Future consent: Complete
$25 and $75
Complete
Complete
Complete
Complete
Complete
Complete (to be entered electronically)
Non-marked clothing items on page 8, (F1.4) on page 9, (F9)
on page 16.


                                                                      13

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CTEPP OH QA/QC Report                                            02/17/2004
                  Exhibit 7. CTEPP Data Entry Program Test
                                DATA ENTRY TEST
                                 SUZANNE BENNY
                                       8/21/00
 Form 4:

 1.   No place for cooperation/quality of interviewer - need this info?
     Fixed 08/28/00 ER
 2.   A3 - asks for to identify room - include # only, or verbal description too?
     Verbal description too. 08/31/00 ER
 3.   A3 & A7 - include instructions on how to advance from these (i.e., leave blank)?
     Fixed 08/28/00 ER
 4.   A12 j & k - include instructions to leave blank if n/a, and not to put "2" for "No"
     Fixed 08/28/00 ER
 5.   B17 - no place for "n/a" - this is the farm income question
     Fixed 08/28/00 ER
 6.   C1&C10- assume minutes = 0 if blank? Yes (added instructions on screen) 08/31/00
     ER
 7.   C6 - no place for "none"
     Fixed 08/28/00 ER
 8.   C26- no option for "never"
     Fixed 08/28/00 ER
                                                                            14

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CTEPP OH QA/QC Report
02/17/2004
                Exhibit 8.  CTEPP Double Data Entry Program

      Initial Screen
           Choose a Team
            Form 1
            Form 2
            Form 3
            Form
            Form 5
            Form 6
            Form 7
            Form 8
            Form 9
            Form 10
                                                                        15

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CTEPP OH QA/QC Report
02/17/2004
               Exhibit 9. CTEPP Double Data Entry Program
Data Entry Screen
1 IS Blaise Data Entry - K:\Projects\CATI\Ctepp\DataForm\Real\TeamA\Form04\form04
Forms Answer Navigate Options Help
D i H B X * 0 B B- <>
FORM04 |
CARPET INFORMATION
(A2) Is there any carpet (including area rugs) in
r 2. No r
r 7. Refused
your home?
8. Don't Know
9. Missing

[A2 Q yes | Mm
\A3 [BEDROOM AB
i R "
A5 |2/YR A^ly
« & — r
Old 3/26 Modified by rules Clean Navigate FQRM04
1 e -d
|2/YR
J7DA/WK
IBEDROOM
|2/YR ^
1 //,
                                                                     16

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CTEPP OH QA/QC Report
02/17/2004
                Exhibit 10. CTEPP Double Data Entry Program
Status Screen
    Data Entry Forms
                                                                        17

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CTEPP OH QA/QC Report
                                                                 02/17/2004
            Exhibit 11. CTEPP Double Keying Crosschecks & Corrections
  Hi DOUBLE KEY SOFTWARE
                                                                                          -Ifllxj
   File  Edit
                Double Keying Error Correction Form
                 Tables:
      I Form 03
- Functions—
                                                        Friday, September 06, 2002 12:13PM
                                                                    Total Records: 32









^








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CTEPP OH QA/QC Report
02/17/2004
            Table 1. Final Data Verification Checks for OH Database
PID
41-001-1
46-002-1
52-004-1
61-004-1
64-003-1
70-001-1
98-008-1
98-026-1
98-053-1
98-069-1
98-115-1
51-000-3
66-000-3
Data Forms Checked
2, 4, 6, 9, Air Data Log
1,2, 4, 6, 9, Air Data Log
2, 4, 6, 9, Air Data Log
2, 4, 6, 9, Air Data Log
2, 4, 6, 9, Air Data Log
2, 4, 6, 9, Air Data Log
2, 4, 6, 8, Air Data Log
2, 4, 6, 8, Air Data Log
2, 4, 6, 8, Air Data Log
2, 4, 6, 8, Air Data Log
2, 4, 6, 8, Air Data Log
3,5,7, 10, Air Data Log
3,5,7, 10, Air Data Log
QA/QC Checks Status
Complete Checks: Checked all
variables of each data form
Complete Checks: Checked all
variables of each data form
Complete Checks: Checked all
variables of each data form
Partial Checks: Checked some
randomly selected variables of
each data form
Partial Checks: Checked some
randomly selected variables of
each data form
Partial Checks: Checked some
randomly selected variables of
each data form
Complete Checks: Checked all
variables of each data form
Complete Checks: Checked all
variables of each data form
Partial Checks: Checked some
randomly selected variables of
each data form
Partial Checks: Checked some
randomly selected variables of
each data form
Partial Checks: Checked some
randomly selected variables of
each data form
Partial Checks: Checked some
randomly selected variables of
each data form
Partial Checks: Checked some
randomly selected variables of
each data form
Results
No problem
No problem
No problem
No problem
No problem
No problem
No problem
No problem
No problem
No problem
No problem
No problem
No problem
                                                                         19

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CTEPP OH QA/QC Report
02/17/2004
             Table 2. Potential Participant Identifying Information
Form#
2
2
2
2
2
2
2
2
2
3
3
3
3
3
3
3
3
3
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
5
5
5
5
5
5
Field Name
C3al
C3bl
C3cl
CSlatdeg
CSlatms
CSdirl
CSlondeg
CSlonms
C8dir2
C3al
C3bl
C3cl
CSlatdeg
CSlatms
CSdirl
CSlondeg
CSlonms
C8dir2
Name
Phone
Jan Note - Dec Note
A14spec
Bl 1(-10)
B6
B7
B8
B9spec
BIO
Bll
B12
B13spec
B14
B15
B16
B29
B31
B33
C32m and C32d
C33mandC33d
Name
Phone
A4 ltoA4 5
A14spec
A16
B15 ItoBIS 4
Remarks
May contain street names
May contain street names
May contain street names
GPS reading
GPS reading
GPS reading
GPS reading
GPS reading
GPS reading
May contain street names
May contain street names
May contain street names
GPS reading
GPS reading
GPS reading
GPS reading
GPS reading
GPS reading
Contact name for who knows the age of the house
Phone number for who knows the age of the house
May contain names
May contain street names
People's names
Employer's name, check all
May be too specialized, check all
May be too specialized, check all
Person's name
Employer's name, check all
May be too specialized, check all
May be too specialized, check all
Person's name
Employer's name
May be too specialized, check all
May be too specialized, check all
Person's name
Person's name
Person's name
Child's DOB - Day and Month (kept Year)
Adult's DOB - Day and Month (kept Year)
contact name for age of the house
Phone number for age of the house
Change all Classrooms names to either Cl
(classroom 1) or C2 (classroom 2).
May contain street names
May contain street names
Change all Classrooms names to either Cl
(classroom 1) or C2 (classroom 2).
Action
Revised as needed
Revised as needed
Revised as needed
Removed
Removed
Removed
Removed
Removed
Removed
Revised as needed
Revised as needed
Revised as needed
Removed
Removed
Removed
Removed
Removed
Removed
Removed
Removed
Revised as needed
Revised as needed
Revised as needed
Revised as needed
Revised as needed
Revised as needed
Revised as needed
Revised as needed
Revised as needed
Revised as needed
Revised as needed
Revised as needed
Revised as needed
Revised as needed
Revised as needed
Revised as needed
Revised as needed
Removed
Removed
Removed
Removed
Revised as needed
Revised as needed
Revised as needed
Revised as needed
                                                                           20

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CTEPP OH QA/QC Report
02/17/2004
             Table 2. Potential Participant Identifying Information
Form#
5
5
6
6
6
6
6
6
7
7
7
8
8
8
8
8
9
9
9
9
9
10
10
10
10
10
Field Name
B21Nm atoB21NmJ
B21TL atoB21TLJ
QIAwhtoQIZwh
QIAho to QlZho
Q21Nm atoQ21Nm k
Q21TL atoQ21TL k
Q22 a to Q22 k
Q24Lc atoQ24Lc k
Q1AB to Q1ZB
Q1AC to Q1ZC
comment
Q4Wher 1 to Q4Wher 5
Q5 ItoQS 5
Q6 ltoQ6 5
ACTdSp 1 to ACTdSp 5
ACTiSp 1 to ACTiSp 5
Q4Wher 1 to Q4Wher 4
Q5 1 to Q5 4
Q6 1 to Q6 4
ACTdSp 1 to ACTdSp 4
ACTiSp 1 to ACTiSp 4
Q4Wher 1 to Q4Wher 3
Q6Spc 1 to Q6Spc 3
Q7Spc 1 to Q7Spc 3
ACTdSp 1 to ACTdSp 3
ACTiSpJ to ACTiSp_3
Remarks
Name of commercial contractor (a to j)
Phone number of commercial contractor (a to j)
May contain names
May contain names
Commercial Contractor name
Commercial Contractor Phone number
Could contain names
Could contain names
Could contain names
Could contain names
Could contain names
Could contain recognizable locations or names of
people
Could contain recognizable locations or names of
people
Could contain recognizable locations or names of
people
May contain names or locations
May contain names or locations
Could contain recognizable locations or names of
people
Could contain recognizable locations or names of
people
Could contain recognizable locations or names of
people
May contain names or locations
May contain names or locations
Could contain recognizable locations or names of
people
Could contain recognizable locations or names of
people
Could contain recognizable locations or names of
people
May contain names or locations
May contain names or locations
Action
Removed
Removed
Revised as needed
Revised as needed
Removed
Removed
Revised as needed
Revised as needed
Revised as needed
Revised as needed
Revised as needed
Revised as needed
Revised as needed
Revised as needed
Revised as needed
Revised as needed
Revised as needed
Revised as needed
Revised as needed
Revised as needed
Revised as needed
Revised as needed
Revised as needed
Revised as needed
Revised as needed
Revised as needed
                                                                           21

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CTEPP OH QA/QC Report                                              02/17/2004
IV.    CTEPP QA/QC Procedures for the Analytical Database

Analytical data were electronically imported into the database according to CTEPP SOP
4.12.  The analytical raw data (QUAN report) were generated from each instrument by a
qualified analyst (the first data reviewer). The QUAN report was then reviewed by the
TOL (the second data reviewer) for all the identified analytes.  The QUAN report was
then electronically transferred into a custom report and saved as a "crd" file.  The "crd"
file was then electronically parsed into an Excel spreadsheet template, pertinent data such
as sample extraction weight and quality assurance codes were added and saved as an
Excel file with an extension of ".xls" by the first data reviewer. The TOL reviewed all
the Excel files before importing into the analytical database. If any anomalous results
were observed in the data, every effort was made to identify any problems in the sample
collection, sample preparation,  and/or analysis, which could have contributed to the
anomaly. Data dictionaries and code sets for core analytical data, QA/QC data, and
ancillary data were developed for the analytical  database.  The completed Excel
spreadsheets were then electronically imported into the analytical database by the
database staff.

Database queries were developed to perform QA/QC  checks. The QA/QC checks
performed for the Ohio analytical database include (1) sample ID checks, (2) missing
data checks, (3) duplication data checks, (4) out-of-range checks, (5) upper- and lower-
concentrations checks, and (6) calculation checks.

Sample ID checks
The sample ID checks were performed to verify that all  Sample IDs with reported data
were valid Sample IDs, i.e., they were logged in as received from the field. If invalid
sample IDs were detected, the database staff traced back to the original raw data,
including laboratory record books and GC/MS logbooks, to identify the transcription
error and to make the corrections  accordingly.  All corrections were documented in the
database importing logbook.

Missing data checks
The missing data checks were performed to verify that all Sample IDs received from the
field had a full set of analytical  data reported.  Samples that were received but that did not
have a complete set of analytical data and/or ancillary data, other than for a stated reason
in the electronic CoC data, were identified, and one of the following correction actions
was taken (as appropriate): analytical data was found  and imported into the database, or
samples were located, processed,  analyzed, reviewed, and the analytical data was
imported into the  database.  Samples that were lost or damaged during laboratory
processing were identified and imported into the QA Action table with an explanation
regarding their disqualification.

Table 3  presents a summary of the number of samples collected and the number of
samples with  data reported.
                                                                              22

-------
CTEPP OH QA/QC Report
02/17/2004
             Table 3.  Summary of Ohio Sample Collection and Analysis
Sample Code a
DAA
DAH
DAN
DCA
BCD
DCH
DCN
DRW
FPW
FSW
IAA
IAN
IFD
LFA
LFC
OAA
OAN
PUF
SFA
SFC
SOL
URA
URC
Sample Description
Dermal Wipe at Home Adult #3 and #4
Dermal Wipe Day care Adult at Home
Dermal Wipe at Home Adult # 1 and #2
Dermal Wipe at Home Child #3 and #4
Dermal Wipe Day care Child at Day care
Dermal Wipe Day care Child at Home
Dermal Wipe at Home Child # 1 and #2
Drinking Water
Food Preparation Surface Wipe
Floor Surface Wipe
Indoor Air Acid
Indoor Air Neutral
Indoor Floor Dust
Liquid Food Adult
Liquid Food Child
Outdoor Air Acid
Outdoor Air Neutral
PUF Roller Surface Dislodgeables
Solid Food Adult
Solid Food Child
Soil
Urine Adult
Urine Child
Field Samples
Collected "
# Real ( #QA)
69
58
69
69 (14)
58
59
69 (14)
143(14)
16
38
149(1)
149(1)
143(14)
122c
170C
143(13)
143(13)
16(2)
127
156(14)
143
1,096
1,272
Field Samples
Reported b
69
58
69
83
58
59
83
157
16
38
150
150
157
122
170
155d
156
18
127
170
143
194e
266e
       a Sample code shown is the prefix, or first three letters of the Sample Identification Code.
       b Samples collected include all the number of real field samples followed by the number of field blanks in
         parenthesis.  Samples collected and samples reported do not include samples generated and analyzed as
         laboratory QC samples.
       0 Five households returned empty liquid food containers and indicated that they drank water only. These
       samples were disqualified and were not included in the sample count.
       d Sample OAA19745 was lost during the laboratory extraction.
       e The number of urine samples reported is the number of both composited and non-composited samples.

Duplicate data checks
Duplicate data checks were performed to verify that the same analytical data was not
imported into the database twice for a given sample.  The database staff traced the sample
results back to the laboratory record books, the GC/MS sequence logs, and/or the QUAN
reports to confirm that duplicate data was the result of a double import, and not a QA/QC
re-analysis (e.g. duplicate sample or duplicate injection).  Once the duplicate  data was
identified as a double import, the set of results for the sample having the oldest sample
import date were eliminated from the analytical database.  If the duplicate data was
identified as a QA/QC  re-analysis, the proper QCC code was added to the QC_Code data
field, and the data for the first duplicate (only) remained in the Core_Analytical_Results
table, and the data for the first and second duplicates were reported in the
QA_QC_Results table.

Out of range checks
                                                                                    23

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CTEPP OH QA/QC Report                                              02/17/2004


Out-of-range checks were performed to verify that all data for data fields limited to a
codeset did not violate that codeset. For data fields that were limited to a codeset of
values, queries were performed to identify data within those fields that did not belong to,
or "violated", the codeset.  Once identified, the database staff traced the sample results
back to the laboratory record books to identify the transcription error. The data in the
database was corrected, and that correction was documented.

Upper- and lower- concentration checks
Upper- and lower-level concentrations checks were performed on approximately 5% of
the results that were plus or minus three standard deviations from the mean.  Database
queries were performed to identify those calculated results (Resultl and Result2) greater
than or less than three standard deviations from the domain mean.  Five percent of these
data were reviewed again by the data reviewer.  The data reviewer checked the QUAN
report, all the parameters used for the results calculation, and the result calculation itself
to make sure that identification and quantification were performed correctly. If the data
reviewers detected any mis-identification and/or mis-quantification, corrections were
made accordingly.  The TOL approved the corrected data and the database manager made
the changes in the database.  All activities were documented in the laboratory record
books and database importing logbook.

Several additional checks were performed to:

       (1) review the SRS and MSS recoveries data greater than 150% and less than
       50%;
       (2) review the %D data that are greater than 50%;
       (3) add more flag codes to explain these QC  data from items 1 and 2;
       (4) review all nonzero method blanks and field method blanks; and

Calculation Checks
Calculation checks were performed in Excel spreadsheets for selected samples to verify
that the calculations performed on Excel spreadsheet agreed with the calculations
performed on the analytical database.   Hand calculations, using a calculator, were
performed on select data to verify the calculated data agreed with the database calculated
data.

For those data requiring calculation of results, a random subset (approximately 5%) of the
raw data was calculated using an independent calculation source (Excel) for validation.
In addition, hand calculations were  performed on random data for each sample matrix
using a calculator.
                                                                               24

-------
        Appendix E







EPA SAS Program for QA/QC
           E-l

-------
EPA  SAS Program for QA/QC
             *** AD ***•

proc sort data=new.qa_qc_results(where=(QC_Code ='AD1' & QC_Result> .30 )) out=adl;
by matrix report_c;
run;
data ad 1;
      set ad 1;

      if (qc_result > .5) then qc_flag_adl=3; else
      if (qc_result > .3) then qc_flag_adl=2;
run;

             *** T")S ***•

proc sort data=new.qa_qc_results(where=(QC_Code ='DS1' & QC_Result> .30 )) out=dsl;
by matrix report_c;
run;
data dsl;
       set dsl;

       if (qc_result > .5) then qc_flag_dsl=3; else
       if (qc_result > .3) then qc_flag_dsl=2;

       if flagl-HET' then qc_flag_dsl=2;

run;

             title "SRS";
proc sort data=new.qa_qc_results(where=(QC_Code-SRS' & index(flagl,'NSA')=0))
out=qa_qc_results ;
by matrix report_c;
run;
data srs;
       set qa_qc_results;


                                         E-2

-------
       if (.60 <= QC_Result) & (QC_Result <= 1.3) then qc_flag_srs=l;  else
       if(.40<=QC_Result)       then qc_flag_srs=2;                else
       if(.4>QC_Result)   then qc_flag_srs=3;                else
       if (1.3 < QC_Result) & (QC_Result <= 1.5) & Symboll = '<' then qc_flag_srs=l; else
       if (1.3 < QC_Result) & (QC_Result <= 1.5) & Symboll = '=' then qc_flag_srs=2; else
       if (1.5 < QC_Result) & (QC_Result <= 3.0) & Symboll = '<' then qc_flag_srs=2; else
       if (1.5 < QC_Result) & (QC_Result <= 3.0) & Resultl < 1000 then qc_flag_srs=3; else
       if (1.5 < QC_Result) & (QC_Result <= 3.0) & Resultl >= 1000 then qc_flag_srs=2; else
       if(QC_Result>3.0)  then qc_flag_srs=3;
run;
       title "FMB";

proc sort data=new.qa_qc_results(where=(QC_Code ='FMB' & symbol 1="=")) out=FMB;
by Raw_ID matrix report_c;
run;
proc sql;
       create table fmb2 as
       select core.Raw_ID, fmb.sid as fmb_sid, core.sid, core.pid, core.matrix, core.report_c,
       fmb.qc_result, fmb.sad, fmb.raw_data, fmb.resultl, fmb.mdll,
       core.resultl as core_result, core.mdll as core_mdl, core.Diln_Fac as core_df, core.Flagl
as core_flag
       from fmb, core
       where substr(fmb.Raw_ID,l,4) = substr(core.Raw_ID,l,4) & fmb.report_c=core.report_c
& fmb.matrix=core.matrix
       order by core.sid, core.matrix, core.report_c, fmb.resultl;
run;

proc means data=fmb2 noprint;
       by sid matrix report_c;
       var re suit 1;
       output out=counts n=n;
run;

data ones twos many;
       set counts;
       if n=l then output ones;
       else if n=2 then output twos;
       else output many;
run;
                                          E-3

-------
data one2;
       merge ones(in=keepit)
             fmb2;
       by sid matrix report_c;

       if keepit;
run;
data twos;
       merge twos(in=keepit)
             fmb2;
       by sid matrix report_c;

       if keepit;

run;

proc means data=twos noprint;
       by sid matrix report_c;
       var result 1 mdll;
       output out=two2 min=resultl mdll;
run;


data many;
       merge many(in=keepit)
             fmb2;
       by sid matrix report_c;

       if keepit;

run;

proc means data=many noprint;
       by sid matrix report_c;
       var result 1 mdll;
       output out=many2 mean=resultl mdll;
run;
data all;
       set    one2(keep=sid matrix report_c resultl mdll)
             two2
                                          E-4

-------
             many2;
       by sid matrix report_c;

       if last.report_c;

       drop _FREQ	TYPE_;

run;
data fmb;
       merge  all(in=keepit)
              core(keep=sid matrix report_c resultl rename=(resultl=core_result));
       by sid matrix report_c;

       if keepit = 0 then qc_flag_fmb =1; else
       if core_result <= mdll then qc_flag_fmb =1; else
       if (core_result > (8*resultl)) then qc_flag_fmb =1; else
       if ((2*resultl) <= core_result) & (core_result <= (8*resultl)) then qc_flag_fmb =2; else
       if (core_result < (2*resultl)) then qc_flag_fmb =3;
run;
       title "LMB";

proc sort data=new.qa_qc_results(where=(QC_Code='LMB')) out=qa_qc_results ;
       by sid matrix report_c;
run;
proc sql;
       create table 1mb as
       select core.Raw_ID, 1mb.sid as lmb_sid, core.sid, core.pid, core.matrix, core.report_c,
       lmb.qc_result, 1mb.sad, lmb.raw_data, 1mb.resultl, 1mb.mdll,
       core.resultl as core_result, core.mdll as core_mdl
       from qa_qc_results as 1mb, core
       where substr(lmb.Raw_ID,l,4) = substr(core.Raw_ID,l,4) & lmb.report_c=core.report_c
& 1mb.matrix=core.matrix
       order by core.Raw_ID, core.matrix, core.report_c;
run;
data 1mb;
       set 1mb;
       if resultl <= mdll then qc_flag_LMB =1; else
       if core_result <= mdll then qc_flag_LMB =1; else
                                          E-5

-------
       if (core_result > (8*resultl)) then qc_flag_LMB =1; else
       if ((2*resultl) <= core_result) & (core_result <= (8*resultl)) then qc_flag_LMB =2; else
       if (core_result < (2*resultl)) then qc_flag_LMB =3;
run;
       title "MSS";

proc sort data=new.qa_qc_results(where=(QC_Code='MSS' & index(sid,'LRB')=0))
out=qa_qc_results ;
by matrix report_c;
run;
proc format;
       value $ media
 'DAA',   'DAH',   'DAN',   'DCA,   'DCD',   'DCH',   'DCN', TSW ='Wipe'
 'DRW = 'Water'

 'IAA,   'IAN',   'OAA,   'CAN ='Air'

 'IFD' = 'Dust'

 'PUF ='PUF'

 'LFA,   'LFC',   'SFA,   'SFC ='Solid'

 'SOL'='Soil'

 'URA,    'URC' ='Urine';
run;
data MSS;
       set qa_qc_results;
       media=put(matrix,$media.);
       report_c=trim(left(report_c));

run;
proc sql;
       create table mss2 as
       selectmss.no, sp.spike_level
       from mss, qc.spike_level_mss as sp
                                           E-6

-------
      where mss.media = sp.media & trim(left(mss.report_c)) = trim(left(sp.report_c));
run;

data temp;
      merge mss
             mss2(in=hasspike);
      by no;

      if media = 'Urine' & report_c = "IMP (2-isopropyl-6-methyl-4-pyrimidinol)" then
qc_flag_MSS=3; else
      if flagl-SSL' then qc_flag_MSS=3; else
      if (.70 <= QC_Result) & (QC_Result <= 1.3) then qc_flag_MSS=l;      else
      if(.50<=QC_Result)       then qc_flag_MSS=2;                    else
      if (1.3 < QC_Result) & (QC_Result <= 1.5) then qc_flag_MSS=2; else
      if (QC_Result< .50) | (qc_result >1.5) then do;
             if raw_data > 100 then qc_flag_MSS=3; else
             if raw_data < mdll then qc_flag_MSS=3; else
             if raw_data < 20 then qc_flag_MSS=3;  else
             if (raw_data >=20) & (raw_data<=100) & raw_data > (2*spike_level) then
qc_flag_MSS=3; else
             if (raw_data >=20) & (raw_data<=100) & raw_data<= (2*spike_level) then
qc_flag_MSS=2;
      end;

run;
      *** Over all QC Flag***;

data qc_flag;
      length sid $ 50 report_c $ 60;
      merge adl com dsl fmb 1mb mss srs ;
      by SID Matrix  Report_C;

      array flags qc_flag_adl  qc_flag_com qc_flag_dsl qc_flag_fmb qc_flag_lmb
qc_flag_mss qc_flag_srs ;
      do over flags;
             if flags =11 then flags=l;
             if flags
-------
qc_flag_dsl) >= 7 then qc_flag=2;
else qc_flag=0;

run;
                                          E-8

-------
                         Appendix F
Median Indoor Air Sample Concentrations (ng/m3) in the NC and OH
                 Portions of the CTEPP Study
                             F-l

-------
Median Indoor Air Sample Concentrations (ng/m3) in the NC and OH
                      Portions of the CTEPP Study
Analyte
2,4-D (2,4-dichlorophenoxyacetic acid)
3 ,5 ,6-TCP (3,5 ,6-trichloro-2-pyridinol)
alpha-chlordane
benz[a]anthracene
benzo[a]pyrene
benzo [b] fluoranthene
benzo[e]pyrene
benzo[g,h,i]perylene
benzo [k] fluoranthene
benzylbutylphthalate
bisphenol-A
chlorpyrifos
chrysene
cis-permethrin
cyfluthrin
di-n-butylphthalate
diazinon
dibenzo[a,h]anthracene
gamma-chlordane
heptachlor
indeno[ 1 ,2,3-c,d]pyrene
p,p'-DDE
PCB44
PCB52
PCB95
PCB 101
pentachlorophenol
trans-Dermethrin
Median Indoor Air
Concentration (ng/m3)
NC
0.166
1.77
0.840
0.064
0.080
0.130
0.067
0.120
0.064
40.57
1.595
6.070
0.100
0.405
0.615
239.69
2.025
0.064
1.470
6.590
0.090
0.064
0.043
0.530
0.090
0.060
1.450
0.270
OH
0.127
0.650
0.230
0.064
0.064
0.064
0.064
0.064
0.064
24.78
0.980
1.750
0.064
0.275
0.615
255.40
0.970
0.064
0.340
0.064
0.064
0.064
0.028
0.440
0.110
0.090
2.000
0.236
Note: The median indoor air concentrations in this table were used as estimates for the indoor air
concentrations for all study participants when not in either a day care center or home environment.
                                     F-2

-------
                                   Appendix G







Algorithms for Estimating Daily Ingestion Rate of Dust and Soil in Children Participants
                                       G-l

-------
Algorithms for Estimating Daily Ingestion Rate of Dust and Soil in Children Participants

       Daily ingestion rates of dust and soil were obtained from information found in the EPA
Exposure Factors Handbook. For all participating adult caregivers, the ingestion rates used in the
calculation were Md=25 mg/day and Ms=50 mg/day. For participating children, ingestion rates
were assigned by placing the children into one of three groups (Groups A, B, or C) based upon
their potential for soil ingestion, and then again into one of these three groups based upon their
potential for dust ingestion.

For dust ingestion. the following algorithm was used to assign children to Groups A, B, or C:

1.      Responses were obtained from the following questions on Form 04 (parent pre-
       monitoring questionnaire):
             Question C5: How often did [the child] play with sand or dirt?
       -     Question C6: Which of the following have you seen your child eat: dirt, sand,
             snow
2.      Based on the responses to these two questions, each participating child was placed into
       Group A, B, or C with regard to dust ingestion if any of the following was satisfied:

       Group A: -  Response to C5 was "most of the time"
                -  Response to C5 was "sometimes,"  and response to C6 was "dirt," "soil,"
                    and/or "snow"
       Group B: -  Response to C5 was "sometimes,"  and response to C6 did not include
                    "dirt," "soil," or "snow"
                -  Response to C5 was "rarely  or almost never," and response to C6 was
                    "dirt," "soil," and/or "snow"
       Group C: -  Response to C5 was neither  "most of the time" or "sometimes," and
                    response to C6 did not include "dirt," "soil," or "snow"

For soil ingestion. the following algorithm was used to assign children to Groups A, B, or C:

1.      Responses were obtained from the following questions on Form 04 (parent pre-
       monitoring questionnaire):
       -     Question C12: Did your child use a pacifier in the past month?
             Question C13a: In the past month, did [your child] suck or chew his/her
             thumb/fingers?
             Question C13b: In the past month, did [your child] suck or chew his/her toe/foot?
       -     Question C16: Did [your child] ever put his/her mouth on the floor and lick the
             floor?
       -     Question C21: Is your child currently teething?
       -     Question C22: How often did  [your child] put toys in his/her  mouth?
       -     Question C23: Did [your child] put  any things other than toys or food in his/her
             mouth?
                                          G-2

-------
2.     Based on the responses to these questions, each participating child was placed into Group
      A, B, or C with regard to soil ingestion if any of the following was satisfied:

      Group A:  -   Response to either C12 or C21 was "yes"
                -   Responses to C12 and C21 were both "no," response to C22 was
                    "frequently," and at least one "yes" response was given among questions
                    C13a, C13b, C16, and C23
                -   Responses to C12 and C21 were both "no," response to C22 was
                    "sometimes," and at least three "yes" responses were given among
                    questions C13a, C13b, C16, and C23
      Group B:  -   Responses to C12 and C21 were both "no," response to C22 was
                    "sometimes," and either one or two "yes" responses were given among
                    questions C13a, C13b, C16, and C23
                -   Responses to C12 and C21 were both "no," response to C22 was
                    "frequently," and no "yes" responses were given among questions C13a,
                    C13b, C16, andC23
                -   Responses to C12 and C21 were both "no," response to C22 was not
                    "frequently" or "sometimes," and at least three "yes" responses were
                    given among questions C13a, C13b, C16, and C23
      Group C:  -   Responses to C12 and C21 were both "no," response to C22 was not
                    "frequently" or "sometimes," and no more than two "yes" responses were
                    given among questions C13a, C13b, C16, and C23
                -   Responses to C12 and C21 were both "no," response to C22 was
                    "sometimes," and no "yes" responses were given among questions C13a,
                    C13b, C16, andC23

Once a participating child was placed into either Groups A, B, and C for soil ingestion and for
dust ingestion, then for both dust and soil, the daily ingestion rates were assigned as follows:

•     Children in Group A: Daily ingestion rate =100 mg/day
•     Children in Group B: Daily ingestion rate = 50 mg/day
•     Children in Group C: Daily ingestion rate = 25 mg/day
                                         G-3

-------

-------
                Appendix H
Percentages of NC and OH Multimedia Samples
  with Pollutant Levels At or Above the MQL
                    H-l

-------
H-2

-------
Table H-l   Percentages of NC Samples With Pollutant and Metabolite Levels At or
            Above the MQL in Multimedia and Urine Samples"
Pollutant/Metabolite b
Percentage of Results At or Above the MQL in Multimedia and Urine Samples
INDOORS
Indoor
Air
Dust
OUTDOORS
Outdoor
Air
Soil
PERSONAL
Dermal
Wipe
Solid
Food
Liquid
Food || Urine
OP Pesticides and Metabolite
Chlorpyrifos
Diazinon
3,5,6-TCP
100
98
95
99
81
97
62
31
59
14
14
53
77
35
87
53
8.6
96
8.1
0.68
13
-c
-
84
OC Pesticides
Aldrin
alpha-Chlordane
gamma-Chlordane
p,p '-DDE
p,p '-DDT
Dieldrin
Endrin
Heptachlor
Lindane
Pentachloronitrobenzene
41
91
95
18
28
40
34
93
14
12
15
82
91
34
38
45
18
42
13
2.8
6.4
27
39
0.0
11
12
41
60
11
2.9
0.0
21
23
9.2
18
13
4.2
3.5
3.5
0.0
3.1
33
46
3.1
6.7
4.9
2.2
19
2.2
0.45
2.0
3.9
7.2
52
3.3
2.0
0.65
12
7.2
0.65
0.0
0.0
0.0
6.1
2.0
0.0
0.0
0.0
1.4
0.68
-
-
-
-
-
-
-
-
-
-
Pyrethroid Pesticides
Cyfluthrin
c«-Permethrin
/r
-------
Table H-l      Percentages of NC Samples With Pollutant and Metabolite Levels At or
                  Above the MQL in Multimedia and Urine Samples (cont.)
Pollutant/Metabolite b
Percentage of Results At or Above the MQL in Multimedia and Urine Samples
INDOORS
Indoor
Air
Dust
OUTDOORS
Outdoor
Air
Soil
PERSONAL
Dermal
Wipe
Solid
Food
Liquid
Food || Urine
Phthalates
Benzylbutylphthalate || 24
Di-n-butylphthalate | 99
100 I! 5.7
100 1 28
27 I! 43
21 | 78
2.4
23
3.6 I!
23 1
Phenols
Bisphenol-A
Nonylphenol
Pentachlorophenol
48
6.1
96
12
0.0
88
13
1.4
91
2.2
0.96
22
91
0.45
22
71
0.0
3.2
30
1.3
0.37
-
-
46
PCBs
PCB44
PCB52
PCB70
PCB77
PCB95
PCB 101
PCB 105
PCB 110
PCB 118
PCB 138
PCB 153
PCB 180
46
91
35
0.0
52
36
4.7
35
18
9.5
17
2.0
15
30
13
0.0
18
24
4.3
30
21
12
21
9.2
16
49
5.7
0.0
14
11
0.0
7.9
4.3
1.4
1.4
0.0
1.4
2.1
1.4
0.0
1.4
2.1
2.1
2.8
2.1
7.0
7.0
4.9
0.45
3.1
0.89
0.0
2.2
3.6
0.45
5.8
2.2
0.45
1.3
0.89
0.0
3.3
0.0
0.0
0.66
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
-
-
-
-
-
-
-
-
-
-
-
-
PAH Metabolites Measured in Urine Only
l-hydroxybenz[a]anthracene ||
3-hydroxychrysene ||
»--
-
«--
-
-
-
»5.2
1.1
a The percentages were calculated using results from individual samples. Multiple samples for the same person or room were considered as
individual samples. The MQL is assumed to equal two times the MDL except as specified in Section 9.2. Cells corresponding to pollutants
having at least 50% of samples above the MQL in the specified matrix are shaded in gray.
b In addition to the pollutants represented in this table, atrazine was measured in drinking water samples. Twenty-two percent of NC drinking
water samples had atrazine levels at or above the MQL.
0 A dash indicates that the pollutant was not measured in the specified matrix.
                                                       H-4

-------
Table H-2   Percentages of OH Samples With Pollutant and Metabolite Levels At or
            Above the MQL in Multimedia and Urine Samples"
Pollutant/Metabolite b
Percentage of Results At or Above the MQL in Multimedia and Urine Samples
INDOORS
Indoor
Air
Dust
OUTDOORS
Outdoor
Air
Soil
PERSONAL
Dermal
Wipe
Solid
Food
Liquid
Food || Urine
OP Pesticides and Metabolites
Chlorpyrifos
Diazinon
IMP
3,5,6-TCP
99
97
94
96
97
90
77
99
59
47
72
62
34
24
27
64
56
26
9.8
71
57
9.1
72
97
5.8
0.0
13
18
c
-
d
80
OC Pesticides
Aldrin
alpha-Chlordane
gamma-Chlordane
p,p '-DDE
p,p '-DDT
Dieldrin
Endrin
Heptachlor
Lindane
Pentachloronitrobenzene
2.7
71
83
22
18
11
11
34
4.1
11
3.5
66
69
43
38
21
7.0
5.6
11
0.70
1.4
27
31
0.0
0.0
5.6
19
17
3.5
2.8
2.1
38
31
30
27
17
2.8
2.1
0.0
0.0
0.45
17
17
0.45
3.1
0.45
2.7
1.8
1.3
0.45
0.65
0.65
0.0
55
4.5
8.4
1.3
6.5
3.2
1.9
0.65
0.0
0.0
3.9
1.9
0.0
0.0
1.3
1.3
0.0
-
-
-
-
-
-
-
-
-
-
Pyrethroid Pesticides and Metabolite
Cyfluthrin
cw-Permethrin
/r
-------
Table H-2     Percentages of OH Samples With Pollutant and Metabolite Levels At or
                  Above the MQL in Multimedia and Urine Samples (cont.)
Pollutant/Metabolite b
Percentage of Results At or Above the MQL in Multimedia and Urine Samples
INDOORS
Indoor
Air
Dust
OUTDOORS
Outdoor
Air
Soil
PERSONAL
Dermal
Wipe
Solid
Food
Liquid
Food || Urine
Phthalates
Benzylbutylphthalate || 16
Di-n-butylphthalate | 96
100 I! 4.2
100 1 33
36 I! 28
47 1 30
48
21
4.1 I! -
3.3 1 -
Phenols
Bisphenol-A
Nonylphenol
Pentachlorophenol
24
0.0
87
9.4
3.6
89
6.7
0.0
55
0.71
1.2
47
98
0.44
27
81
0.0
5.3
31
0.0
0.72
-
-
79
PCBs
PCB44
PCB52
PCB70
PCB77
PCB95
PCB 101
PCB 105
PCB 110
PCB 118
PCB 138
PCB 153
PCB 180
31
88
35
0.0
63
55
5.4
44
22
9.5
17
2.7
18
38
17
0.0
26
32
13
40
30
20
30
9.1
15
66
14
0.0
35
25
2.1
20
8.5
2.8
1.4
0.0
14
15
14
0.70
18
20
15
25
20
25
25
13
0.45
2.7
1.8
0.0
1.8
3.6
0.89
4.5
2.2
0.45
0.45
0.45
0.0
3.2
0.0
0.0
0.0
0.65
0.0
0.65
0.0
0.0
0.0
0.0
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
PAH Metabolites Measured in Urine Only
1 -hy droxy benz[a]anthracene
3 -hy droxy benz [a] anthracene
3-hy droxy benzo[a]pyrene
3-hy droxy chrysene
6-hy droxy chrysene
6-hydroxy indeno[l,2,3-«/]pyrene
1 -hy droxypyrene
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
4.3
0.68
0.0
0.45
0.0
0.0
40
a The percentages were calculated using results from individual samples. Multiple samples for the same person or room were considered as
individual samples. The MQL is assumed to equal two times the MDL except as specified in Section 9.2.  Cells corresponding to pollutants
having at least 50% of samples above the MQL in the specified matrix are shaded in gray.
b In addition to the pollutants represented in this table, atrazine was measured in drinking water samples. Fifty-seven percent of OH drinking
water samples had atrazine levels at or above the MQL.
0 A dash indicates that the pollutant was not measured in the specified matrix.
d Low recovery (<10%) of IMP was observed in matrix spikes, and therefore, IMP was not quantifiable in urine samples.
                                                        H-6

-------
Table H-3   Percentages of NC and OH Samples With With Pollutant and Metabolite
            Levels At or Above the MQL in Surface Samplesa
Pollutant/Metabolite
Percentage of Results At or Above the MQL in Samples Collected From
Homes After Recent Pesticide Applications
North Carolina
Hard Floor
Surface Wipe
Food Prep.
Surface Wipe
Trans.
Residue (PUF)
Ohio
Hard Floor
Surface Wipe
Food Prep.
Surface Wipe
Trans.
Residue (PUF)
OP Pesticides and Metabolites
Chlorpyrifos
Diazinon
IMP
3,5,6-TCP
88
44
__b
100
83
56
-
-
94
61
-
-
54
19
25
33
38
23
0.0
0.0
62
46
0.0
33
OC Pesticides
Aldrin
alpha-Chlordane
gararaa-Chlordane
p,p '-DDE
p,p '-DDT
Dieldrin
Endrin
Heptachlor
Lindane
Pentachloronitrobenzene
9.4
44
44
9.4
19
25
13
34
6.3
0.0
5.6
44
50
5.6
17
17
28
33
0.0
0.0
11
28
44
17
28
22
11
28
28
0.0
3.8
15
15
7.7
19
3.8
0.0
3.8
0.0
0.0
0.0
15
15
0.0
7.7
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
23
7.7
0.0
0.0
0.0
Pyrethroid Pesticides
Cyfluthrin
c«-Permethrin
/r
-------
Table H-3     Percentages of NC and OH Samples With With Pollutant and Metabolite
                 Levels At or Above the MQL in Surface Samplesa (cont.)
Pollutant/Metabolite
Percentage of Results At or Above the MQL in Samples Collected From
Homes After Recent Pesticide Applications
North Carolina
Hard Floor
Surface Wipe
Food Prep.
Surface Wipe
Trans.
Residue (PUF)
Ohio
Hard Floor
Surface Wipe
Food Prep.
Surface Wipe
Trans.
Residue (PUF)
Phthalates
Benzylbutylphthalate || 97
Di-n-butylphthalate | 100
44
72
100 I! 58
100 | 62
31
77
100
100
Phenols
Bisphenol-A
Nonylphenol
Pentachlorophenol
66
0.0
36
83
0.0
-
94
6.3
-
96
0.0
8.3
85
0.0
0.0
71
8.3
33
PCBs
PCB44
PCB52
PCB70
PCB77
PCB95
PCB 101
PCB 105
PCB 110
PCB 118
PCB 138
PCB 153
PCB 180
3.1
13
6.3
0.0
9.4
6.3
0.0
9.4
9.4
3.1
3.1
0.0
11
17
11
0.0
11
11
0.0
11
5.6
0.0
5.6
0.0
11
6.3
11
0.0
13
20
22
10
33
0.0
11
5.6
0.0
0.0
3.8
0.0
0.0
3.8
0.0
3.8
3.8
0.0
3.8
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
15
42
23
0.0
31
31
7.7
23
23
0.0
23
0.0
a The percentages were calculated using results from individual samples. Multiple samples for the same person or room were considered as
individual samples. The MQL is assumed to equal two times the MDL except as specified in Section 9.2. Cells corresponding to pollutants
having at least 50% of samples above the MQL in the specified matrix are shaded in gray.
b A dash indicates that the pollutant was not measured in the specified matrix.
                                                     H-8

-------
                         Appendix I
Descriptive Statistics of CTEPP Pollutant/Metabolite Measurements
                  in NC Multimedia Samples
                             l-l

-------
1-2

-------
This appendix contains tables of descriptive statistics of NC multimedia data for the following pollutants
and metabolites:
Pollutant/Metabolite
Aldrin
Atrazine
Benz[a]anthracene
Benzo[£>]fluoranthene
Benzo[/(]fluoranthene
Benzo[g/?/]perylene
Benzo[a]pyrene
Benzo[e]pyrene
Benzylbutylphthalate
Bisphenol-A
a/p/?a-Chlordane
gamma-Chlordane
Chlorpyrifos
Chrysene
Cyfluthrin
Diazinon
Dibenzo[a,/?]anthracene
Di-n-butylphthalate
Dicamba
p,p'-DDE
p,p'-DDT
2,4-D
Dieldrin
Table Numbers
Tables l-1a,
Tables l-2a,
Tables l-3a,
Tables l-4a,
Tables l-5a,
Tables l-6a,
Tables l-7a,
Tables l-8a,
Tables l-9a,
Tables
Tables
Tables
Tables
Tables
Tables
Tables
Tables
Tables
Tables
Tables
Tables
Tables
Tables
-10a,
-11 a,
-12a,
-13a,
-14a,
-15a,
-16a,
-17a,
-18a,
-19a,
-20a,
-21 a,
-22a,
-23a,
-1b
-2b
-3b
-4b
-5b
-6b
-7b
-8b
-9b
-10b
-11b
-12b
-13b
-14b
-15b
-16b
-17b
-18b
-19b
-20b
-21 b
-22b
-23b
Pollutant/Metabolite
Endrin
Heptachlor
lndeno[1 ,2,3-cd]pyrene
Lindane
Nonylphenol
Pentachloronitrobenzene
Pentachlorophenol
c/s-Permethrin
frans-Permethrin
PCS 44
PCB52
PCS 70
PCB77
PCS 95
PCB101
PCB 105
PCB 110
PCS 118
PCB 138
PCB 153
PCB 180
2,4,5-T
3,5,6-TCP
Table Numbers
Tables
Tables
Tables
Tables
Tables
Tables
Tables
Tables
Tables
Tables
Tables
Tables
Tables
Tables
Tables
Tables
-24a,
-25a,
-26a,
-27a,
-28a,
-29a,
-30a,
-31a,
-32a,
-33a,
-34a,
-35a,
-36a,
-37a,
-38a,
-39a,
-24b
-25b
-26b
-27b
-28b
-29b
-30b
-31 b
-32b
-33b
-34b
-35b
-36b
-37b
-38b
-39b
Tables l-40a, l-40b
Tables l-41a, 1-41 b
Tables l-42a, l-42b
Tables l-43a, l-43b
Tables l-44a, l-44b
Tables l-45a, l-45b
Tables l-46a, l-46b
For each media type, descriptive statistics are presented separately for the following four groups of
samples:
•      Samples collected at the homes of study participants
       o      Samples collected at the homes of stay-at-home children only
       o      Samples collected at the homes of day-care children only
•      Samples collected at participating day care centers
                                               1-3

-------
Table 1-1 a.     Aldrin (309-00-2): Summaries of concentrations in NC multimedia samples
                 collected from the homes and day care centers of preschool children who
                 stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
20
121
66
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
129
66
63
24



126
64
62
22



% Detected
38.3
36.4
40.3
55.0
9.4
7.7
11.3
0.0
0.0
0.0
0.0
0.0
15.7
13.6
18.2
15.0
15.7
13.6
18.2
15.0
10.7
0.0
16.7
100.0
5.6
0.0
12.5

11.1
20.0
0.0

1.0
0.0
3.3
3.2
5.2
4.5
6.5
2.3
0.0
4.8
4.2



0.0
0.0
0.0
0.0



Arithmetic Mean
-
-
-
5.37
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
22.1
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Std. Dev.
-
-
-
9.87
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Geometric
Mean
-
-
-
0.638
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
22.1
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Log Std. Dev.
-
-
-
2.42
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



* Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected. Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                      1-4

-------
Table 1-1 b.    Aldrin (309-00-2):  Range of Reported Concentrations in NC multimedia
                samples collected from the homes and day care centers of preschool
                children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
20
121
66
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
129
66
63
24



126
64
62
22



Minimum

-------
Table l-2a.    Atrazine (1912-24-9): Summaries of concentrations in NC multimedia
                samples collected from the homes and day care centers of preschool
                children who stay at home or attend day care during the day.a
Medium
Drinking
Water
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
N
124
64
60
12
% Detected
37.1
23.4
51.7
41.7
Arithmetic Mean
-
-
0.018
-
Std. Dev.
-
-
0.018
-
Geometric
Mean
-
-
0.013
-
Log Std. Dev.
-
-
0.719
-
a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Means and standard deviations are not reported
when the percentage of detected results is below 50%.
                                                    1-6

-------
Table l-2b.     Atrazine (1912-24-9):  Range of Reported Concentrations in NC multimedia
                 samples collected from the  homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Drinking
Water
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
N
124
64
60
12
Minimum

-------
Table l-3a.     Benzralanthracene (56-55-3): Summaries of concentrations in NC
                 multimedia samples collected from the homes and day care centers of
                 preschool children who stay at home or attend day care during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - atdaycare
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
128
66
62
20
127
65
62
13
128
65
63
13
118
63
55
20
118
63
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
128
66
62
24



127
65
62
24



% Detected
49.2
51.5
46.8
40.0
51.2
58.5
43.5
69.2
72.7
76.9
68.3
76.9
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
75.0
60.0
83.3
100.0
33.3
30.0
37.5

94.4
100.0
87.5

38.5
40.9
33.3
32.3
40.2
43.9
32.3
32.0
36.4
27.4
25.0



1.6
1.5
1.6
0.0



Arithmetic Mean
-
0.255
-
-
0.233
0.238
-
0.127
42.0
17.8
67.0
20.4
343
248
453
1,180
652
334
1,020
2,450
429
11.4
661
7.24
-
-
-

213
197
234

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Std. Dev.
-
0.452
-
-
0.600
0.467
-
0.174
186
82.9
250
46.5
886
455
1,200
4,160
2,580
537
3,720
4,840
1,770
9.11
2,200

-
-
-

313
194
435

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Geometric
Mean
-
0.135
-
-
0.117
0.132
-
0.079
2.26
1.92
2.66
4.43
135
132
137
237
145
133
160
1,050
25.0
9.04
43.9
7.24
-
-
-

87.8
117
61.6

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Log Std. Dev.
-
0.970
-
-
0.917
0.917
-
0.859
2.00
1.72
2.26
1.87
1.14
0.991
1.30
1.27
1.53
1.51
1.55
1.21
1.84
0.684
2.04

-
-
-

1.55
1.19
1.93

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



* Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations.  This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     1-8

-------
Table l-3b.    Benzralanthracene (56-55-3):  Range of Reported Concentrations in NC
                multimedia samples collected from the homes and day care centers of
                preschool children who stay at home or attend day care during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
128
66
62
20
127
65
62
13
128
65
63
13
118
63
55
20
118
63
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
128
66
62
24



127
65
62
24



Minimum

-------
Table l-4a.     BenzoHblfluoranthene (205-99-2): Summaries of concentrations in NC
                 multimedia samples collected from the homes and day care centers of
                 preschool children who stay at home or attend day care during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - atdaycare
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
128
66
62
20
127
65
62
13
128
65
63
13
118
63
55
20
118
63
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
128
66
62
24



127
65
62
24



% Detected
60.2
57.6
62.9
65.0
67.7
69.2
66.1
69.2
77.3
76.9
77.8
76.9
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
75.0
50.0
88.9
100.0
33.3
40.0
25.0

66.7
60.0
75.0

28.1
27.3
30.0
48.4
28.9
25.8
35.5
32.8
36.4
29.0
25.0



2.4
0.0
4.8
0.0



Arithmetic Mean
0.276
0.264
0.288
0.188
0.366
0.416
0.313
0.259
61.2
28.4
95.2
38.9
947
549
1,400
2,330
1,840
854
2,960
6,590
611
21.8
938
34.8
-
-
-

88.9
97.4
78.4

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Std. Dev.
0.326
0.338
0.316
0.189
0.463
0.508
0.409
0.357
237
106
318
90.1
2,670
922
3,750
7,670
7,360
1,260
10,600
14,400
2,470
23.2
3,060

-
-
-

131
162
87.1

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Geometric
Mean
0.161
0.156
0.168
0.132
0.200
0.226
0.176
0.138
3.73
3.27
4.28
7.03
353
325
387
575
380
328
451
2,550
48.7
12.8
102
34.8
-
-
-

24.8
20.8
30.8

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Log Std. Dev.
1.00
0.973
1.04
0.817
1.09
1.12
1.05
1.08
2.13
1.91
2.34
2.10
1.15
0.947
1.35
1.22
1.56
1.56
1.55
1.25
1.92
1.10
1.90

-
-
-

1.81
1.96
1.72

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



* Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                    1-10

-------
Table l-4b.    BenzoHblfluoranthene (205-99-2):  Range of Reported Concentrations in NC
                multimedia samples collected from the homes and day care centers of
                preschool children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
128
66
62
20
127
65
62
13
128
65
63
13
118
63
55
20
118
63
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
128
66
62
24



127
65
62
24



Minimum

-------
Table l-5a.     Benzo|7clfluoranthene (207-08-9): Summaries of concentrations in NC
                 multimedia samples collected from the homes and day care centers of
                 preschool children who stay at home or attend day care during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - atdaycare
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
128
66
62
20
127
65
62
13
128
65
63
13
118
63
55
20
118
63
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
128
66
62
24



127
65
62
24



% Detected
43.8
39.4
48.4
40.0
51.2
55.4
46.8
46.2
70.3
73.8
66.7
76.9
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
71.4
40.0
88.9
100.0
27.8
30.0
25.0

66.7
60.0
75.0

27.1
25.8
30.0
48.4
22.7
19.7
29.0
17.2
19.7
14.5
12.5



0.0
0.0
0.0
0.0



Arithmetic Mean
-
-
-
-
0.142
0.170
-
-
25.8
13.8
38.2
14.3
327
208
464
817
673
293
1,110
2,170
229
-
349
8.07
-
-
-

30.5
30.1
30.9

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Std. Dev.
-
-
-
-
0.162
0.202
-
-
107
64.0
138
31.7
914
363
1,270
2,730
2,880
431
4,160
4,520
931
-
1,150

-
-
-

39.4
47.5
29.7

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Geometric
Mean
-
-
-
-
0.104
0.118
-
-
1.77
1.58
1.99
3.48
123
118
129
192
132
119
150
852
20.2
-
32.5
8.07
-
-
-

13.1
11.1
16.1

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Log Std. Dev.
-
-
-
-
0.705
0.766
-
-
1.87
1.66
2.06
1.75
1.14
0.962
1.32
1.25
1.56
1.51
1.61
1.24
1.66
-
1.84

-
-
-

1.38
1.44
1.37

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                    1-12

-------
Table l-5b.    Benzo|7clfluoranthene (207-08-9):  Range of Reported Concentrations in NC
                multimedia samples collected from the homes and day care centers of
                preschool children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
128
66
62
20
127
65
62
13
128
65
63
13
118
63
55
20
118
63
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
128
66
62
24



127
65
62
24



Minimum

-------
Table l-6a.     Benzorqfo/lperylene (191-24-2):  Summaries of concentrations in NC
                 multimedia samples collected from the homes and day care centers of
                 preschool children who stay at home or attend day care during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
128
66
62
20
127
65
62
13
128
65
63
13
118
63
55
20
118
63
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
128
66
62
24



127
65
62
24



% Detected
62.5
59.1
66.1
65.0
63.8
69.2
58.1
69.2
73.4
73.8
73.0
76.9
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
85.7
70.0
94.4
100.0
16.7
20.0
12.5

66.7
70.0
62.5

44.8
39.4
56.7
61.3
36.1
28.8
51.6
1.6
1.5
1.6
0.0



0.0
0.0
0.0
0.0



Arithmetic Mean
0.243
0.259
0.225
0.124
0.274
0.339
0.206
0.182
30.9
16.1
46.1
18.9
481
309
679
1,020
994
453
1,610
3,520
297
13.4
455
12.1
-
-
-

25.2
27.1
22.8

-
-
175
275
-
-
28.0
-
-
-
-



-
-
-
-



Std. Dev.
0.298
0.354
0.225
0.080
0.355
0.442
0.215
0.253
118
73.0
150
45.3
1,320
462
1,850
3,020
4,080
608
5,910
7,270
1,270
12.7
1,570

-
-
-

36.2
38.2
36.1

-
-
526
830
-
-
22.9
-
-
-
-



-
-
-
-



Geometric
Mean
0.150
0.149
0.151
0.103
0.160
0.187
0.136
0.109
2.32
2.02
2.69
4.06
197
197
199
325
213
198
231
1,440
25.3
10.1
42.2
12.1
-
-
-

12.2
14.1
10.1

-
-
61.0
66.5
-
-
21.9
-
-
-
-



-
-
-
-



Log Std. Dev.
0.927
0.969
0.887
0.622
0.987
1.05
0.894
0.934
1.93
1.70
2.15
1.81
1.07
0.879
1.27
1.15
1.54
1.48
1.60
1.21
1.62
0.731
1.76

-
-
-

1.22
1.21
1.29

-
-
1.11
1.23
-
-
0.668
-
-
-
-



-
-
-
-



* Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                    1-14

-------
Table l-6b.    Benzorqfo/lperylene (191-24-2):  Range of Reported Concentrations in NC
                multimedia samples collected from the homes and day care centers of
                preschool children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
128
66
62
20
127
65
62
13
128
65
63
13
118
63
55
20
118
63
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
128
66
62
24



127
65
62
24



Minimum

-------
Table l-7a.     Benzolalpyrene (50-32-8): Summaries of concentrations in NC multimedia
                 samples collected from the homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - atdaycare
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
128
66
62
20
127
65
62
13
128
65
63
13
118
63
55
20
118
63
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
128
66
62
24



127
65
62
24



% Detected
50.8
47.0
54.8
45.0
53.5
56.9
50.0
53.8
74.2
73.8
74.6
76.9
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
78.6
60.0
88.9
100.0
16.7
20.0
12.5

61.1
50.0
75.0

25.0
21.2
33.3
41.9
19.6
15.2
29.0
18.0
24.2
11.3
8.3



0.0
0.0
0.0
0.0



Arithmetic Mean
0.216
-
0.224
-
0.179
0.218
0.139
0.124
42.8
22.0
64.2
22.6
509
318
727
1,270
979
434
1,600
3,330
407
13.4
626
7.86
-
-
-

60.3
59.0
62.0

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Std. Dev.
0.263
-
0.264
-
0.259
0.321
0.165
0.161
177
111
225
53.9
1,430
485
2,020
4,200
4,080
596
5,910
6,860
1,720
13.1
2,140

-
-
-

113
136
83.8

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Geometric
Mean
0.132
-
0.138
-
0.115
0.132
0.100
0.081
2.59
2.23
3.02
4.80
197
193
201
318
212
195
234
1,410
24.8
9.82
41.5
7.86
-
-
-

14.0
11.1
18.7

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Log Std. Dev.
0.922
-
0.946
-
0.818
0.892
0.711
0.823
1.99
1.76
2.22
1.87
1.12
0.933
1.31
1.22
1.50
1.46
1.55
1.18
1.76
0.780
1.95

-
-
-

1.71
1.72
1.77

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



* Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations.  This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                    1-16

-------
Table l-7b.    Benzolalpyrene (50-32-8): Range of Reported Concentrations in NC
                multimedia samples collected from the homes and day care centers of
                preschool children who stay at home or attend day care during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
128
66
62
20
127
65
62
13
128
65
63
13
118
63
55
20
118
63
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
128
66
62
24



127
65
62
24



Minimum

-------
Table l-8a.     Benzorelpyrene (192-97-2): Summaries of concentrations in NC multimedia
                 samples collected from the homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - atdaycare
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
128
66
62
20
127
65
62
13
128
65
63
13
118
63
55
20
118
63
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
128
66
62
24



127
65
62
24



% Detected
50.0
47.0
53.2
45.0
55.9
60.0
51.6
61.5
75.0
75.4
74.6
76.9
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
85.7
70.0
94.4
100.0
16.7
20.0
12.5

66.7
60.0
75.0

30.2
28.8
33.3
41.9
26.8
19.7
41.9
25.0
33.3
16.1
16.7



3.1
1.5
4.8
4.2



Arithmetic Mean
0.141
-
0.150
-
0.182
0.214
0.148
0.121
32.8
16.7
49.4
19.0
503
310
723
1,190
1,030
461
1,670
3,480
383
15.5
588
14.9
-
-
-

40.7
35.5
47.1

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Std. Dev.
0.128
-
0.141
-
0.203
0.235
0.158
0.139
131
77.7
168
44.4
1,430
494
2,010
3,830
4,150
658
6,000
7,210
1,700
16.0
2,110

-
-
-

57.8
64.3
52.2

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Geometric
Mean
0.107
-
0.112
-
0.124
0.143
0.107
0.084
2.44
2.06
2.91
4.16
196
190
203
317
211
191
237
1,410
26.9
11.3
43.7
14.9
-
-
-

15.5
12.5
20.5

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Log Std. Dev.
0.691
-
0.735
-
0.813
0.855
0.745
0.788
1.93
1.68
2.15
1.82
1.10
0.901
1.29
1.20
1.55
1.50
1.61
1.21
1.68
0.781
1.86

-
-
-

1.47
1.46
1.52

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



* Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                    1-18

-------
Table l-8b.    Benzorelpyrene (192-97-2):  Range of Reported Concentrations in NC
                multimedia samples collected from the homes and day care centers of
                preschool children who stay at home or attend day care during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
128
66
62
20
127
65
62
13
128
65
63
13
118
63
55
20
118
63
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
128
66
62
24



127
65
62
24



Minimum

-------
Table l-9a.     Benzylbutylphthalate (85-68-7): Summaries of concentrations in NC
                 multimedia samples collected from the homes and day care centers of
                 preschool children who stay at home or attend day care during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
128
66
62
20
127
65
62
13
127
65
62
12
119
64
55
20
119
64
55
20
28
10
18
1
18
10
8

8
5
3

96
66
30
31
97
66
31
107
53
54
18



116
60
56
22



% Detected
34.4
31.8
37.1
35.0
6.3
7.7
4.8
7.7
32.3
21.5
43.5
50.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
96.4
100.0
94.4
100.0
55.6
50.0
62.5

100.0
100.0
100.0

60.4
50.0
83.3
48.4
55.7
59.1
48.4
2.8
3.8
1.9
5.6



2.6
3.3
1.8
13.6



Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
101
38,200
35,900
40,800
66,100
105,000
89,100
123,000
575,000
88,100
68,600
99,000
160,000
6,560
5,430
7,970

49,300
42,400
60,800

30,900
29,000
34,900
-
13,300
12,500
-
-
-
-
-



-
-
-
-



Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
190
50,600
46,000
55,900
67,000
270,000
243,000
299,000
902,000
106,000
107,000
107,000

7,370
6,510
8,560

51 ,800
44,900
71 ,000

42,000
40,700
45,100
-
28,200
15,100
-
-
-
-
-



-
-
-
-



Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
30.2
20,600
19,500
22,000
43,700
20,700
17,200
25,700
194,000
37,100
27,600
43,700
160,000
3,170
2,730
3,830

22,400
20,800
25,200

16,100
14,700
19,700
-
6,490
7,180
-
-
-
-
-



-
-
-
-



Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
1.55
1.09
1.09
1.09
0.980
1.81
1.77
1.85
1.69
1.51
1.40
1.58

1.27
1.24
1.38

1.55
1.49
1.98

1.10
1.12
1.04
-
1.06
1.04
-
-
-
-
-



-
-
-
-



* Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations.  This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                    1-20

-------
Table l-9b.    Benzylbutylphthalate (85-68-7):  Range of Reported Concentrations in NC
                multimedia samples collected from the homes and day care centers of
                preschool children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
128
66
62
20
127
65
62
13
127
65
62
12
119
64
55
20
119
64
55
20
28
10
18
1
18
10
8

8
5
3

96
66
30
31
97
66
31
107
53
54
18



116
60
56
22



Minimum

-------
Table 1-1 Oa.   Bisphenol-A (80-05-7): Summaries of concentrations in NC multimedia
                 samples collected from the homes and day care centers  of preschool
                 children who stay at home or attend  day care during the  day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - atdaycare
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
128
66
62
20
127
65
62
13
126
64
62
12
119
65
54
19
119
65
54
19
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
129
66
63
24



127
65
62
24



% Detected
68.0
74.2
61.3
45.0
30.7
33.8
27.4
38.5
3.2
3.1
3.2
0.0
25.2
18.5
33.3
52.6
25.2
18.5
33.3
52.6
82.1
70.0
88.9
0.0
88.9
90.0
87.5

100.0
100.0
100.0

93.8
92.4
96.7
100.0
92.8
97.0
83.9
89.1
89.4
88.9
83.3



79.5
87.7
71.0
79.2



Arithmetic Mean
4.54
6.13
2.85
-
-
-
-
-
-
-
-
-
-
-
-
42.9
-
-
-
302
1,140
193
1,660
-
481
546
399

603
633
565

1 1 ,000
12,800
7,230
24,200
10,300
5,680
20,000
11.1
6.72
15.8
8.53



1.08
1.01
1.15
2.41



Std. Dev.
17.3
23.7
4.17
-
-
-
-
-
-
-
-
-
-
-
-
36.5
-
-
-
490
2,040
189
2,400
-
632
739
505

437
458
437

25,100
29,700
8,470
17,700
47,000
4,540
82,900
26.0
7.72
36.0
16.0



2.38
2.10
2.66
3.18



Geometric
Mean
1.87
2.07
1.68
-
-
-
-
-
-
-
-
-
-
-
-
30.8
-
-
-
133
337
130
572
-
275
303
244

446
481
406

5,010
5,580
3,940
14,100
3,400
3,890
2,560
4.22
3.74
4.80
3.36



0.389
0.467
0.321
0.757



Log Std. Dev.
1.05
1.13
0.963
-
-
-
-
-
-
-
-
-
-
-
-
0.852
-
-
-
1.31
1.57
0.916
1.63
-
1.04
1.10
1.03

0.856
0.815
0.952

1.34
1.38
1.24
1.32
1.36
1.04
1.87
1.29
1.14
1.44
1.31



1.47
1.25
1.66
1.93



* Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations.  This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries.  Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     1-22

-------
Table 1-1 Ob.   Bisphenol-A (80-05-7):  Range of Reported Concentrations in NC
                 multimedia samples collected from the homes and day care centers of
                 preschool children who stay at home or attend day care during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
128
66
62
20
127
65
62
13
126
64
62
12
119
65
54
19
119
65
54
19
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
129
66
63
24



127
65
62
24



Minimum

-------
Table 1-11 a.   a/pfra-Chlordane (5103-71-9): Summaries of concentrations in NC
                 multimedia samples collected from the homes and day care centers of
                 preschool children who stay at home or attend day care during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - atdaycare
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
20
121
66
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
129
66
63
24



126
64
62
22



% Detected
98.4
97.0
100.0
100.0
50.4
40.0
61.3
84.6
29.5
19.7
39.7
46.2
95.0
92.4
98.2
100.0
95.0
92.4
98.2
100.0
64.3
60.0
66.7
0.0
55.6
60.0
50.0

44.4
40.0
50.0

51.0
45.5
63.3
64.5
64.9
60.6
74.2
17.1
13.6
20.6
12.5



4.8
4.7
4.8
9.1



Arithmetic Mean
4.21
4.13
4.29
2.71
0.223
-
0.274
8.54
-
-
-
-
97.0
88.2
108
197
201
271
117
1,670
91.0
24.4
128
-
50.5
64.9
32.5

-
-
7.10

127
-
146
89.8
90.7
97.7
75.7
-
-
-
-



-
-
-
-



Std. Dev.
9.15
8.90
9.48
4.79
0.456
-
0.582
29.9
-
-
-
-
260
142
355
312
513
645
264
2,580
352
22.0
439
-
103
130
58.0

-
-
5.37

241
-
251
134
210
239
130
-
-
-
-



-
-
-
-



Geometric
Mean
1.17
1.08
1.27
0.837
0.117
-
0.132
0.262
-
-
-
-
27.2
32.4
22.1
60.9
28.3
30.7
25.7
270
16.6
15.0
17.5
-
16.2
20.1
12.3

-
-
5.65

61.6
-
72.5
55.8
35.8
34.6
38.4
-
-
-
-



-
-
-
-



Log Std. Dev.
1.55
1.65
1.44
1.50
0.899
-
0.966
2.01
-
-
-
-
1.45
1.44
1.46
1.62
2.04
2.23
1.78
2.19
1.41
1.10
1.58
-
1.41
1.50
1.32

-
-
0.705

1.02
-
1.06
0.836
1.15
1.19
1.07
-
-
-
-



-
-
-
-



* Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations.  This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                    1-24

-------
Table 1-11b.  a/pfra-Chlordane (5103-71-9):  Range of Reported Concentrations in NC
                multimedia samples collected from the homes and day care centers of
                preschool children who stay at home or attend day care during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
20
121
66
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
129
66
63
24



126
64
62
22



Minimum

-------
Table 1-12a.   qa/n/na-Chlordane (5103-74-2): Summaries of concentrations in NC
                 multimedia samples collected from the homes and day care centers of
                 preschool children who stay at home or attend day care during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - atdaycare
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
120
65
55
20
120
65
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
129
66
63
24



126
64
62
22



% Detected
100.0
100.0
100.0
100.0
61.4
52.3
71.0
84.6
29.5
19.7
39.7
46.2
96.7
95.4
98.2
100.0
96.7
95.4
98.2
100.0
67.9
60.0
72.2
100.0
55.6
60.0
50.0

44.4
40.0
50.0

54.2
47.0
70.0
64.5
67.0
63.6
74.2
18.6
15.2
22.2
12.5



0.0
0.0
0.0
0.0



Arithmetic Mean
7.52
7.56
7.48
6.34
0.404
0.284
0.530
9.21
-
-
-
-
133
132
134
304
283
373
176
2,750
104
44.8
137
9.86
102
150
40.7

-
-
10.7

174
-
198
130
122
131
101
-
-
-
-



-
-
-
-



Std. Dev.
15.2
15.3
15.2
13.0
1.17
0.583
1.56
31.8
-
-
-
-
285
197
365
445
684
821
460
4,710
340
49.2
423

269
356
77.0

-
-
9.40

312
-
334
180
235
266
152
-
-
-
-



-
-
-
-



Geometric
Mean
2.02
1.89
2.17
1.49
0.153
0.130
0.182
0.374
-
-
-
-
39.4
47.1
31.8
93.0
40.4
43.4
37.1
412
21.7
20.6
22.4
9.86
19.7
26.5
13.6

-
-
7.28

75.8
-
92.3
73.2
45.0
43.5
48.3
-
-
-
-



-
-
-
-



Log Std. Dev.
1.62
1.73
1.50
1.62
1.08
1.00
1.14
2.01
-
-
-
-
1.49
1.48
1.49
1.67
2.07
2.29
1.81
2.21
1.54
1.42
1.65

1.66
1.85
1.41

-
-
0.961

1.16
-
1.15
0.990
1.29
1.34
1.19
-
-
-
-



-
-
-
-



* Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                    1-26

-------
Table 1-12b.   qa/n/na-Chlordane (5103-74-2):  Range of Reported Concentrations in NC
                multimedia samples collected from the homes and day care centers of
                preschool children who stay at  home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
120
65
55
20
120
65
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
129
66
63
24



126
64
62
22



Minimum
0.090
0.090
0.120
0.210

-------
Table 1-13a.   Chlorpyrifos (2921-88-2): Summaries of concentrations in NC multimedia
                 samples collected from the homes and day care centers  of preschool
                 children who stay at home or attend day care during the  day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - atdaycare
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
128
66
62
20
127
65
62
13
128
65
63
13
121
66
55
19
121
66
55
19
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
129
66
63
24



126
64
62
22



% Detected
100.0
100.0
100.0
100.0
83.5
78.5
88.7
76.9
18.8
16.9
20.6
7.7
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
89.3
80.0
94.4
100.0
88.9
80.0
100.0

94.4
90.0
100.0

80.2
80.3
80.0
67.7
84.5
86.4
80.6
65.1
71.2
58.7
54.2



10.3
9.4
11.3
13.6



Arithmetic Mean
19.0
14.9
23.3
8.17
1.06
0.576
1.57
0.402
-
-
-
-
413
307
541
237
1,430
1,310
1,580
2,100
198
301
140
134
265
257
275

142
189
83.7

528
467
663
234
323
290
394
0.567
0.678
0.451
0.231



-
-
-
-



Std. Dev.
41.9
24.9
54.4
8.87
4.21
1.06
5.92
0.419
-
-
-
-
1,430
527
2,040
256
6,310
5,740
6,990
3,650
455
631
329

395
320
497

230
285
128

1,090
944
1,360
225
509
497
533
1.82
2.46
0.719
0.255



-
-
-
-



Geometric
Mean
6.99
5.91
8.35
3.86
0.311
0.237
0.414
0.228
-
-
-
-
137
131
145
132
143
124
169
530
61.9
75.5
55.4
134
78.5
75.6
82.2

47.6
52.2
42.4

195
174
250
130
128
117
155
0.204
0.211
0.196
0.139



-
-
-
-



Log Std. Dev.
1.37
1.36
1.36
1.34
1.29
1.21
1.32
1.21
-
-
-
-
1.31
1.27
1.37
1.24
1.99
2.08
1.89
1.86
1.45
1.84
1.23

1.76
1.99
1.54

1.50
1.79
1.14

1.36
1.32
1.46
1.23
1.43
1.36
1.58
1.23
1.21
1.25
1.00



-
-
-
-



* Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations.  This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries.  Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     1-28

-------
Table 1-13b.  Chlorpyrifos (2921-88-2): Range of Reported Concentrations in NC
                multimedia samples collected from the homes and day care centers of
                preschool children who stay at home or attend day care during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
128
66
62
20
127
65
62
13
128
65
63
13
121
66
55
19
121
66
55
19
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
129
66
63
24



126
64
62
22



Minimum
0.310
0.310
0.400
0.580

-------
Table 1-14a.   Chrysene (218-01-9): Summaries of concentrations in NC multimedia
                 samples collected from the homes  and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - atdaycare
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
128
66
62
20
127
65
62
13
128
65
63
13
118
63
55
20
118
63
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
128
66
62
24



127
65
62
24



% Detected
60.9
56.1
66.1
60.0
67.7
70.8
64.5
84.6
75.0
76.9
73.0
76.9
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
85.7
80.0
88.9
100.0
50.0
50.0
50.0

83.3
80.0
87.5

43.8
42.4
46.7
48.4
40.2
42.4
35.5
35.2
42.4
27.4
20.8



3.9
3.1
4.8
0.0



Arithmetic Mean
0.220
0.247
0.192
0.153
0.245
0.254
0.235
0.163
43.3
20.3
67.0
22.7
545
330
790
1,630
1,040
482
1,690
3,440
358
23.0
544
52.7
10.7
12.4
8.64

88.5
113
58.0

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Std. Dev.
0.292
0.351
0.211
0.311
0.478
0.427
0.530
0.168
181
98.9
236
50.6
1,630
586
2,290
5,870
4,100
774
5,910
7,490
1,450
16.7
1,800

11.2
14.3
6.04

164
215
65.1

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Geometric
Mean
0.137
0.144
0.130
0.094
0.142
0.155
0.130
0.116
2.64
2.24
3.13
5.08
190
178
205
301
205
179
239
1,330
34.1
17.9
48.9
52.7
8.10
8.68
7.42

25.9
26.1
25.8

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Log Std. Dev.
0.882
0.945
0.814
0.693
0.876
0.873
0.878
0.794
2.00
1.72
2.25
1.90
1.18
1.03
1.33
1.31
1.59
1.57
1.61
1.24
1.66
0.800
1.91

0.678
0.792
0.544

1.61
1.78
1.48

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



* Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations.  This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries.  Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     1-30

-------
Table 1-14b.  Chrysene (218-01-9):  Range of Reported Concentrations in NC multimedia
                samples collected from the homes and day care centers of preschool
                children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
128
66
62
20
127
65
62
13
128
65
63
13
118
63
55
20
118
63
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
128
66
62
24



127
65
62
24



Minimum

-------
Table 1-15a.   Cyfluthrin (68359-37-5): Summaries of concentrations in NC multimedia
                 samples collected from the homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
19
121
66
55
19
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
128
66
62
24



122
63
59
22



% Detected
3.9
0.0
8.1
10.0
0.0
0.0
0.0
0.0
11.6
7.6
15.9
7.7
47.9
54.5
40.0
42.1
47.9
54.5
40.0
42.1
7.1
0.0
11.1
0.0
0.0
0.0
0.0

77.8
80.0
75.0

32.3
30.3
36.7
19.4
14.4
18.2
6.5
6.3
4.5
8.1
4.2



0.0
0.0
0.0
0.0



Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
281
-
-
-
341
-
-
-
-
-
-
-
-
-

1,100
1,340
795

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
466
-
-
-
709
-
-
-
-
-
-
-
-
-

1,030
1,200
725

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
92.2
-
-
-
87.3
-
-
-
-
-
-
-
-
-

492
616
372

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
1.55
-
-
-
1.77
-
-
-
-
-
-
-
-
-

1.69
1.75
1.67

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



* Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations.  This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries.  Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     1-32

-------
Table 1-15b.  Cyfluthrin (68359-37-5):  Range of Reported Concentrations in NC
                multimedia samples collected from the homes and day care centers of
                preschool children who stay at home or attend day care during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
19
121
66
55
19
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
128
66
62
24



122
63
59
22



Minimum

-------
Table 1-16a.   Diazinon (333-41-5): Summaries of concentrations in NC multimedia
                 samples collected from the homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - atdaycare
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
19
121
66
55
19
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
128
65
63
24



126
64
62
22



% Detected
100.0
100.0
100.0
100.0
50.4
46.2
54.8
61.5
17.8
24.2
11.1
0.0
95.9
95.5
96.4
100.0
95.9
95.5
96.4
100.0
67.9
70.0
66.7
100.0
61.1
60.0
62.5

66.7
60.0
75.0

45.8
43.9
50.0
58.1
54.6
48.5
67.7
21.9
21.5
22.2
25.0



0.8
1.6
0.0
0.0



Arithmetic Mean
40.3
45.2
35.1
11.1
0.642
-
0.310
0.122
-
-
-
-
282
359
190
439
964
1,630
164
5,710
557
609
528
32.9
625
240
1,110

750
998
441

-
-
353
152
363
-
440
-
-
-
-



-
-
-
-



Std. Dev.
217
211
225
24.4
3.88
-
0.947
0.087
-
-
-
-
1,380
1,570
1,110
1,560
6,380
8,610
341
22,500
1,940
1,580
2,150

2,080
629
3,080

2,220
2,930
852

-
-
1,350
316
2,000
-
2,130
-
-
-
-



-
-
-
-



Geometric
Mean
2.41
2.24
2.59
2.47
0.133
-
0.133
0.095
-
-
-
-
24.4
28.0
20.6
58.6
25.4
26.6
24.1
235
23.2
44.1
16.3
32.9
27.0
27.9
25.9

41.2
34.1
52.3

-
-
69.9
69.5
35.3
-
44.1
-
-
-
-



-
-
-
-



Log Std. Dev.
1.81
1.97
1.63
1.78
1.12
-
0.986
0.743
-
-
-
-
1.62
1.75
1.45
1.73
2.17
2.29
2.04
2.38
2.07
2.41
1.83

2.18
2.00
2.53

2.56
2.62
2.62

-
-
1.35
1.08
1.40
-
1.41
-
-
-
-



-
-
-
-



* Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries.  Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     1-34

-------
Table l-16b.   Diazinon (333-41-5):  Range of Reported Concentrations in NC multimedia
                 samples collected from the homes and day care centers of preschool
                 children who stay at  home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
19
121
66
55
19
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
128
65
63
24



126
64
62
22



Minimum
0.140
0.160
0.140
0.170

-------
Table 1-17a.   Dibenzora.frlanthracene (53-70-3): Summaries of concentrations in NC
                 multimedia samples collected from the homes and day care centers of
                 preschool children who stay at home or attend day care during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
118
63
55
20
118
63
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
128
66
62
24



127
65
62
24



% Detected
5.5
4.5
6.5
0.0
3.9
6.2
1.6
0.0
52.7
48.5
57.1
76.9
94.9
93.7
96.4
100.0
94.9
93.7
96.4
100.0
35.7
10.0
50.0
0.0
5.6
10.0
0.0

22.2
20.0
25.0

7.3
7.6
6.7
12.9
10.3
9.1
12.9
0.0
0.0
0.0
0.0



0.0
0.0
0.0
0.0



Arithmetic Mean
-
-
-
-
-
-
-
-
9.50
-
13.9
5.35
100
74.5
130
268
206
115
310
858
-
-
132
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Std. Dev.
-
-
-
-
-
-
-
-
35.7
-
45.0
11.2
213
117
284
826
806
162
1,160
1,840
-
-
450
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Geometric
Mean
-
-
-
-
-
-
-
-
1.09
-
1.31
1.85
44.6
44.0
45.2
78.7
48.1
44.3
52.7
348
-
-
14.1
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Log Std. Dev.
-
-
-
-
-
-
-
-
1.61
-
1.78
1.38
1.15
1.00
1.31
1.17
1.61
1.60
1.63
1.20
-
-
1.66
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



* Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                    1-36

-------
Table 1-17b.  Dibenzora.frlanthracene (53-70-3):  Range of Reported Concentrations in
                NC multimedia samples collected from the homes and day care centers of
                preschool children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
118
63
55
20
118
63
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
128
66
62
24



127
65
62
24



Minimum

-------
Table 1-18a.   Di-n-butylphthalate (84-74-2): Summaries of concentrations in NC
                 multimedia samples collected from the homes and day care centers of
                 preschool children who stay at home or attend day care during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - atdaycare
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
128
66
62
20
127
65
62
13
128
65
63
13
119
64
55
20
119
64
55
20
28
10
18
1
18
10
8

7
4
3

96
66
30
31
97
66
31
110
55
55
18



117
61
56
22



% Detected
100.0
100.0
100.0
100.0
36.2
26.2
46.8
69.2
33.6
26.2
41.3
61.5
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
72.2
70.0
75.0

100.0
100.0
100.0

81.3
72.7
100.0
90.3
84.5
84.8
83.9
31.8
27.3
36.4
33.3



28.2
31.1
25.0
40.9



Arithmetic Mean
276
234
321
576
-
-
-
41.7
-
-
-
78.6
8,960
9,390
8,460
15,200
21,500
19,500
23,800
112,000
7,130
3,950
8,900
18,100
5,590
4,360
7,130

10,700
15,500
4,470

17,400
14,900
23,100
30,300
31,100
25,400
43,400
-
-
-
-



-
-
-
-



Std. Dev.
180
146
201
623
-
-
-
60.3
-
-
-
140
8,960
9,700
8,090
8,330
51 ,000
46,200
56,400
130,000
9,680
2,820
1 1 ,600

7,860
4,890
10,700

12,900
16,200
2,110

24,000
21,600
28,100
55,500
61 ,600
64,000
55,200
-
-
-
-



-
-
-
-



Geometric
Mean
229
195
271
397
-
-
-
19.5
-
-
-
22.5
6,400
6,900
5,860
12,800
6,430
6,090
6,830
56,600
4,420
3,080
5,410
18,100
2,330
2,040
2,760

6,200
8,540
4,050

9,260
7,520
14,700
12,200
8,290
6,520
13,800
-
-
-
-



-
-
-
-



Log Std. Dev.
0.635
0.639
0.590
0.840
-
-
-
1.20
-
-
-
1.62
0.789
0.726
0.854
0.664
1.48
1.52
1.45
1.41
0.940
0.775
0.982

1.53
1.51
1.64

1.09
1.35
0.574

1.14
1.18
0.920
1.28
1.63
1.49
1.80
-
-
-
-



-
-
-
-



* Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations.  This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries.  Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     1-38

-------
Table 1-18b.   Di-n-butylphthalate (84-74-2):  Range of Reported Concentrations in NC
                 multimedia samples collected from the homes and day care centers of
                 preschool children who stay at home or attend day care during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
128
66
62
20
127
65
62
13
128
65
63
13
119
64
55
20
119
64
55
20
28
10
18
1
18
10
8

7
4
3

96
66
30
31
97
66
31
110
55
55
18



117
61
56
22



Minimum
18.7
18.7
75.9
127

-------
Table 1-19a.   Dicamba (1918-00-9): Summaries of concentrations in NC multimedia
                 samples collected from the homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - atdaycare
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
128
66
62
20
126
65
61
13
127
65
62
13
121
66
55
20
121
66
55
20
13

13
1








98
66
32
32
98
66
32
129
66
63
24
128
66
62
125
64
61
23
120
64
56
% Detected
0.8
1.5
0.0
0.0
7.9
10.8
4.9
7.7
5.5
6.2
4.8
0.0
23.1
27.3
18.2
5.0
23.1
27.3
18.2
5.0
0.0

0.0
0.0








0.0
0.0
0.0
0.0
1.0
1.5
0.0
16.3
18.2
14.3
4.2
13.3
13.6
12.9
0.0
0.0
0.0
0.0
0.0
0.0
0.0
Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-








-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-








-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-








-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-








-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
* Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations.  This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                    1-40

-------
Table l-19b.   Dicamba (1918-00-9):  Range of Reported Concentrations in NC multimedia
                samples collected from the homes and day care centers of preschool
                children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
128
66
62
20
126
65
61
13
127
65
62
13
121
66
55
20
121
66
55
20
13

13
1








98
66
32
32
98
66
32
129
66
63
24
128
66
62
125
64
61
23
120
64
56
Minimum

-------
Table l-20a.   p.p'-DDE (72-55-9):  Summaries of concentrations in NC multimedia samples
                 collected from the homes and day care centers of preschool children who
                 stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
20
121
66
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
129
66
63
24



126
64
62
22



% Detected
33.6
30.3
37.1
15.0
0.0
0.0
0.0
7.7
14.7
9.1
20.6
15.4
39.7
39.4
40.0
50.0
39.7
39.4
40.0
50.0
17.9
20.0
16.7
0.0
11.1
0.0
25.0

27.8
30.0
25.0

4.2
1.5
10.0
3.2
3.1
1.5
6.5
58.9
65.2
52.4
54.2



21.4
17.2
25.8
18.2



Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
11.2
-
-
-
71.3
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
0.315
0.324
0.305
0.385



-
-
-
-



Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
17.6
-
-
-
120
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
0.410
0.351
0.467
0.571



-
-
-
-



Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
4.51
-
-
-
20.0
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
0.175
0.190
0.160
0.176



-
-
-
-



Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
1.38
-
-
-
1.72
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
1.07
1.06
1.08
1.24



-
-
-
-



a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations.  This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries.  Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     1-42

-------
Table l-20b.  p.p'-DDE (72-55-9):  Range of Reported Concentrations in NC multimedia
                samples collected from the homes and day care centers of preschool
                children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
20
121
66
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
129
66
63
24



126
64
62
22



Minimum

-------
Table 1-21 a.   p.p'-DDT (50-29-3): Summaries of concentrations in NC multimedia samples
                 collected from the homes and day care centers of preschool children who
                 stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
20
121
66
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
129
66
63
24



126
64
62
22



% Detected
36.7
36.4
37.1
20.0
11.8
15.4
8.1
15.4
20.2
12.1
28.6
15.4
38.8
36.4
41.8
30.0
38.8
36.4
41.8
30.0
17.9
10.0
22.2
0.0
16.7
10.0
25.0

27.8
40.0
12.5

8.3
7.6
10.0
3.2
6.2
4.5
9.7
3.9
1.5
6.3
4.2



2.4
3.1
1.6
0.0



Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations.  This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries.  Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     1-44

-------
Table 1-21 b.  p.p'-DDT (50-29-3):  Range of Reported Concentrations in NC multimedia
                samples collected from the homes and day care centers of preschool
                children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
20
121
66
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
129
66
63
24



126
64
62
22



Minimum

-------
Table l-22a.   2.4-D (2.4-dichlorophenoxyacetic acid) (94-75-7):  Summaries of
                 concentrations in NC multimedia samples collected from the homes and
                 day care centers of preschool children who stay at home or attend day care
                 during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
128
66
62
20
126
65
61
13
126
65
61
13
120
66
54
20
120
66
54
20
13

13
1








98
66
32
32
98
66
32
129
66
63
24
128
66
62
125
64
61
23
120
64
56
% Detected
46.1
37.9
54.8
60.0
19.0
18.5
19.7
46.2
19.0
16.9
21.3
0.0
65.8
83.3
44.4
75.0
65.8
83.3
44.4
75.0
7.7

7.7
0.0








9.2
7.6
12.5
3.1
7.1
4.5
12.5
55.8
47.0
65.1
37.5
50.8
50.0
51.6
1.6
1.6
1.6
0.0
4.2
3.1
5.4
Arithmetic Mean
-
-
1.06
1.58
-
-
-
-
-
-
-
-
214
280
-
28.3
227
317
-
205
-

-
-








-
-
-
-
-
-
-
0.629
-
0.632
-
0.678
0.643
0.716
-
-
-
-
-
-
-
Std. Dev.
-
-
1.29
1.99
-
-
-
-
-
-
-
-
744
933
-
24.6
789
992
-
329
-

-
-








-
-
-
-
-
-
-
0.727
-
0.678
-
0.808
0.805
0.815
-
-
-
-
-
-
-
Geometric
Mean
-
-
0.481
0.574
-
-
-
-
-
-
-
-
30.4
57.3
-
15.5
31.7
54.3
-
68.5
-

-
-








-
-
-
-
-
-
-
0.393
-
0.415
-
0.387
0.379
0.396
-
-
-
-
-
-
-
Log Std. Dev.
-
-
1.33
1.58
-
-
-
-
-
-
-
-
2.01
1.74
-
1.37
1.93
1.81
-
1.61
-

-
-








-
-
-
-
-
-
-
0.932
-
0.900
-
1.02
0.974
1.07
-
-
-
-
-
-
-
a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries.  Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                    1-46

-------
Table l-22b.   2.4-D (2.4-dichlorophenoxyacetic acid) (94-75-7):  Range of Reported
                Concentrations in NC multimedia samples collected from the homes and
                day care centers of preschool children who stay at home or attend day care
                during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
128
66
62
20
126
65
61
13
126
65
61
13
120
66
54
20
120
66
54
20
13
0
13
1




0
0
0
0
98
66
32
32
98
66
32
129
66
63
24
128
66
62
125
64
61
23
120
64
56
Minimum

-------
Table l-23a.   Dieldrin (60-57-1): Summaries of concentrations in NC multimedia samples
                 collected from the homes and day care centers of preschool children who
                 stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
19
121
66
55
19
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
129
66
63
24



126
64
62
22



% Detected
41.4
40.9
41.9
30.0
12.6
13.8
11.3
23.1
14.0
10.6
17.5
7.7
43.0
47.0
38.2
57.9
43.0
47.0
38.2
57.9
28.6
20.0
33.3
0.0
16.7
10.0
25.0

22.2
30.0
12.5

4.2
6.1
0.0
3.2
6.2
7.6
3.2
2.3
1.5
3.2
0.0



0.0
0.0
0.0
0.0



Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
161
-
-
-
878
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
390
-
-
-
2,420
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
20.0
-
-
-
80.2
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
2.44
-
-
-
2.60
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     1-48

-------
Table l-23b.   Dieldrin (60-57-1): Range of Reported Concentrations in NC multimedia
                 samples collected from the homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
19
121
66
55
19
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
129
66
63
24



126
64
62
22



Minimum

-------
Table l-24a.   Endrin (72-20-8): Summaries of concentrations in NC multimedia samples
                 collected from the homes and day care centers of preschool children who
                 stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
20
121
66
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
129
66
63
24



126
64
62
22



% Detected
33.6
36.4
30.6
35.0
39.4
43.1
35.5
53.8
3.9
4.5
3.2
7.7
19.0
22.7
14.5
15.0
19.0
22.7
14.5
15.0
14.3
20.0
11.1
0.0
27.8
10.0
50.0

11.1
20.0
0.0

3.1
4.5
0.0
3.2
1.0
1.5
0.0
0.8
1.5
0.0
0.0



0.0
0.0
0.0
0.0



Arithmetic Mean
-
-
-
-
-
-
-
0.304
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
40.4

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Std. Dev.
-
-
-
-
-
-
-
0.330
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
45.7

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Geometric
Mean
-
-
-
-
-
-
-
0.159
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
18.4

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Log Std. Dev.
-
-
-
-
-
-
-
1.25
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
1.45

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries.  Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     1-50

-------
Table l-24b.   Endrin (72-20-8):  Range of Reported Concentrations in NC multimedia
                 samples collected from the homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
20
121
66
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
129
66
63
24



126
64
62
22



Minimum

-------
Table l-25a.   Heptachlor (76-44-8): Summaries of concentrations in NC multimedia
                 samples collected from the homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
120
65
55
20
120
65
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
129
66
63
24



126
64
62
22



% Detected
92.2
92.4
91.9
100.0
60.6
56.9
64.5
69.2
3.1
3.0
3.2
23.1
40.8
41.5
40.0
55.0
40.8
41.5
40.0
55.0
39.3
30.0
44.4
0.0
33.3
40.0
25.0

27.8
40.0
12.5

21.9
22.7
20.0
22.6
17.5
18.2
16.1
14.0
19.7
7.9
12.5



0.0
0.0
0.0
0.0



Arithmetic Mean
29.3
30.2
28.5
39.4
1.22
1.39
1.04
5.31
-
-
-
-
-
-
-
192
-
-
-
1,680
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Std. Dev.
66.5
73.0
59.4
87.0
4.15
5.03
3.00
15.0
-
-
-
-
-
-
-
322
-
-
-
3,540
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Geometric
Mean
7.34
6.76
8.02
8.87
0.282
0.261
0.305
0.530
-
-
-
-
-
-
-
19.9
-
-
-
88.0
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Log Std. Dev.
1.89
1.92
1.86
1.52
1.50
1.57
1.43
2.17
-
-
-
-
-
-
-
2.61
-
-
-
3.11
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations.  This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries.  Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     1-52

-------
Table l-25b.   Heptachlor (76-44-8):  Range of Reported Concentrations in NC multimedia
                samples collected from the homes and day care centers of preschool
                children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
120
65
55
20
120
65
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
129
66
63
24



126
64
62
22



Minimum

-------
Table l-26a.   IndenoM ,2.3-cc/lpvrene (193-39-5): Summaries of concentrations in NC
                 multimedia samples collected from the homes and day care centers of
                 preschool children who stay at home or attend day care during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
128
66
62
20
127
65
62
13
128
65
63
13
118
63
55
20
118
63
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
128
66
62
24



127
65
62
24



% Detected
52.3
50.0
54.8
40.0
56.7
58.5
54.8
69.2
70.3
72.3
68.3
76.9
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
82.1
60.0
94.4
100.0
22.2
20.0
25.0

66.7
60.0
75.0

28.1
25.8
33.3
45.2
20.6
15.2
32.3
0.8
0.0
1.6
0.0



0.0
0.0
0.0
0.0



Arithmetic Mean
0.200
0.201
0.198
-
0.205
0.248
0.160
0.142
36.4
19.8
53.5
19.7
412
310
528
1,090
855
449
1,320
3,570
323
12.5
495
12.3
-
-
-

38.0
31.0
46.7

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Std. Dev.
0.233
0.253
0.213
-
0.258
0.318
0.165
0.201
143
102
176
49.1
1,060
471
1,460
3,360
3,910
606
5,690
7,850
1,350
12.1
1,670

-
-
-

51.3
49.8
55.2

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Geometric
Mean
0.127
0.124
0.130
-
0.131
0.151
0.112
0.088
2.14
1.90
2.41
4.02
183
190
175
301
197
192
204
1,330
24.9
9.39
42.8
12.3
-
-
-

13.9
11.1
18.4

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Log Std. Dev.
0.883
0.883
0.890
-
0.880
0.941
0.792
0.876
1.99
1.73
2.23
1.81
1.07
0.924
1.22
1.22
1.54
1.53
1.56
1.28
1.68
0.741
1.82

-
-
-

1.49
1.46
1.58

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



* Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                    1-54

-------
Table l-26b.  lndenori.2.3-cc/lpvrene (193-39-5):  Range of Reported Concentrations in NC
                multimedia samples collected from the homes and day care centers of
                preschool children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
128
66
62
20
127
65
62
13
128
65
63
13
118
63
55
20
118
63
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
128
66
62
24



127
65
62
24



Minimum

-------
Table l-27a.   Lindane (58-89-9):  Summaries of concentrations in NC multimedia samples
                 collected  from the homes and day care centers of preschool children who
                 stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
20
121
66
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
129
66
63
24



126
64
62
22



% Detected
12.5
10.6
14.5
20.0
11.8
6.2
17.7
7.7
6.2
3.0
9.5
7.7
14.0
13.6
14.5
20.0
14.0
13.6
14.5
20.0
10.7
0.0
16.7
0.0
0.0
0.0
0.0

27.8
30.0
25.0

2.1
1.5
3.3
0.0
5.2
4.5
6.5
7.8
7.6
7.9
4.2



2.4
1.6
3.2
0.0



Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations.  This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries.  Reported measures of 0 ng/mL in liquid food do not
enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     1-56

-------
Table l-27b.   Lindane (58-89-9): Range of Reported Concentrations in NC multimedia
                 samples collected from the homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
20
121
66
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
129
66
63
24



126
64
62
22



Minimum

-------
Table l-28a.   Nonylphenol (104-40-5): Summaries of concentrations in NC multimedia
                 samples collected from the homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
128
66
62
20
127
65
62
13
97
50
47
7
53
32
21
14
53
32
21
14
28
10
18
1
18
10
8

16
8
8

96
66
30
31
97
66
31
129
66
63
23



127
65
62
24



% Detected
10.9
12.1
9.7
0.0
2.4
3.1
1.6
0.0
2.1
4.0
0.0
0.0
3.8
6.3
0.0
7.1
3.8
6.3
0.0
7.1
0.0
0.0
0.0
0.0
0.0
0.0
0.0

6.3
12.5
0.0

0.0
0.0
0.0
0.0
3.1
0.0
9.7
3.1
3.0
3.2
0.0



4.7
6.2
3.2
4.2



Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do not
enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     1-58

-------
Table l-28b.  Nonylphenol (104-40-5):  Range of Reported Concentrations in NC
                multimedia samples collected from the homes and day care centers of
                preschool children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
128
66
62
20
127
65
62
13
97
50
47
7
53
32
21
14
53
32
21
14
28
10
18
1
18
10
8

16
8
8

96
66
30
31
97
66
31
129
66
63
23



127
65
62
24



Minimum

-------
Table l-29a.   Pentachloronitrobenzene (82-68-8): Summaries of concentrations in NC
                 multimedia samples collected from the homes and day care centers of
                 preschool  children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
20
121
66
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
129
66
63
24



126
64
62
22



% Detected
13.3
9.1
17.7
15.0
2.4
3.1
1.6
7.7
0.0
0.0
0.0
0.0
2.5
4.5
0.0
5.0
2.5
4.5
0.0
5.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0

0.0
0.0
0.0

0.0
0.0
0.0
0.0
1.0
0.0
3.2
0.8
0.0
1.6
0.0



1.6
1.6
1.6
0.0



Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries.  Reported measures of 0 ng/mL in liquid food do not
enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     1-60

-------
Table l-29b.   Pentachloronitrobenzene (82-68-8):  Range of Reported Concentrations in
                NC multimedia samples collected from the homes and day care centers of
                preschool children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
20
121
66
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
129
66
63
24



126
64
62
22



Minimum

-------
Table l-30a.   Pentachlorophenol (87-86-5): Summaries of concentrations in NC
                 multimedia samples collected from the homes and day care centers of
                 preschool children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
128
66
62
20
126
65
61
13
126
65
61
13
121
66
55
20
121
66
55
20
13

13
1








98
66
32
32
98
66
32
129
66
63
24
128
66
62
125
64
61
23
119
64
55
% Detected
96.9
95.5
98.4
100.0
94.4
90.8
98.4
100.0
32.5
24.6
41.0
23.1
91.7
92.4
90.9
100.0
91.7
92.4
90.9
100.0
46.2

46.2
0.0








35.7
34.8
37.5
18.8
30.6
24.2
43.8
6.2
7.6
4.8
12.5
8.6
4.5
12.9
2.4
1.6
3.3
0.0
0.8
1.6
0.0
Arithmetic Mean
3.10
3.05
3.15
5.12
1.54
1.22
1.88
0.960
-
-
-
-
172
169
176
104
452
524
366
1,100
-

-
-








-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Std. Dev.
4.67
5.35
3.86
13.9
4.66
1.27
6.58
0.607
-
-
-
-
419
237
567
134
1,140
1,200
1,070
2,130
-

-
-








-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Geometric
Mean
1.46
1.24
1.75
1.71
0.798
0.724
0.883
0.815
-
-
-
-
65.5
80.8
51.0
63.3
68.2
76.5
59.4
281
-

-
-








-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Log Std. Dev.
1.26
1.33
1.17
1.17
1.05
1.16
0.920
0.586
-
-
-
-
1.42
1.24
1.58
1.08
2.04
2.08
1.99
1.94
-

-
-








-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do not
enter into the descriptive statistics.  Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     1-62

-------
Table l-30b.   Pentachlorophenol (87-86-5):  Range of Reported Concentrations in NC
                multimedia samples collected from the homes and day care centers of
                preschool children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
128
66
62
20
126
65
61
13
126
65
61
13
121
66
55
20
121
66
55
20
13

13
1








98
66
32
32
98
66
32
129
66
63
24
128
66
62
125
64
61
23
119
64
55
Minimum

-------
Table 1-31 a.   c/s-Permethrin (61949-76-6): Summaries of concentrations in NC multimedia
                 samples collected from the homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
20
121
66
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
129
66
63
24



123
62
61
22



% Detected
66.4
59.1
74.2
55.0
15.7
7.7
24.2
38.5
22.5
25.8
19.0
7.7
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
92.9
90.0
94.4
100.0
83.3
80.0
87.5

83.3
90.0
75.0

86.5
83.3
93.3
93.5
73.2
72.7
74.2
45.7
47.0
44.4
25.0



17.9
14.5
21.3
13.6



Arithmetic Mean
2.13
1.37
2.94
0.506
-
-
-
-
-
-
-
-
6,080
3,880
8,710
3,500
9,750
9,630
9,900
54,400
1,610
1,930
1,440
938
30,500
52,300
3,100

1,640
1,560
1,740

9,210
2,540
23,900
1,660
1 1 ,400
698
34,100
-
-
-
-



-
-
-
-



Std. Dev.
5.15
2.54
6.87
0.779
-
-
-
-
-
-
-
-
29,400
9,780
42,300
6,760
30,200
25,300
35,500
196,000
2,630
2,810
2,590

117,000
158,000
5,080

3,190
2,710
3,910

65,400
6,640
116,000
3,850
104,000
1,540
184,000
-
-
-
-



-
-
-
-



Geometric
Mean
0.463
0.361
0.603
0.199
-
-
-
-
-
-
-
-
995
1,030
959
1,140
1,040
972
1,120
5,070
353
460
305
938
443
486
395

196
292
118

712
526
1,390
665
200
157
333
-
-
-
-



-
-
-
-



Log Std. Dev.
1.76
1.70
1.81
1.35
-
-
-
-
-
-
-
-
1.53
1.52
1.56
1.46
2.18
2.31
2.03
2.12
2.06
2.31
1.97

3.19
3.66
2.72

2.56
2.38
2.84

1.90
1.85
1.86
1.37
2.12
1.87
2.54
-
-
-
-



-
-
-
-



a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations.  This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do not
enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     1-64

-------
Table 1-31 b.  c/s-Permethrin (61949-76-6): Range of Reported Concentrations in NC
                multimedia samples collected from the homes and day care centers of
                preschool children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
20
121
66
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
129
66
63
24



123
62
61
22



Minimum

-------
Table l-32a.   frans-Permethrin (61949-77-7): Summaries of concentrations in NC
                 multimedia samples collected from the homes and day care  centers of
                 preschool children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
20
121
66
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
128
66
62
24



121
62
59
22



% Detected
65.6
57.6
74.2
50.0
15.7
7.7
24.2
38.5
22.5
25.8
19.0
7.7
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
92.9
90.0
94.4
100.0
83.3
80.0
87.5

83.3
90.0
75.0

86.5
83.3
93.3
93.5
73.2
72.7
74.2
46.1
47.0
45.2
25.0



16.5
14.5
18.6
13.6



Arithmetic Mean
1.92
1.26
2.62
0.451
-
-
-
-
-
-
-
-
6,120
3,810
8,900
3,600
9,420
9,030
9,890
55,900
1,570
2,020
1,320
732
34,800
60,100
3,300

1,750
1,730
1,760

9,310
2,760
23,700
1,400
12,000
836
35,800
-
-
-
-



-
-
-
-



Std. Dev.
5.22
2.49
7.02
0.681
-
-
-
-
-
-
-
-
30,400
10,000
43,800
7,120
29,900
24,300
35,700
202,000
2,680
3,220
2,400

135,000
181,000
5,590

3,380
3,000
4,030

68,100
7,270
121,000
3,770
110,000
1,990
195,000
-
-
-
-



-
-
-
-



Geometric
Mean
0.382
0.304
0.487
0.185
-
-
-
-
-
-
-
-
835
898
764
1,110
869
851
891
4,900
268
388
218
732
414
485
340

183
279
108

548
454
830
455
162
137
231
-
-
-
-



-
-
-
-



Log Std. Dev.
1.71
1.67
1.74
1.32
-
-
-
-
-
-
-
-
1.64
1.58
1.71
1.45
2.25
2.34
2.17
2.09
2.22
2.40
2.15

3.26
3.74
2.77

2.63
2.51
2.85

1.93
1.93
1.90
1.39
2.13
1.95
2.47
-
-
-
-



-
-
-
-



a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do not
enter into the descriptive statistics.  Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     1-66

-------
Table l-32b.   frans-Permethrin (61949-77-7):  Range of Reported Concentrations in NC
                multimedia samples collected from the homes and day care centers of
                preschool children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
20
121
66
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
128
66
62
24



121
62
59
22



Minimum

-------
Table l-33a.   PCB 44 (41464-39-5): Summaries of concentrations in NC multimedia
                 samples collected from the homes  and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
20
121
66
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
129
66
63
23



126
64
62
22



% Detected
46.9
51.5
41.9
55.0
22.0
16.9
27.4
46.2
1.6
3.0
0.0
0.0
15.7
9.1
23.6
45.0
15.7
9.1
23.6
45.0
10.7
10.0
11.1
0.0
22.2
20.0
25.0

11.1
10.0
12.5

1.0
1.5
0.0
0.0
3.1
1.5
6.5
1.6
1.5
1.6
0.0



0.0
0.0
0.0
0.0



Arithmetic Mean
-
0.230
-
0.706
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Std. Dev.
-
0.359
-
1.02
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Geometric
Mean
-
0.097
-
0.176
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Log Std. Dev.
-
1.28
-
1.91
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations.  This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries.  Reported measures of 0 ng/mL in liquid food do not
enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     1-68

-------
Table l-33b.  PCB 44 (41464-39-5):  Range of Reported Concentrations in NC multimedia
                samples collected from the homes and day care centers of preschool
                children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
20
121
66
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
129
66
63
23



126
64
62
22



Minimum

-------
Table l-34a.   PCB 52 (35693-99-3): Summaries of concentrations in NC multimedia
                 samples collected from the homes  and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
20
121
66
55
20
28
10
18
1
18
10
8

16
9
7

96
66
30
31
97
66
31
129
66
63
23



126
64
62
22



% Detected
89.1
93.9
83.9
100.0
62.2
50.8
74.2
92.3
3.9
4.5
3.2
7.7
32.2
24.2
41.8
60.0
32.2
24.2
41.8
60.0
25.0
10.0
33.3
0.0
22.2
20.0
25.0

6.3
11.1
0.0

9.4
12.1
3.3
6.5
4.1
3.0
6.5
7.0
4.5
9.5
8.7



0.0
0.0
0.0
0.0



Arithmetic Mean
0.853
0.624
1.10
1.19
0.105
0.084
0.128
0.177
-
-
-
-
-
-
-
16.6
-
-
-
130
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Std. Dev.
1.73
0.618
2.39
1.42
0.112
0.090
0.128
0.214
-
-
-
-
-
-
-
20.3
-
-
-
171
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Geometric
Mean
0.469
0.477
0.459
0.698
0.073
0.059
0.092
0.106
-
-
-
-
-
-
-
7.35
-
-
-
32.6
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Log Std. Dev.
1.14
0.770
1.44
1.01
0.840
0.796
0.827
1.02
-
-
-
-
-
-
-
1.40
-
-
-
2.13
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations.  This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries.  Reported measures of 0 ng/mL in liquid food do not
enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     1-70

-------
Table l-34b.  PCB 52 (35693-99-3):  Range of Reported Concentrations in NC multimedia
                samples collected from the homes and day care centers of preschool
                children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
20
121
66
55
20
28
10
18
1
18
10
8

16
9
7

96
66
30
31
97
66
31
129
66
63
23



126
64
62
22



Minimum

-------
Table l-35a.   PCB 70(32698-11-1): Summaries of concentrations in NC multimedia
                 samples collected from the homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
20
121
66
55
20
28
10
18
1
18
10
8

18
10
8

96
66



















% Detected
45.3
48.5
41.9
60.0
15.7
12.3
19.4
38.5
1.6
3.0
0.0
0.0
18.2
12.1
25.5
45.0
18.2
12.1
25.5
45.0
14.3
10.0
16.7
0.0
16.7
20.0
12.5

16.7
10.0
25.0

3.1
3.0



















Arithmetic Mean
-
-
-
0.289
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-



















Std. Dev.
-
-
-
0.486
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-



















Geometric
Mean
-
-
-
0.100
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-



















Log Std. Dev.
-
-
-
1.43
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-



















a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do not
enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     1-72

-------
Table l-35b.  PCB 70(32698-11-1):  Range of Reported Concentrations in NC multimedia
                samples collected from the homes and day care centers of preschool
                children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
20
121
66
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
129
66
63
23



126
64
62
22



Minimum

-------
Table l-36a.   PCB 77(32598-13-3): Summaries of concentrations in NC multimedia
                 samples collected from the homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
20
121
66
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
129
66
63
23



126
64
62
22



% Detected
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0

0.0
0.0
0.0

0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0



0.0
0.0
0.0
0.0



Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do not
enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     1-74

-------
Table l-36b.  PCB 77(32598-13-3): Range of Reported Concentrations in NC multimedia
                samples collected from the homes and day care centers of preschool
                children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
20
121
66
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
129
66
63
23



126
64
62
22



Minimum

-------
Table l-37a.   PCB 95 (38379-99-6): Summaries of concentrations in NC multimedia
                 samples collected from the homes  and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
20
121
66
55
20
28
10
18
1
18
10
8

15
10
5

96
66
30
31
97
66
31
129
66
63
23



126
64
62
22



% Detected
75.8
74.2
77.4
70.0
40.9
27.7
54.8
76.9
3.1
3.0
3.2
0.0
35.5
34.8
36.4
50.0
35.5
34.8
36.4
50.0
14.3
10.0
16.7
0.0
22.2
20.0
25.0

13.3
20.0
0.0

9.4
12.1
3.3
3.2
9.3
10.6
6.5
3.1
4.5
1.6
0.0



0.0
0.0
0.0
0.0



Arithmetic Mean
0.192
0.144
0.243
0.187
-
-
0.065
0.080
-
-
-
-
-
-
-
6.88
-
-
-
59.7
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Std. Dev.
0.580
0.303
0.773
0.240
-
-
0.077
0.085
-
-
-
-
-
-
-
8.16
-
-
-
96.7
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Geometric
Mean
0.092
0.090
0.094
0.100
-
-
0.048
0.057
-
-
-
-
-
-
-
3.99
-
-
-
17.7
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Log Std. Dev.
0.938
0.809
1.07
1.15
-
-
0.667
0.815
-
-
-
-
-
-
-
1.05
-
-
-
1.73
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations.  This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries.  Reported measures of 0 ng/mL in liquid food do not
enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     1-76

-------
Table l-37b.   PCB 95 (38379-99-6):  Range of Reported Concentrations in NC multimedia
                 samples collected from the homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
20
121
66
55
20
28
10
18
1
18
10
8

15
10
5

96
66
30
31
97
66
31
129
66
63
23



126
64
62
22



Minimum

-------
Table l-38a.   PCB 101 (37680-73-2): Summaries of concentrations in NC multimedia
                 samples collected from the homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
20
121
66
55
20
28
10
18
1
18
10
8

15
9
6

96
66
30
31
97
66
31
129
66
63
23



126
64
62
22



% Detected
52.3
59.1
45.2
60.0
22.8
16.9
29.0
61.5
3.9
3.0
4.8
0.0
34.7
34.8
34.5
55.0
34.7
34.8
34.5
55.0
7.1
10.0
5.6
0.0
16.7
10.0
25.0

20.0
22.2
16.7

11.5
15.2
3.3
6.5
12.4
15.2
6.5
0.0
0.0
0.0
0.0



0.0
0.0
0.0
0.0



Arithmetic Mean
0.162
0.136
-
0.175
-
-
-
0.092
-
-
-
-
-
-
-
8.09
-
-
-
68.8
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Std. Dev.
0.477
0.327
-
0.236
-
-
-
0.135
-
-
-
-
-
-
-
9.34
-
-
-
120
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Geometric
Mean
0.070
0.076
-
0.088
-
-
-
0.052
-
-
-
-
-
-
-
4.29
-
-
-
19.0
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Log Std. Dev.
1.02
0.893
-
1.19
-
-
-
1.01
-
-
-
-
-
-
-
1.18
-
-
-
1.72
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations.  This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do not
enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     1-78

-------
Table l-38b.  PCB  101 (37680-73-2):  Range of Reported Concentrations in NC multimedia
                samples collected from the homes and day care centers of preschool
                children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
20
121
66
55
20
28
10
18
1
18
10
8

15
9
6

96
66
30
31
97
66
31
129
66
63
23



126
64
62
22



Minimum

-------
Table l-39a.   PCB 105 (32598-14-4): Summaries of concentrations in NC multimedia
                 samples collected from the homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
20
121
66
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
129
66
63
23



126
64
62
22



% Detected
7.0
9.1
4.8
5.0
0.8
0.0
1.6
0.0
2.3
3.0
1.6
0.0
5.8
3.0
9.1
5.0
5.8
3.0
9.1
5.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0

22.2
30.0
12.5

1.0
1.5
0.0
0.0
1.0
1.5
0.0
0.0
0.0
0.0
0.0



0.0
0.0
0.0
0.0



Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations.  This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do not
enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     1-80

-------
Table l-39b.  PCB  105 (32598-14-4):  Range of Reported Concentrations in NC multimedia
                samples collected from the homes and day care centers of preschool
                children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
20
121
66
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
129
66
63
23



126
64
62
22



Minimum

-------
Table l-40a.   PCB 110 (38380-03-9): Summaries of concentrations in NC multimedia
                 samples collected from the homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
N
128
66
62
20
127
65
62
13
129
66
63
12
121
66
55
20
121
66
55
20
28
10
18
1
18
10
8

10
6
4

96
66
30
31
97
66
31
129
66
63
23



126
64
62
22



% Detected
40.6
47.0
33.9
50.0
16.5
15.4
17.7
46.2
7.0
6.1
7.9
8.3
37.2
36.4
38.2
70.0
37.2
36.4
38.2
70.0
21.4
10.0
27.8
0.0
27.8
20.0
37.5

10.0
16.7
0.0

14.6
21.2
0.0
6.5
11.3
15.2
3.2
0.0
0.0
0.0
0.0



0.0
0.0
0.0
0.0



Arithmetic Mean
-
-
-
0.128
-
-
-
-
-
-
-
-
-
-
-
8.16
-
-
-
67.5
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Std. Dev.
-
-
-
0.155
-
-
-
-
-
-
-
-
-
-
-
7.23
-
-
-
131
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Geometric
Mean
-
-
-
0.075
-
-
-
-
-
-
-
-
-
-
-
5.18
-
-
-
22.9
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Log Std. Dev.
-
-
-
1.03
-
-
-
-
-
-
-
-
-
-
-
1.05
-
-
-
1.52
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations.  This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do not
enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     1-82

-------
Table l-40b.  PCB  110 (38380-03-9):  Range of Reported Concentrations in NC multimedia
                samples collected from the homes and day care centers of preschool
                children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
128
66
62
20
127
65
62
13
129
66
63
12
121
66
55
20
121
66
55
20
28
10
18
1
18
10
8

10
6
4

96
66
30
31
97
66
31
129
66
63
23



126
64
62
22



Minimum

-------
Table 1-41 a.   PCB 118 (31508-00-6): Summaries of concentrations in NC multimedia
                 samples collected from the homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
20
121
66
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
129
66
63
23



126
64
62
22



% Detected
23.4
25.8
21.0
25.0
6.3
3.1
9.7
30.8
4.7
4.5
4.8
15.4
24.0
24.2
23.6
40.0
24.0
24.2
23.6
40.0
10.7
10.0
11.1
0.0
16.7
0.0
37.5

33.3
30.0
37.5

11.5
16.7
0.0
0.0
7.2
9.1
3.2
0.0
0.0
0.0
0.0



0.0
0.0
0.0
0.0



Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations.  This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries.  Reported measures of 0 ng/mL in liquid food do not
enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     1-84

-------
Table 1-41 b.   PCB 118 (31508-00-6):  Range of Reported Concentrations in NC multimedia
                 samples collected from the homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
20
121
66
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
129
66
63
23



126
64
62
22



Minimum

-------
Table l-42a.   PCB 138 (35065-28-2): Summaries of concentrations in NC multimedia
                 samples collected from the homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
20
121
66
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
129
66
63
23



126
64
62
22



% Detected
12.5
13.6
11.3
15.0
1.6
0.0
3.2
15.4
9.3
9.1
9.5
15.4
18.2
18.2
18.2
30.0
18.2
18.2
18.2
30.0
3.6
0.0
5.6
0.0
0.0
0.0
0.0

0.0
0.0
0.0

3.1
4.5
0.0
0.0
2.1
3.0
0.0
0.0
0.0
0.0
0.0



0.0
0.0
0.0
0.0



Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations.  This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do not
enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     1-86

-------
Table l-42b.  PCB  138 (35065-28-2):  Range of Reported Concentrations in NC multimedia
                samples collected from the homes and day care centers of preschool
                children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
20
121
66
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
129
66
63
23



126
64
62
22



Minimum

-------
Table l-43a.   PCB 153 (35065-27-1): Summaries of concentrations in NC multimedia
                 samples collected from the homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
20
121
66
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
129
66
63
23



126
64
62
22



% Detected
20.3
19.7
21.0
25.0
1.6
0.0
3.2
15.4
9.3
9.1
9.5
7.7
28.9
30.3
27.3
40.0
28.9
30.3
27.3
40.0
3.6
0.0
5.6
0.0
11.1
10.0
12.5

16.7
20.0
12.5

5.2
7.6
0.0
0.0
3.1
4.5
0.0
0.0
0.0
0.0
0.0



0.0
0.0
0.0
0.0



Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations.  This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do not
enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     1-8

-------
Table l-43b.  PCB  153 (35065-27-1):  Range of Reported Concentrations in NC multimedia
                samples collected from the homes and day care centers of preschool
                children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
20
121
66
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
129
66
63
23



126
64
62
22



Minimum

-------
Table l-44a.   PCB 180 (35065-29-3): Summaries of concentrations in NC multimedia
                 samples collected from the homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
20
121
66
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
129
66
63
23



126
64
62
22



% Detected
5.5
4.5
6.5
0.0
0.0
0.0
0.0
7.7
7.8
9.1
6.3
7.7
10.7
10.6
10.9
20.0
10.7
10.6
10.9
20.0
3.6
0.0
5.6
0.0
0.0
0.0
0.0

5.6
10.0
0.0

1.0
1.5
0.0
0.0
1.0
1.5
0.0
0.0
0.0
0.0
0.0



0.0
0.0
0.0
0.0



Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations.  This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do not
enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     1-90

-------
Table l-44b.  PCB  180 (35065-29-3):  Range of Reported Concentrations in NC multimedia
                samples collected from the homes and day care centers of preschool
                children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
20
121
66
55
20
28
10
18
1
18
10
8

18
10
8

96
66
30
31
97
66
31
129
66
63
23



126
64
62
22



Minimum

-------
Table l-45a.   2.4.5-T (2.4.5-trichlorophenoxyacetic acid) (93-76-5): Summaries of
                 concentrations in  NC multimedia samples collected from the homes and day
                 care centers of preschool children who stay at home or attend day care
                 during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
128
66
62
20
126
65
61
13
126
65
61
13
121
66
55
20
121
66
55
20
13

13
1








98
66
32
32
98
66
32
129
66
63
24
128
66
62
125
64
61
23
120
64
56
% Detected
7.0
7.6
6.5
5.0
8.7
10.8
6.6
7.7
0.8
1.5
0.0
0.0
0.0
0.0
0.0
5.0
0.0
0.0
0.0
5.0
0.0

0.0
0.0








0.0
0.0
0.0
0.0
0.0
0.0
0.0
1.6
3.0
0.0
0.0
0.8
0.0
1.6
0.0
0.0
0.0
0.0
0.0
0.0
0.0
Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-








-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-








-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-








-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-








-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries.  Reported measures of 0 ng/mL in liquid food do not
enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                    1-92

-------
Table l-45b.   2.4.5-T (2.4.5-trichlorophenoxyacetic acid) (93-76-5):  Range of Reported
                Concentrations in NC multimedia samples collected from the homes and
                day care centers of preschool children who stay at home or attend day care
                during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
128
66
62
20
126
65
61
13
126
65
61
13
121
66
55
20
121
66
55
20
13
0
13
1




0
0
0
0
98
66
32
32
98
66
32
129
66
63
24
128
66
62
125
64
61
23
120
64
56
Minimum

-------
Table l-46a.   3.5.6-TCP (3.5.6-trichloro-2-pyridinol) (6515-38-4): Summaries of
                 concentrations in NC multimedia samples collected from the homes and day
                 care centers of preschool children who stay at home or attend day care
                 during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
20
121
66
55
20
13

13
1








99
66
33
32
98
66
32
128
66
62
24
129
66
63
127
65
62
24
121
64
57
% Detected
99.2
98.5
100.0
95.0
89.0
92.3
85.5
76.9
71.3
63.6
79.4
46.2
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0

100.0
100.0








100.0
100.0
100.0
87.5
100.0
100.0
100.0
98.4
98.5
98.4
100.0
98.4
98.5
98.4
41.7
47.7
35.5
58.3
35.5
35.9
35.1
Arithmetic Mean
5.00
3.63
6.46
2.61
0.466
0.421
0.513
0.211
3.61
4.18
3.02
-
309
282
341
93.9
1,050
609
1,580
836
65.9

65.9
52.5








230
238
213
122
125
124
128
3.05
3.52
2.55
3.78
3.65
3.71
3.59
-
-
-
0.088
-
-
-
Std. Dev.
13.3
7.14
17.6
3.26
0.951
0.667
1.18
0.193
14.9
15.9
13.9
-
791
577
994
100
3,810
1,400
5,410
1,260
63.5

63.5









215
247
130
75.7
127
149
61.8
2.79
3.23
2.14
3.34
3.92
4.02
3.83
-
-
-
0.076
-
-
-
Geometric
Mean
1.91
1.57
2.36
1.08
0.251
0.247
0.257
0.143
0.616
0.513
0.746
-
105
110
99.1
51.0
109
104
116
226
48.3

48.3
52.5








181
184
176
99.4
93.3
84.8
114
2.09
2.46
1.77
2.83
2.41
2.45
2.36
-
-
-
0.046
-
-
-
Log Std. Dev.
1.30
1.27
1.32
1.47
0.963
0.927
1.01
0.942
1.44
1.56
1.29
-
1.37
1.37
1.38
1.30
2.24
2.23
2.26
1.86
0.771

0.771









0.655
0.659
0.657
0.681
0.724
0.793
0.510
0.972
0.951
0.972
0.843
0.996
0.980
1.02
-
-
-
1.34
-
-
-
a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries.  Reported measures of 0 ng/mL in liquid food do not
enter into the descriptive statistics.  Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     1-94

-------
Table l-46b.   3.5.6-TCP (3.5.6-trichloro-2-pyridinol) (6515-38-4):  Range of Reported
                Concentrations in NC multimedia samples collected from the homes and
                day care centers of preschool children who stay at home or attend day care
                during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
128
66
62
20
127
65
62
13
129
66
63
13
121
66
55
20
121
66
55
20
13

13
1








99
66
33
32
98
66
32
128
66
62
24
129
66
63
127
65
62
24
121
64
57
Minimum

-------

-------
                         Appendix J
Descriptive Statistics of CTEPP Pollutant/Metabolite Measurements
                  in OH Multimedia Samples
                             J-l

-------
J-2

-------
This appendix contains tables of descriptive statistics of OH multimedia data for the following pollutants
and metabolites:
Pollutant/Metabolite
Aldrin
Atrazine
Benz[a]anthracene
Benzo[£>]fluoranthene
Benzo[/(]fluoranthene
Benzo[g/?/]perylene
Benzo[a]pyrene
Benzo[e]pyrene
Benzylbutylphthalate
Bisphenol-A
a/p/?a-Chlordane
gamma-Chlordane
Chlorpyrifos
Chrysene
Cyfluthrin
Diazinon
Dibenzo[a,/?]anthracene
Di-n-butylphthalate
Dicamba
p,p'-DDE
p,p'-DDT
2,4-D
Dieldrin

Table Numbers
Tables J-1a, J-1b
Tables J-2a, J-2b
Tables J-3a, J-3b
Tables J-4a, J-4b
Tables J-5a, J-5b
Tables J-6a, J-6b
Tables J-7a, J-7b
Tables J-8a, J-8b
Tables J-9a, J-9b
Tables J-10a, J-1 Ob
Tables J-11 a, J-11b
Tables J-12a, J-12b
Tables J-1 3a, J-1 3b
Tables J-14a, J-14b
Tables J-1 5a, J-15b
Tables J-16a, J-16b
Tables J-1 7a, J-17b
Tables J-1 8a, J-1 8b
Tables J-1 9a, J-1 9b
Tables J-20a, J-20b
Tables J-21 a, J-21b
Tables J-22a, J-22b
Tables J-23a, J-23b

Pollutant/Metabolite
Endrin
Heptachlor
lndeno[1 ,2,3-cd]pyrene
IMP
Lindane
Nonylphenol
Pentachloronitrobenzene
Pentachlorophenol
c/s-Permethrin
frans-Permethrin
PCS 44
PCB52
PCS 70
PCB77
PCS 95
PCB 101
PCB 105
PCB 110
PCB 118
PCB 138
PCB 153
PCB 180
2,4,5-T
3,5,6-TCP
Table Numbers
Tables J-24a, J-24b
Tables J-25a, J-25b
Tables J-26a, J-26b
Tables J-27a, J-27b
Tables J-28a, J-28b
Tables J-29a, J-29b
Tables J-30a, J-30b
Tables J-31 a, J-31b
Tables J-32a, J-32b
Tables J-33a, J-33b
Tables J-34a, J-34b
Tables J-35a, J-35b
Tables J-36a, J-36b
Tables J-37a, J-37b
Tables J-38a, J-38b
Tables J-39a, J-39b
Tables J-40a, J-40b
Tables J-41 a, J-41b
Tables J-42a, J-42b
Tables J-43a, J-43b
Tables J-44a, J-44b
Tables J-45a, J-45b
Tables J-46a, J-46b
Tables J-47a, J-47b
For each media type, descriptive statistics are presented separately for the following four groups of
samples:
•      Samples collected at the homes of study participants
       o      Samples collected at the homes of stay-at-home children only
       o      Samples collected at the homes of day-care children only
•      Samples collected at participating day care centers
                                               J-3

-------
Table J-1a.    Aldrin (309-00-2): Summaries of concentrations in OH multimedia samples
                 collected from the homes and day care centers of preschool children who
                 stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
125
69
56
22
127
69
58
16
127
69
58
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
125
69
56
29



126
69
57
28



% Detected
3.2
0.0
7.1
0.0
1.6
1.4
1.7
0.0
2.4
0.0
5.2
0.0
0.8
0.0
1.8
17.4
0.8
0.0
1.8
17.4
4.8
6.7
0.0
0.0
0.0
0.0
0.0

0.0
0.0
0.0

1.0
0.0
3.4
0.0
0.0
0.0
0.0
0.0
0.0
0.0
3.4



0.0
0.0
0.0
3.6



Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



* Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries.  Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics.  Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     J-4

-------
Table J-1b.   Aldrin (309-00-2):  Range of Reported Concentrations in OH multimedia
                samples collected from the homes and day care centers of preschool
                children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
125
69
56
22
127
69
58
16
127
69
58
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
125
69
56
29



126
69
57
28



Minimum

-------
Table J-2a.   Atrazine (1912-24-9): Summaries of concentrations in OH multimedia
                samples collected from the homes and day care centers of preschool
                children who stay at home or attend day care during the day.a
Medium
Drinking
Water
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
N
125
67
58
16
% Detected
56.8
50.7
63.8
75.0
Arithmetic Mean
0.078
0.080
0.076
0.107
Std. Dev.
0.124
0.146
0.095
0.144
Geometric
Mean
0.029
0.026
0.034
0.048
Log Std. Dev.
1.42
1.47
1.36
1.39
a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Means and standard deviations are not reported
when the percentage of detected results is below 50%.
                                                    J-6

-------
Table J-2b.    Atrazine (1912-24-9):  Range of Reported Concentrations in OH multimedia
                 samples collected from the  homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Drinking
Water
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
N
125
67
58
16
Minimum

-------
Table J-3a.    Benzralanthracene (56-55-3): Summaries of concentrations in OH
                 multimedia samples collected from the homes and day care centers of
                 preschool children who stay at home or attend day care during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - atdaycare
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
125
69
56
22
111
60
51
14
126
68
58
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

96
67
29
29
97
69
28
127
69
58
29



126
69
57
28



% Detected
39.2
34.8
44.6
31.8
25.2
21.7
29.4
28.6
90.5
92.6
87.9
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
95.2
93.3
100.0
100.0
30.8
22.2
50.0

61.5
44.4
100.0

61.5
59.7
65.5
58.6
54.6
50.7
64.3
31.5
33.3
29.3
13.8



0.0
0.0
0.0
3.6



Arithmetic Mean
-
-
-
-
-
-
-
-
156
105
216
51.1
1,620
1,390
1,880
1,810
1,740
1,530
1,970
11,100
37.3
26.1
65.2
18.3
-
-
7.70

12.7
-
12.4

149
162
119
191
30.2
30.8
28.8
-
-
-
-



-
-
-
-



Std. Dev.
-
-
-
-
-
-
-
-
369
227
481
76.1
3,780
2,850
4,610
1,490
2,850
3,200
2,410
13,100
34.9
20.9
48.2
18.7
-
-
4.11

16.8
-
2.86

352
411
140
518
34.3
38.9
19.7
-
-
-
-



-
-
-
-



Geometric
Mean
-
-
-
-
-
-
-
-
16.1
13.6
19.6
15.3
575
496
676
1,390
630
443
931
3,700
26.2
20.0
51.1
13.1
-
-
7.01

7.92
-
12.2

65.2
62.6
71.5
62.4
22.5
21.8
24.2
-
-
-
-



-
-
-
-



Log Std. Dev.
-
-
-
-
-
-
-
-
2.43
2.28
2.59
1.81
1.29
1.34
1.23
0.749
1.49
1.54
1.34
1.90
0.861
0.758
0.779
0.964
-
-
0.485

0.930
-
0.225

1.04
1.07
0.986
1.21
0.671
0.708
0.575
-
-
-
-



-
-
-
-



* Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations.  This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     J-8

-------
Table J-3b.   Benzralanthracene (56-55-3):  Range of Reported Concentrations in OH
                multimedia samples collected from the homes and day care centers of
                preschool children who stay at home or attend day care during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
125
69
56
22
111
60
51
14
126
68
58
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

96
67
29
29
97
69
28
127
69
58
29



126
69
57
28



Minimum

-------
Table J-4a.    BenzoHblfluoranthene (205-99-2): Summaries of concentrations in OH
                 multimedia samples collected from the homes and day care centers of
                 preschool children who stay at home or attend day care during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - atdaycare
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
125
69
56
22
127
69
58
16
126
68
58
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

96
67
29
29
97
69
28
127
69
58
29



126
69
57
28



% Detected
27.2
21.7
33.9
27.3
35.4
27.5
44.8
43.8
90.5
91.2
89.7
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
95.2
93.3
100.0
100.0
46.2
33.3
75.0

92.3
88.9
100.0

83.3
82.1
86.2
82.8
71.1
69.6
75.0
40.9
40.6
41.4
31.0



0.8
0.0
1.8
7.1



Arithmetic Mean
-
-
-
-
-
-
-
-
253
189
329
87.4
3,820
3,170
4,540
4,740
4,240
3,900
4,630
30,500
87.0
63.1
147
90.5
-
-
14.5

46.7
47.3
45.1

419
494
245
464
69.8
77.0
52.1
-
-
-
-



-
-
-
-



Std. Dev.
-
-
-
-
-
-
-
-
565
385
718
126
8,820
5,970
1 1 ,200
3,780
7,470
8,860
5,610
35,700
77.6
50.3
105
63.8
-
-
8.17

68.8
82.4
28.5

1,100
1,300
250
1,120
92.3
105
42.8
-
-
-
-



-
-
-
-



Geometric
Mean
-
-
-
-
-
-
-
-
27.0
24.4
30.4
29.6
1,470
1,330
1,640
3,700
1,610
1,180
2,260
9,830
56.8
43.3
112
73.8
-
-
12.5

23.2
18.3
39.9

156
160
148
135
41.9
43.2
38.8
-
-
-
-



-
-
-
-



Log Std. Dev.
-
-
-
-
-
-
-
-
2.49
2.36
2.65
1.67
1.23
1.24
1.22
0.722
1.43
1.46
1.32
1.90
1.04
1.00
0.860
0.823
-
-
0.681

1.21
1.36
0.547

1.24
1.31
1.08
1.44
0.970
1.04
0.792
-
-
-
-



-
-
-
-



* Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                    J-10

-------
Table J-4b.   BenzoFblfluoranthene (205-99-2):  Range of Reported Concentrations in OH
                multimedia samples collected from the homes and day care centers of
                preschool children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
125
69
56
22
127
69
58
16
126
68
58
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

96
67
29
29
97
69
28
127
69
58
29



126
69
57
28



Minimum

-------
Table J-5a.    Benzo|7clfluoranthene (207-08-9): Summaries of concentrations in OH
                 multimedia samples collected from the homes and day care centers of
                 preschool children who stay at home or attend day care during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - atdaycare
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
125
69
56
22
127
69
58
16
126
68
58
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4
13
9
4


96
67
29
29
97
69
28
127
69
58
29



126
69
57
28



% Detected
20.8
14.5
28.6
22.7
24.4
20.3
29.3
31.3
91.3
91.2
91.4
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
90.5
86.7
100.0
100.0
38.5
33.3
50.0
84.6
77.8
100.0


77.1
74.6
82.8
58.6
61.9
63.8
57.1
18.1
17.4
19.0
6.9



0.0
0.0
0.0
7.1



Arithmetic Mean
-
-
-
-
-
-
-
-
95.5
71.3
124
35.0
1,360
1,170
1,570
1,700
1,490
1,400
1,590
10,300
37.6
28.2
61.2
28.5
-
-
7.32
18.3
19.4
15.6


174
184
151
177
36.9
38.6
32.7
-
-
-
-



-
-
-
-



Std. Dev.
-
-
-
-
-
-
-
-
207
143
262
46.9
3,070
2,270
3,770
1,300
2,620
3,150
1,890
12,100
32.2
23.4
41.1
27.8
-
-
3.49
28.2
34.1
7.64


384
449
157
342
37.7
41.8
25.3
-
-
-
-



-
-
-
-



Geometric
Mean
-
-
-
-
-
-
-
-
13.2
11.4
15.7
13.6
521
478
574
1,360
572
426
790
3,620
25.8
20.1
48.4
20.4
-
-
6.78
10.4
8.97
14.3


82.6
78.9
91.9
71.8
26.5
27.0
25.4
-
-
-
-



-
-
-
-



Log Std. Dev.
-
-
-
-
-
-
-
-
2.21
2.12
2.32
1.60
1.24
1.26
1.23
0.686
1.40
1.44
1.29
1.77
0.934
0.885
0.797
0.993
-
-
0.437
0.988
1.14
0.482


1.04
1.05
1.02
1.23
0.755
0.781
0.697
-
-
-
-



-
-
-
-



a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                    J-12

-------
Table J-5b.   Benzo|7clfluoranthene (207-08-9):  Range of Reported Concentrations in OH
                multimedia samples collected from the homes and day care centers of
                preschool children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
125
69
56
22
127
69
58
16
126
68
58
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

96
67
29
29
97
69
28
127
69
58
29



126
69
57
28



Minimum

-------
Table J-6a.    Benzorqfo/lperylene (191-24-2):  Summaries of concentrations in OH
                 multimedia samples collected from the homes and day care centers of
                 preschool children who stay at home or attend day care during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
125
69
56
22
127
69
58
16
126
68
58
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

96
67
29
29
97
69
28
127
69
58
29



126
69
57
28



% Detected
26.4
18.8
35.7
27.3
22.0
20.3
24.1
31.3
89.7
91.2
87.9
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
90.5
86.7
100.0
100.0
30.8
22.2
50.0

84.6
77.8
100.0

79.2
77.6
82.8
72.4
63.9
66.7
57.1
4.7
2.9
6.9
0.0



0.0
0.0
0.0
0.0



Arithmetic Mean
-
-
-
-
-
-
-
-
131
96.4
171
43.9
1,950
1,670
2,260
2,530
2,200
2,000
2,410
16,800
50.5
36.3
86.1
37.6
-
-
8.27

33.0
34.7
29.4

252
263
227
218
40.6
44.2
31.8
-
-
-
-



-
-
-
-



Std. Dev.
-
-
-
-
-
-
-
-
297
198
381
64.7
4,310
3,220
5,280
1,800
3,720
4,370
2,860
19,500
42.8
27.8
55.2
40.9
-
-
5.10

49.5
59.9
13.5

529
609
271
422
48.6
55.3
23.9
-
-
-
-



-
-
-
-



Geometric
Mean
-
-
-
-
-
-
-
-
14.5
13.0
16.5
13.9
780
709
866
2,030
855
632
1,190
5,390
33.9
25.7
67.2
25.5
-
-
7.31

17.0
13.9
26.9

108
101
124
86.8
28.0
29.2
25.3
-
-
-
-



-
-
-
-



Log Std. Dev.
-
-
-
-
-
-
-
-
2.37
2.26
2.51
1.75
1.22
1.22
1.22
0.700
1.42
1.45
1.32
1.92
0.995
0.936
0.850
1.04
-
-
0.551

1.18
1.36
0.492

1.17
1.19
1.14
1.24
0.781
0.825
0.664
-
-
-
-



-
-
-
-



* Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                    J-14

-------
Table J-6b.   Benzorqfo/lperylene (191-24-2):  Range of Reported Concentrations in OH
                multimedia samples collected from the homes and day care centers of
                preschool children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
125
69
56
22
127
69
58
16
126
68
58
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

96
67
29
29
97
69
28
127
69
58
29



126
69
57
28



Minimum

-------
Table J-7a.    Benzolalpyrene (50-32-8): Summaries of concentrations in OH multimedia
                 samples collected from the homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - atdaycare
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
125
69
56
22
127
69
58
16
126
68
58
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

96
67
29
29
97
69
28
127
69
58
29



126
69
57
28



% Detected
18.4
10.1
28.6
18.2
15.0
17.4
12.1
18.8
89.7
91.2
87.9
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
85.7
80.0
100.0
100.0
30.8
22.2
50.0

84.6
77.8
100.0

69.8
67.2
75.9
65.5
57.7
59.4
53.6
18.9
18.8
19.0
10.3



0.0
0.0
0.0
0.0



Arithmetic Mean
-
-
-
-
-
-
-
-
173
121
234
57.8
2,220
1,870
2,590
2,340
2,300
2,030
2,610
14,100
42.1
30.4
71.4
23.3
-
-
7.92

25.9
26.2
25.3

234
263
167
259
38.5
41.1
32.2
-
-
-
-



-
-
-
-



Std. Dev.
-
-
-
-
-
-
-
-
411
258
535
88.7
5,260
3,790
6,530
1,840
3,750
4,160
3,240
16,400
39.8
25.5
55.5
21.0
-
-
4.68

36.5
44.3
9.79

622
733
202
610
46.9
52.2
29.9
-
-
-
-



-
-
-
-



Geometric
Mean
-
-
-
-
-
-
-
-
17.3
14.9
20.7
16.3
793
706
902
1,820
870
630
1,240
4,830
27.7
21.1
54.5
17.4
-
-
7.08

14.1
11.1
23.9

88.7
85.9
95.6
83.5
26.3
27.1
24.3
-
-
-
-



-
-
-
-



Log Std. Dev.
-
-
-
-
-
-
-
-
2.46
2.34
2.61
1.87
1.28
1.30
1.25
0.728
1.45
1.49
1.33
1.85
0.996
0.949
0.822
0.938
-
-
0.522

1.12
1.28
0.393

1.16
1.21
1.07
1.31
0.784
0.816
0.706
-
-
-
-



-
-
-
-



* Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations.  This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                    J-16

-------
Table J-7b.   Benzolalpyrene (50-32-8): Range of Reported Concentrations in OH
                multimedia samples collected from the homes and day care centers of
                preschool children who stay at home or attend  day care during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
125
69
56
22
127
69
58
16
126
68
58
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

96
67
29
29
97
69
28
127
69
58
29



126
69
57
28



Minimum

-------
Table J-8a.    Benzorelpyrene (192-97-2): Summaries of concentrations in OH multimedia
                 samples collected from the homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - atdaycare
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
125
69
56
22
127
69
58
16
126
68
58
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

96
67
29
29
97
69
28
127
69
58
29



126
69
57
28



% Detected
21.6
14.5
30.4
22.7
25.2
23.2
27.6
31.3
89.7
91.2
87.9
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
95.2
93.3
100.0
100.0
38.5
33.3
50.0

92.3
88.9
100.0

82.3
80.6
86.2
82.8
69.1
68.1
71.4
21.3
18.8
24.1
10.3



0.0
0.0
0.0
3.6



Arithmetic Mean
-
-
-
-
-
-
-
-
127
92.5
167
47.1
2,050
1,740
2,380
2,500
2,270
2,080
2,470
16,300
58.4
40.0
104
47.9
-
-
8.44

26.2
26.4
25.7

250
275
192
240
51.0
56.3
38.1
-
-
-
-



-
-
-
-



Std. Dev.
-
-
-
-
-
-
-
-
279
190
354
71.7
4,640
3,350
5,750
1,880
3,920
4,640
2,940
19,100
54.3
31.4
74.0
40.0
-
-
5.58

34.9
42.5
7.28

555
652
199
496
54.5
61.1
30.4
-
-
-
-



-
-
-
-



Geometric
Mean
-
-
-
-
-
-
-
-
15.3
13.7
17.5
14.8
801
732
886
1,990
878
653
1,220
5,290
38.1
28.8
76.8
37.4
-
-
7.35

15.7
12.8
25.0

114
112
119
92.4
34.6
36.9
29.6
-
-
-
-



-
-
-
-



Log Std. Dev.
-
-
-
-
-
-
-
-
2.33
2.19
2.50
1.74
1.21
1.22
1.21
0.703
1.41
1.44
1.31
1.89
1.00
0.900
0.955
0.869
-
-
0.578

1.01
1.16
0.262

1.10
1.14
1.02
1.23
0.852
0.902
0.704
-
-
-
-



-
-
-
-



* Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                    J-18

-------
Table J-8b.   Benzorelpyrene (192-97-2):  Range of Reported Concentrations in OH
                multimedia samples collected from the homes and day care centers of
                preschool children who stay at home or attend day care during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
125
69
56
22
127
69
58
16
126
68
58
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

96
67
29
29
97
69
28
127
69
58
29



126
69
57
28



Minimum

-------
Table J-9a.    Benzylbutylphthalate (85-68-7): Summaries of concentrations in OH
                 multimedia samples collected from the homes and day care centers of
                 preschool children who stay at home or attend day care during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - atdaycare
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
125
69
56
22
126
69
57
16
127
69
58
16
118
62
56
23
118
62
56
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
91
47
44
15



97
51
46
25



% Detected
32.8
24.6
42.9
31.8
9.5
10.1
8.8
18.8
37.8
46.4
27.6
31.3
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
76.2
66.7
100.0
100.0
53.8
44.4
75.0

100.0
100.0
100.0

46.4
41.2
58.6
41.4
46.4
46.4
46.4
58.2
48.9
68.2
53.3



7.2
7.8
6.5
4.0



Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
29,400
23,600
35,800
56,300
55,400
33,000
80,100
356,000
113,000
21,200
342,000
438,000
3,090
-
4,550

6,460
5,050
9,630

-
-
22,100
-
-
-
-
36.1
-
38.7
36.6



-
-
-
-



Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
44,500
26,300
58,000
96,500
112,000
57,000
148,000
613,000
265,000
44,700
432,000
399,000
2,420
-
3,350

3,750
2,080
5,020

-
-
21,100
-
-
-
-
59.5
-
56.3
85.6



-
-
-
-



Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
16,700
14,600
19,300
35,400
17,500
12,300
25,900
94,000
10,800
5,200
66,000
339,000
2,390
-
3,570

5,660
4,680
8,680

-
-
14,900
-
-
-
-
14.1
-
17.2
11.7



-
-
-
-



Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
1.06
0.993
1.12
0.802
1.51
1.43
1.52
1.83
2.23
1.59
2.70
0.846
0.730
-
0.845

0.526
0.422
0.528

-
-
0.886
-
-
-
-
1.31
-
1.28
1.33



-
-
-
-



* Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations.  This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                    J-20

-------
Table J-9b.   Benzylbutylphthalate (85-68-7):  Range of Reported Concentrations in OH
                multimedia samples collected from the homes and day care centers of
                preschool children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
125
69
56
22
126
69
57
16
127
69
58
16
118
62
56
23
118
62
56
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
91
47
44
15



97
51
46
25



Minimum

-------
Table J-10a.   Bisphenol-A (80-05-7): Summaries of concentrations in OH multimedia
                 samples collected from the homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - atdaycare
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
125
69
56
22
103
59
44
16
126
68
58
14
116
61
55
23
116
61
55
23
21
15
6
3
13
9
4

7
5
2

97
68
29
29
97
69
28
127
69
58
29



111
58
53
25



% Detected
63.2
59.4
67.9
72.7
34.0
30.5
38.6
43.8
2.4
2.9
1.7
0.0
47.4
54.1
40.0
69.6
47.4
54.1
40.0
69.6
95.2
93.3
100.0
100.0
84.6
88.9
75.0

71.4
60.0
100.0

99.0
98.5
100.0
89.7
99.0
98.6
100.0
100.0
100.0
100.0
100.0



69.4
70.7
67.9
80.0



Arithmetic Mean
2.19
1.69
2.80
1.29
-
-
-
-
-
-
-
-
-
60.0
-
41.2
-
76.9
-
213
2,660
1,190
6,340
450
940
527
1,870

269
166
526

7,810
8,530
6,120
5,070
6,420
6,650
5,870
7.60
5.75
9.80
4.38



0.761
0.648
0.884
0.848



Std. Dev.
3.98
3.76
4.19
1.44
-
-
-
-
-
-
-
-
-
84.4
-
26.6
-
217
-
235
5,360
2,730
8,440
186
1,030
418
1,450

275
181
372

10,200
1 1 ,800
4,550
8,780
7,190
7,530
6,370
16.8
6.22
23.9
3.73



1.66
0.759
2.28
1.01



Geometric
Mean
1.25
1.05
1.53
0.992
-
-
-
-
-
-
-
-
-
39.9
-
34.8
-
32.2
-
92.6
789
446
3,280
425
411
290
894

145
91.4
455

5,410
5,660
4,870
2,140
4,100
4,120
4,070
3.98
3.76
4.26
3.36



0.279
0.279
0.279
0.425



Log Std. Dev.
0.856
0.710
0.975
0.642
-
-
-
-
-
-
-
-
-
0.792
-
0.573
-
1.04
-
1.54
1.53
1.26
1.24
0.410
1.76
1.66
1.96

1.33
1.26
0.778

0.835
0.890
0.694
1.68
0.981
1.03
0.861
0.961
0.902
1.03
0.728



1.60
1.60
1.61
1.44



* Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations.  This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                    J-22

-------
Table J-1 Ob.   Bisphenol-A (80-05-7):  Range of Reported Concentrations in OH
                 multimedia samples collected from the homes and day care centers of
                 preschool children who stay at home or attend day care during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
125
69
56
22
103
59
44
16
126
68
58
14
116
61
55
23
116
61
55
23
21
15
6
3
13
9
4

7
5
2

97
68
29
29
97
69
28
127
69
58
29



111
58
53
25



Minimum

-------
Table J-11a.   a/pfra-Chlordane (5103-71-9): Summaries of concentrations in OH
                 multimedia samples collected from the homes and day care centers of
                 preschool children who stay at home or attend day care during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
125
69
56
22
127
69
58
16
127
69
58
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
125
69
56
29



126
69
57
28



% Detected
92.8
92.8
92.9
95.5
55.9
59.4
51.7
56.3
56.7
59.4
53.4
37.5
84.2
84.1
84.2
95.7
84.2
84.1
84.2
95.7
28.6
20.0
50.0
0.0
15.4
22.2
0.0

23.1
22.2
25.0

30.9
33.8
24.1
3.4
34.0
37.7
25.0
8.0
11.6
3.6
3.4



0.0
0.0
0.0
0.0



Arithmetic Mean
1.15
1.44
0.796
0.237
0.233
0.215
0.254
0.098
59.5
24.6
101
-
44.1
61.0
25.4
13.2
86.4
108
62.8
85.5
-
-
8.11
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Std. Dev.
2.69
3.35
1.50
0.190
0.606
0.277
0.848
0.098
440
83.8
645
-
118
157
42.5
7.49
250
321
133
86.2
-
-
4.36
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Geometric
Mean
0.370
0.400
0.336
0.193
0.126
0.135
0.115
0.075
1.57
1.66
1.47
-
13.4
16.0
11.0
11.5
14.6
14.2
15.1
30.7
-
-
7.26
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Log Std. Dev.
1.30
1.39
1.19
0.628
0.873
0.877
0.868
0.676
2.02
1.99
2.08
-
1.36
1.45
1.23
0.514
1.80
1.90
1.69
1.83
-
-
0.501
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



* Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                    J-24

-------
Table J-11b.  a/pfra-Chlordane (5103-71-9):  Range of Reported Concentrations in OH
                multimedia samples collected from the homes and day care centers of
                preschool children who stay at home or attend day care during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
125
69
56
22
127
69
58
16
127
69
58
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
125
69
56
29



126
69
57
28



Minimum

-------
Table J-12a.   qa/n/na-Chlordane (5103-74-2): Summaries of concentrations in OH
                 multimedia samples collected from the homes and day care centers of
                 preschool children who stay at home or attend day care during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
125
69
56
22
127
69
58
16
127
69
58
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
125
69
56
29



126
69
57
28



% Detected
96.0
95.7
96.4
100.0
58.3
62.3
53.4
62.5
52.8
58.0
46.6
37.5
83.3
82.5
84.2
95.7
83.3
82.5
84.2
95.7
28.6
20.0
50.0
0.0
15.4
22.2
0.0

23.1
22.2
25.0

32.0
35.3
24.1
3.4
34.0
37.7
25.0
6.4
10.1
1.8
3.4



0.0
0.0
0.0
0.0



Arithmetic Mean
1.84
2.42
1.13
0.320
0.260
0.235
0.290
0.104
62.8
22.2
-
-
50.3
70.4
28.2
15.1
92.6
114
69.0
99.6
-
-
7.75
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Std. Dev.
5.72
7.44
2.12
0.233
0.704
0.290
0.997
0.101
504
82.5
-
-
135
179
48.7
8.17
257
324
151
104
-
-
4.30
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Geometric
Mean
0.505
0.542
0.463
0.263
0.135
0.147
0.122
0.080
1.34
1.39
-
-
14.4
17.2
11.8
13.2
15.8
15.3
16.3
35.2
-
-
6.99
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Log Std. Dev.
1.36
1.46
1.22
0.623
0.909
0.898
0.920
0.667
1.97
1.90
-
-
1.39
1.50
1.25
0.523
1.83
1.94
1.72
1.86
-
-
0.471
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                    J-26

-------
Table J-12b.  qa/n/na-Chlordane (5103-74-2):  Range of Reported Concentrations in OH
                multimedia samples collected from the homes and day care centers of
                preschool children who stay at  home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
125
69
56
22
127
69
58
16
127
69
58
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
125
69
56
29



126
69
57
28



Minimum

-------
Table J-13a.   Chlorpyrifos (2921-88-2):  Summaries of concentrations in OH multimedia
                 samples collected from the homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - atdaycare
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
125
69
56
22
112
60
52
14
127
69
58
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
125
69
56
29



126
69
57
28



% Detected
98.4
98.6
98.2
100.0
75.0
85.0
63.5
71.4
39.4
52.2
24.1
37.5
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
85.7
80.0
100.0
33.3
61.5
66.7
50.0

84.6
77.8
100.0

57.7
57.4
58.6
62.1
62.9
60.9
67.9
65.6
71.0
58.9
69.0



6.3
7.2
5.3
10.7



Arithmetic Mean
6.42
6.40
6.44
5.20
0.420
0.415
0.425
0.154
-
46.3
-
-
871
415
1,380
272
1,060
283
1,920
1,910
1,940
118
6,510
-
677
126
1,920

2,500
29.0
8,070

1,810
298
5,360
362
452
137
1,230
0.380
0.331
0.441
0.204



-
-
-
-



Std. Dev.
14.8
14.9
14.9
5.59
0.785
0.847
0.715
0.112
-
352
-
-
5,030
2,160
6,940
285
5,400
759
7,740
3,330
8,410
270
15,700
-
2,110
315
3,810

8,920
47.1
16,100

15,000
620
27,400
1,060
2,890
271
5,340
0.608
0.499
0.720
0.190



-
-
-
-



Geometric
Mean
2.16
2.00
2.38
2.92
0.219
0.238
0.198
0.118
-
1.47
-
-
70.4
64.5
77.6
168
77.2
57.5
107
445
42.9
27.4
132
-
25.4
19.7
44.6

25.8
12.0
143

110
103
129
101
56.1
47.9
82.7
0.193
0.192
0.194
0.145



-
-
-
-



Log Std. Dev.
1.35
1.37
1.33
1.13
1.04
0.917
1.17
0.781
-
1.74
-
-
1.63
1.45
1.81
1.01
1.93
1.63
2.18
1.91
2.17
1.62
3.06
-
2.30
1.77
3.50

2.43
1.34
3.63

1.56
1.36
1.97
1.39
1.55
1.34
1.93
1.10
0.989
1.23
0.817



-
-
-
-



* Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations.  This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                    J-28

-------
Table J-13b.  Chlorpyrifos (2921-88-2): Range of Reported Concentrations in OH
                multimedia samples collected from the homes and day care centers of
                preschool children who stay at home or attend day care during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
125
69
56
22
112
60
52
14
127
69
58
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
125
69
56
29



126
69
57
28



Minimum

-------
Table J-14a.   Chrysene (218-01-9): Summaries of concentrations in OH multimedia
                 samples collected from the homes and day care centers  of preschool
                 children who stay at home or attend day care during the  day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - atdaycare
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
125
69
56
22
110
58
52
15
126
68
58
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

96
67
29
29
97
69
28
127
69
58
29



126
69
57
28



% Detected
39.2
30.4
50.0
59.1
46.4
43.1
50.0
73.3
92.1
92.6
91.4
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
95.2
93.3
100.0
100.0
46.2
33.3
75.0

84.6
77.8
100.0

79.2
77.6
82.8
82.8
70.1
66.7
78.6
38.6
42.0
34.5
24.1



0.0
0.0
0.0
3.6



Arithmetic Mean
-
-
0.227
0.091
-
-
0.142
0.139
145
102
196
57.1
2,240
1,860
2,660
2,630
2,390
2,240
2,550
16,000
71.6
50.1
125
94.3
-
-
10.8

25.0
25.6
23.5

247
258
222
271
46.1
48.0
41.3
-
-
-
-



-
-
-
-



Std. Dev.
-
-
0.426
0.047
-
-
0.115
0.118
316
208
404
86.2
5,400
3,700
6,810
2,060
4,250
5,080
3,120
18,900
62.5
41.8
76.8
67.4
-
-
5.75

34.0
41.5
5.42

467
536
246
579
52.3
59.7
26.6
-
-
-
-



-
-
-
-



Geometric
Mean
-
-
0.123
0.082
-
-
0.109
0.104
17.9
15.7
20.9
18.7
802
729
892
2,050
879
650
1,230
5,450
47.6
35.3
100
68.1
-
-
9.68

14.0
11.2
23.0

108
102
123
104
31.9
31.1
33.8
-
-
-
-



-
-
-
-



Log Std. Dev.
-
-
0.927
0.458
-
-
0.688
0.773
2.32
2.17
2.50
1.69
1.26
1.27
1.25
0.735
1.44
1.49
1.32
1.85
1.00
0.938
0.800
1.14
-
-
0.562

1.10
1.26
0.253

1.17
1.19
1.14
1.24
0.802
0.856
0.660
-
-
-
-



-
-
-
-



* Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations.  This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                    J-30

-------
Table J-14b.  Chrysene (218-01-9): Range of Reported Concentrations in OH multimedia
                samples collected from the  homes and day care centers of preschool
                children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
125
69
56
22
110
58
52
15
126
68
58
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

96
67
29
29
97
69
28
127
69
58
29



126
69
57
28



Minimum

-------
Table J-15a.   Cyfluthrin (68359-37-5): Summaries of concentrations in OH multimedia
                 samples collected from the homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
125
69
56
22
125
67
58
16
127
69
58
16
119
63
56
23
119
63
56
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
125
69
56
29



126
69
57
28



% Detected
1.6
0.0
3.6
9.1
0.8
0.0
1.7
0.0
17.3
17.4
17.2
25.0
73.9
79.4
67.9
73.9
73.9
79.4
67.9
73.9
9.5
6.7
16.7
0.0
0.0
0.0
0.0

0.0
0.0
0.0

11.3
14.7
3.4
0.0
4.1
4.3
3.6
3.2
2.9
3.6
0.0



0.8
0.0
1.8
0.0



Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
329
346
310
389
557
477
648
3,710
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
482
498
467
323
1,040
994
1,100
4,990
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
148
161
134
221
160
144
180
587
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
1.35
1.30
1.42
1.32
1.72
1.57
1.88
2.67
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



* Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations.  This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries.  Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                    J-32

-------
Table J-15b.  Cyfluthrin (68359-37-5):  Range of Reported Concentrations in OH
                multimedia samples collected from the homes and day care centers of
                preschool children who stay at home or attend day care during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
125
69
56
22
125
67
58
16
127
69
58
16
119
63
56
23
119
63
56
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
125
69
56
29



126
69
57
28



Minimum

-------
Table J-16a.   Diazinon (333-41-5): Summaries of concentrations in OH multimedia
                 samples collected from the homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - atdaycare
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
125
69
56
22
127
69
58
16
127
69
58
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
125
69
56
29



126
69
57
28



% Detected
97.6
97.1
98.2
100.0
74.8
81.2
67.2
68.8
33.9
43.5
22.4
18.8
95.8
96.8
94.7
100.0
95.8
96.8
94.7
100.0
38.1
26.7
66.7
0.0
30.8
44.4
0.0

53.8
55.6
50.0

35.1
30.9
44.8
37.9
42.3
40.6
46.4
15.2
8.7
23.2
24.1



1.6
2.9
0.0
3.6



Arithmetic Mean
11.8
8.00
16.5
11.6
1.20
2.02
0.226
0.262
-
-
-
-
1,360
2,120
519
260
939
593
1,320
994
-
-
16.4
-
-
-
-

93.4
132
7.52

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Std. Dev.
51.4
33.6
67.3
21.0
7.33
9.90
0.193
0.548
-
-
-
-
8,470
1 1 ,400
2,800
472
5,920
2,350
8,250
2,650
-
-
16.0
-
-
-
-

287
344
6.34

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Geometric
Mean
1.32
1.16
1.57
2.05
0.199
0.238
0.161
0.116
-
-
-
-
34.3
33.2
35.6
73.7
37.6
29.6
48.9
196
-
-
11.7
-
-
-
-

11.3
15.1
5.84

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Log Std. Dev.
1.62
1.49
1.77
1.89
1.21
1.43
0.829
1.08
-
-
-
-
1.97
2.07
1.86
1.57
2.02
1.96
2.08
1.78
-
-
0.868
-
-
-
-

1.71
1.96
0.803

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



* Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations.  This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries.  Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     J-34

-------
Table J-16b.   Diazinon (333-41-5):  Range of Reported Concentrations in OH multimedia
                 samples collected from the homes and  day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
125
69
56
22
127
69
58
16
127
69
58
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
125
69
56
29



126
69
57
28



Minimum

-------
Table J-17a.   Dibenzora.frlanthracene (53-70-3): Summaries of concentrations in OH
                 multimedia samples collected from the homes and day care centers of
                 preschool children who stay at home or attend day care during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
125
69
56
22
127
69
58
16
126
68
58
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

96
67
29
29
97
69
28
127
69
58
29



126
69
57
28



% Detected
0.8
0.0
1.8
0.0
0.0
0.0
0.0
0.0
73.8
72.1
75.9
81.3
99.2
98.4
100.0
100.0
99.2
98.4
100.0
100.0
66.7
53.3
100.0
33.3
7.7
11.1
0.0

15.4
11.1
25.0

27.1
22.4
37.9
34.5
5.2
7.2
0.0
1.6
1.4
1.7
0.0



0.0
0.0
0.0
0.0



Arithmetic Mean
-
-
-
-
-
-
-
-
34.0
24.7
45.0
10.9
410
352
474
530
472
423
526
3,570
11.9
8.89
19.4
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Std. Dev.
-
-
-
-
-
-
-
-
80.7
50.8
105
16.2
878
663
1,070
356
795
920
632
4,080
8.75
5.48
11.3
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Geometric
Mean
-
-
-
-
-
-
-
-
4.43
3.98
5.02
3.57
165
146
187
432
180
131
258
1,150
9.51
7.68
16.2
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Log Std. Dev.
-
-
-
-
-
-
-
-
2.14
2.03
2.27
1.69
1.24
1.27
1.21
0.678
1.46
1.51
1.33
1.93
0.663
0.533
0.696
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



* Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                    J-36

-------
Table J-17b.  Dibenzora.frlanthracene (53-70-3):  Range of Reported Concentrations in
                OH multimedia samples collected from the homes and day care centers of
                preschool children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
125
69
56
22
127
69
58
16
126
68
58
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

96
67
29
29
97
69
28
127
69
58
29



126
69
57
28



Minimum

-------
Table J-18a.   Di-n-butylphthalate (84-74-2): Summaries of concentrations in OH
                 multimedia samples collected from the homes and day care centers of
                 preschool children who stay at home or attend day care during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - atdaycare
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
125
69
56
22
126
69
57
16
124
67
57
16
119
63
56
23
119
63
56
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
91
47
44
15



96
51
45
25



% Detected
96.8
98.6
94.6
100.0
48.4
46.4
50.9
56.3
60.5
73.1
45.6
37.5
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
66.7
60.0
83.3
100.0
84.6
88.9
75.0

100.0
100.0
100.0

40.2
30.9
62.1
58.6
45.4
36.2
67.9
26.4
25.5
27.3
13.3



3.1
3.9
2.2
4.0



Arithmetic Mean
268
254
285
495
-
-
61.0
51.0
301
436
-
-
7,100
7,450
6,710
15,700
13,100
10,500
16,100
117,000
8,750
8,700
8,880
74,300
5,060
5,260
4,610

9,740
8,900
1 1 ,600

-
-
23,500
18,800
-
-
19,200
-
-
-
-



-
-
-
-



Std. Dev.
180
136
222
426
-
-
67.1
80.9
572
703
-
-
5,840
5,610
6,100
10,100
25,700
22,900
28,400
148,000
12,500
14,200
7,680
58,500
2,570
2,320
3,440

4,790
3,390
7,370

-
-
20,400
22,800
-
-
22,400
-
-
-
-



-
-
-
-



Geometric
Mean
208
208
208
386
-
-
38.1
27.5
72.8
118
-
-
5,470
5,700
5,220
13,700
5,910
5,080
7,000
36,400
4,600
4,200
5,750
44,400
4,280
4,590
3,660

8,910
8,350
10,300

-
-
16,600
13,100
-
-
10,700
-
-
-
-



-
-
-
-



Log Std. Dev.
0.806
0.730
0.898
0.661
-
-
0.925
1.02
1.62
1.70
-
-
0.725
0.761
0.686
0.519
1.19
1.11
1.27
1.89
1.15
1.19
1.13
1.53
0.664
0.622
0.826

0.421
0.376
0.539

-
-
0.860
0.791
-
-
1.11
-
-
-
-



-
-
-
-



* Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations.  This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries.  Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                    J-38

-------
Table J-18b.   Di-n-butylphthalate (84-74-2):  Range of Reported Concentrations in OH
                 multimedia samples collected from the homes and day care centers of
                 preschool children who stay at home or attend day care during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
125
69
56
22
126
69
57
16
124
67
57
16
119
63
56
23
119
63
56
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
91
47
44
15



96
51
45
25



Minimum

-------
Table J-19a.   Dicamba (1918-00-9): Summaries of concentrations in OH multimedia
                 samples collected from the homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
123
67
56
22
121
67
54
15
127
69
58
16
119
62
57
23
119
62
57
23
9
6
3
3
3
1
2

3
1
2

96
67
29
29
97
68
29
127
69
58
29
127
69
58
126
69
57
28
122
67
55
% Detected
0.8
1.5
0.0
0.0
3.3
4.5
1.9
0.0
3.9
4.3
3.4
6.3
47.1
51.6
42.1
52.2
47.1
51.6
42.1
52.2
0.0
0.0
0.0
0.0
0.0
0.0
0.0

0.0
0.0
0.0

4.2
4.5
3.4
3.4
1.0
1.5
0.0
11.8
14.5
8.6
13.8
15.0
13.0
17.2
0.0
0.0
0.0
0.0
0.8
0.0
1.8
Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
43.5
-
34.8
-
58.6
-
228
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
99.8
-
70.8
-
140
-
655
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
11.1
-
10.8
-
10.0
-
28.6
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
1.62
-
1.40
-
1.82
-
2.03
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
* Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                    J-40

-------
Table J-19b.  Dicamba (1918-00-9):  Range of Reported Concentrations in OH multimedia
                samples collected from the homes and day care centers  of preschool
                children who stay at home or attend day care during the  day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
123
67
56
22
121
67
54
15
127
69
58
16
119
62
57
23
119
62
57
23
9
6
3
3
3
1
2

3
1
2

96
67
29
29
97
68
29
127
69
58
29
127
69
58
126
69
57
28
122
67
55
Minimum

-------
Table J-20a.   p.p'-DDE (72-55-9): Summaries of concentrations in OH multimedia
                 samples collected from the homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
125
69
56
22
127
69
58
16
127
69
58
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
125
69
56
29



126
69
57
28



% Detected
35.2
36.2
33.9
36.4
3.1
4.3
1.7
0.0
45.7
44.9
46.6
12.5
48.3
49.2
47.4
43.5
48.3
49.2
47.4
43.5
14.3
13.3
16.7
0.0
0.0
0.0
0.0

0.0
0.0
0.0

5.2
7.4
0.0
0.0
5.2
5.8
3.6
76.8
75.4
78.6
55.2



7.9
11.6
3.5
0.0



Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
0.292
0.272
0.316
0.172



-
-
-
-



Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
0.456
0.463
0.450
0.134



-
-
-
-



Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
0.183
0.169
0.203
0.127



-
-
-
-



Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
0.876
0.860
0.892
0.797



-
-
-
-



a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations.  This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries.  Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                    J-42

-------
Table J-20b.  p.p'-DDE (72-55-9):  Range of Reported Concentrations in OH  multimedia
                samples collected from the homes and day care centers  of preschool
                children who stay at home or attend day care during the  day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
125
69
56
22
127
69
58
16
127
69
58
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
125
69
56
29



126
69
57
28



Minimum

-------
Table J-21a.   p.p'-DDT (50-29-3): Summaries of concentrations in OH  multimedia samples
                 collected from the homes and day care centers of preschool children who
                 stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
125
69
56
22
127
69
58
16
127
69
58
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
125
69
56
29



126
69
57
28



% Detected
24.0
29.0
17.9
9.1
2.4
2.9
1.7
0.0
32.3
29.0
36.2
6.3
41.7
46.0
36.8
26.1
41.7
46.0
36.8
26.1
19.0
13.3
33.3
0.0
7.7
0.0
25.0

0.0
0.0
0.0

1.0
1.5
0.0
0.0
7.2
8.7
3.6
4.0
4.3
3.6
10.3



2.4
2.9
1.8
0.0



Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations.  This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries.  Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                    J-44

-------
Table J-21b.  p.p'-DDT (50-29-3):  Range of Reported Concentrations in OH multimedia
                samples collected from the  homes and day care centers of preschool
                children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
125
69
56
22
127
69
58
16
127
69
58
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
125
69
56
29



126
69
57
28



Minimum

-------
Table J-22a.   2.4-D (2.4-dichlorophenoxyacetic acid) (94-75-7): Summaries of
                 concentrations in OH multimedia samples collected from the homes and
                 day care centers of preschool children who stay at home or attend day care
                 during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
123
67
56
22
116
65
51
14
127
69
58
16
119
62
57
23
119
62
57
23
9
6
3
3
3
1
2

3
1
2

96
67
29
29
97
68
29
127
69
58
29
127
69
58
126
69
57
28
122
67
55
% Detected
44.7
49.3
39.3
40.9
32.8
33.8
31.4
28.6
41.7
44.9
37.9
18.8
95.8
98.4
93.0
100.0
95.8
98.4
93.0
100.0
55.6
50.0
66.7
0.0
0.0
0.0
0.0

33.3
100.0
0.0

39.6
49.3
17.2
17.2
53.6
63.2
31.0
41.7
43.5
39.7
24.1
45.7
47.8
43.1
4.0
2.9
5.3
7.1
6.6
6.0
7.3
Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
579
731
414
391
769
942
580
2,310
58.1
55.4
63.6
-
-
-
-

-
8.86
-

-
-
-
-
100
102
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
2,080
2,760
835
612
2,220
2,790
1,340
5,820
86.0
102
58.7
-
-
-
-

-

-

-
-
-
-
166
108
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
137
170
108
171
151
154
149
454
26.5
21.3
40.7
-
-
-
-

-
8.86
-

-
-
-
-
57.3
66.8
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
1.65
1.58
1.69
1.27
1.72
1.81
1.64
1.87
1.25
1.28
1.31
-
-
-
-

-

-

-
-
-
-
0.948
0.909
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries.  Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                    J-46

-------
Table J-22b.  2.4-D (2.4-dichlorophenoxyacetic acid) (94-75-7):  Range of Reported
                Concentrations in OH multimedia samples collected from the homes and
                day care centers of preschool children who stay at home or attend day care
                during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
123
67
56
22
116
65
51
14
127
69
58
16
119
62
57
23
119
62
57
23
9
6
3
3
3
1
2

3
1
2

96
67
29
29
97
68
29
127
69
58
29
127
69
58
126
69
57
28
122
67
55
Minimum

-------
Table J-23a.  Dieldrin (60-57-1): Summaries of concentrations in OH multimedia samples
                 collected from the homes and day care centers of preschool children who
                 stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
125
69
56
22
127
69
58
16
127
69
58
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
125
69
56
29



126
69
57
28



% Detected
12.0
11.6
12.5
13.6
7.9
5.8
10.3
0.0
18.9
18.8
19.0
6.3
18.3
20.6
15.8
34.8
18.3
20.6
15.8
34.8
4.8
6.7
0.0
0.0
0.0
0.0
0.0

23.1
22.2
25.0

1.0
1.5
0.0
0.0
0.0
0.0
0.0
8.0
5.8
10.7
10.3



0.0
0.0
0.0
0.0



Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries.  Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics.  Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     J-48

-------
Table J-23b.   Dieldrin (60-57-1):  Range of Reported Concentrations in OH multimedia
                 samples collected from the homes and day care centers of preschool
                 children who stay  at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
125
69
56
22
127
69
58
16
127
69
58
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
125
69
56
29



126
69
57
28



Minimum

-------
Table J-24a.   Endrin (72-20-8): Summaries of concentrations in OH multimedia samples
                 collected from the homes and day care centers of preschool children who
                 stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
125
69
56
22
127
69
58
16
127
69
58
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
125
69
56
29



126
69
57
28



% Detected
11.2
10.1
12.5
18.2
18.9
15.9
22.4
18.8
3.1
2.9
3.4
0.0
2.5
1.6
3.5
30.4
2.5
1.6
3.5
30.4
0.0
0.0
0.0
0.0
0.0
0.0
0.0

7.7
11.1
0.0

4.1
4.4
3.4
0.0
2.1
2.9
0.0
0.8
0.0
1.8
3.4



0.0
0.0
0.0
0.0



Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations.  This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries.  Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     J-50

-------
Table J-24b.   Endrin (72-20-8):  Range of Reported Concentrations in OH multimedia
                 samples collected from the homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
125
69
56
22
127
69
58
16
127
69
58
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
125
69
56
29



126
69
57
28



Minimum

-------
Table J-25a.   Heptachlor (76-44-8): Summaries of concentrations in OH multimedia
                 samples collected from the homes  and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
125
69
56
22
127
69
58
16
127
69
58
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
125
69
56
29



126
69
57
28



% Detected
33.6
39.1
26.8
36.4
18.9
26.1
10.3
12.5
2.4
0.0
5.2
0.0
5.8
6.3
5.3
4.3
5.8
6.3
5.3
4.3
4.8
6.7
0.0
0.0
0.0
0.0
0.0

0.0
0.0
0.0

3.1
2.9
3.4
0.0
2.1
2.9
0.0
9.6
14.5
3.6
0.0



0.0
0.0
0.0
7.1



Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations.  This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries.  Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                    J-52

-------
Table J-25b.  Heptachlor (76-44-8):  Range of Reported Concentrations in OH multimedia
                samples collected from the homes and day care centers of preschool
                children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
125
69
56
22
127
69
58
16
127
69
58
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
125
69
56
29



126
69
57
28



Minimum

-------
Table J-26a.   IndenoM ,2.3-cc/lpvrene (193-39-5): Summaries of concentrations in OH
                 multimedia samples collected from the homes and day care centers of
                 preschool children who stay at home or attend day care during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
125
69
56
22
127
69
58
16
126
68
58
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

96
67
29
29
97
69
28
127
69
58
29



126
69
57
28



% Detected
19.2
10.1
30.4
22.7
15.0
11.6
19.0
31.3
89.7
91.2
87.9
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
95.2
93.3
100.0
100.0
30.8
22.2
50.0

69.2
66.7
75.0

75.0
70.1
86.2
65.5
60.8
60.9
60.7
3.9
1.4
6.9
0.0



0.0
0.0
0.0
3.6



Arithmetic Mean
-
-
-
-
-
-
-
-
151
112
195
46.1
2,040
1,730
2,370
2,580
2,240
2,070
2,430
17,100
54.4
39.6
91.4
40.7
-
-
8.18

20.9
23.5
15.1

233
255
183
237
39.4
40.6
36.5
-
-
-
-



-
-
-
-



Std. Dev.
-
-
-
-
-
-
-
-
357
238
457
67.2
4,660
3,450
5,730
1,930
3,930
4,650
2,980
19,700
48.3
34.3
61.2
44.4
-
-
5.15

27.6
33.0
9.60

568
667
206
501
44.7
48.2
35.1
-
-
-
-



-
-
-
-



Geometric
Mean
-
-
-
-
-
-
-
-
14.7
13.2
16.7
14.5
765
694
850
2,040
838
620
1,170
5,430
36.1
27.7
70.2
27.6
-
-
7.21

11.2
10.9
11.8

93.9
88.1
109
85.1
26.9
27.0
26.7
-
-
-
-



-
-
-
-



Log Std. Dev.
-
-
-
-
-
-
-
-
2.43
2.32
2.56
1.76
1.26
1.26
1.26
0.718
1.45
1.48
1.34
1.93
0.981
0.916
0.868
1.04
-
-
0.552

1.14
1.27
0.933

1.16
1.21
1.05
1.29
0.795
0.817
0.753
-
-
-
-



-
-
-
-



* Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                    J-54

-------
Table J-26b.  IndenoM,2.3-cc/lpvrene (193-39-5):  Range of Reported Concentrations in
                OH multimedia samples collected from the homes and day care centers of
                preschool children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
125
69
56
22
127
69
58
16
126
68
58
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

96
67
29
29
97
69
28
127
69
58
29



126
69
57
28



Minimum

-------
Table J-27a.   IMP (2-isopropvl-6-methvl-4-pyrimidinol) (2814-20-2): Summaries of
                 concentrations in OH multimedia samples collected from the homes and
                 day care centers of preschool children who stay at home or attend day care
                 during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
125
69
56
22
126
69
57
15
125
67
58
16
120
63
57
23
120
63
57
23
9
6
3
3
3
1
2

3
1
2

98
69
29
29
97
68
29
40
26
14
10
34
21
13
38
25
13
7
44
20
24
% Detected
96.0
97.1
94.6
90.9
84.9
88.4
80.7
93.3
40.8
44.8
36.2
37.5
87.5
85.7
89.5
87.0
87.5
85.7
89.5
87.0
44.4
33.3
66.7
0.0
0.0
0.0
0.0

0.0
0.0
0.0

29.6
30.4
27.6
24.1
21.6
16.2
34.5
87.5
96.2
71.4
70.0
88.2
81.0
100.0
26.3
28.0
23.1
57.1
34.1
40.0
29.2
Arithmetic Mean
1.41
1.00
1.91
2.16
1.24
1.90
0.455
3.49
-
-
-
-
84.0
70.9
98.4
73.0
106
64.5
152
181
-
-
47.2
-
-
-
-

-
-
-

-
-
-
-
-
-
-
0.524
0.615
0.353
0.249
0.703
0.808
0.533
-
-
-
0.084
-
-
-
Std. Dev.
3.55
1.50
5.02
4.03
4.93
6.59
0.551
11.4
-
-
-
-
313
277
350
155
341
213
439
367
-
-
37.0
-
-
-
-

-
-
-

-
-
-
-
-
-
-
0.538
0.600
0.354
0.215
0.890
1.10
0.348
-
-
-
0.072
-
-
-
Geometric
Mean
0.625
0.580
0.685
0.726
0.360
0.457
0.269
0.331
-
-
-
-
16.4
14.3
19.0
18.8
18.0
12.8
26.2
49.9
-
-
28.3
-
-
-
-

-
-
-

-
-
-
-
-
-
-
0.358
0.433
0.251
0.190
0.451
0.461
0.435
-
-
-
0.045
-
-
-
Log Std. Dev.
1.07
0.953
1.21
1.46
1.26
1.39
1.03
1.76
-
-
-
-
1.52
1.49
1.56
1.68
1.74
1.62
1.81
1.74
-
-
1.52
-
-
-
-

-
-
-

-
-
-
-
-
-
-
0.870
0.838
0.842
0.740
0.947
1.10
0.677
-
-
-
1.41
-
-
-
a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations.  This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do
not enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
Note that IMP data for solid and liquid food samples are to be interpreted with caution due to recoveries being below 50%.
                                                    J-56

-------
Table J-27b.   IMP (2-isopropvl-6-methvl-4-pyrimidinol) (2814-20-2):  Range of Reported
                 Concentrations in OH multimedia samples collected from the homes and
                 day care centers of preschool children who stay at home or attend day care
                 during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
N
125
69
56
22
126
69
57
15
125
67
58
16
120
63
57
23
120
63
57
23
9
6
3
3
3
1
2

3
1
2

98
69
29
29
97
68
29
40
26
14
10
34
21
13
38
25
13
7
44
20
24
Minimum

-------
Table J-28a.   Lindane (58-89-9): Summaries of concentrations in OH multimedia samples
                 collected  from the homes and day care centers of preschool children who
                 stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
N
125
69
56
22
127
69
58
16
127
69
58
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
125
69
56
29



126
69
57
28



% Detected
4.8
4.3
5.4
0.0
3.1
4.3
1.7
6.3
0.8
1.4
0.0
0.0
10.0
12.7
7.0
17.4
10.0
12.7
7.0
17.4
0.0
0.0
0.0
0.0
0.0
0.0
0.0

0.0
0.0
0.0

2.1
2.9
0.0
0.0
2.1
2.9
0.0
3.2
2.9
3.6
3.4



0.8
1.4
0.0
3.6



Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations.  This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries.  Reported measures of 0 ng/mL in liquid food do not
enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     J-58

-------
Table J-28b.   Lindane (58-89-9): Range of Reported Concentrations in OH multimedia
                 samples collected from the homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
125
69
56
22
127
69
58
16
127
69
58
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
125
69
56
29



126
69
57
28



Minimum

-------
Table J-29a.   Nonylphenol (104-40-5): Summaries of concentrations in OH multimedia
                 samples collected from the homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
125
69
56
22
127
69
58
16
73
40
33
9
18
10
8
10
18
10
8
10
21
15
6
3
13
9
4

12
8
4

98
69
29
29
97
69
28
127
69
58
29



126
69
57
28



% Detected
0.8
0.0
1.8
0.0
0.0
0.0
0.0
0.0
2.7
2.5
3.0
0.0
0.0
0.0
0.0
10.0
0.0
0.0
0.0
10.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0

8.3
12.5
0.0

0.0
0.0
0.0
0.0
3.1
2.9
3.6
0.8
1.4
0.0
3.4



0.0
0.0
0.0
0.0



Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do not
enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     J-60

-------
Table J-29b.  Nonylphenol (104-40-5):  Range of Reported Concentrations in OH
                multimedia samples collected from the homes and day care centers of
                preschool children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
125
69
56
22
127
69
58
16
73
40
33
9
18
10
8
10
18
10
8
10
21
15
6
3
13
9
4

12
8
4

98
69
29
29
97
69
28
127
69
58
29



126
69
57
28



Minimum

-------
Table J-30a.   Pentachloronitrobenzene (82-68-8): Summaries of concentrations in OH
                 multimedia samples collected from the homes and day care centers of
                 preschool  children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
125
69
56
22
127
69
58
16
127
69
58
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
125
69
56
29



126
69
57
28



% Detected
9.6
7.2
12.5
18.2
3.1
1.4
5.2
6.3
0.0
0.0
0.0
0.0
0.0
0.0
0.0
4.3
0.0
0.0
0.0
4.3
0.0
0.0
0.0
0.0
0.0
0.0
0.0

0.0
0.0
0.0

2.1
2.9
0.0
0.0
1.0
1.4
0.0
0.8
0.0
1.8
6.9



0.0
0.0
0.0
0.0



Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-



-
-
-
-



a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries.  Reported measures of 0 ng/mL in liquid food do not
enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                    J-62

-------
Table J-30b.  Pentachloronitrobenzene (82-68-8):  Range of Reported Concentrations in
                OH multimedia samples collected from the homes and day care centers of
                preschool children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
125
69
56
22
127
69
58
16
127
69
58
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
125
69
56
29



126
69
57
28



Minimum

-------
Table J-31a.   Pentachlorophenol (87-86-5): Summaries of concentrations in OH
                 multimedia samples collected from the homes and day care centers of
                 preschool  children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
123
67
56
22
106
56
50
13
127
69
58
16
119
62
57
23
119
62
57
23
9
6
3
3
3
1
2

3
1
2

96
67
29
29
97
68
29
127
69
58
29
127
69
58
126
69
57
28
122
67
55
% Detected
91.9
95.5
87.5
68.2
60.4
71.4
48.0
53.8
51.2
50.7
51.7
37.5
94.1
95.2
93.0
91.3
94.1
95.2
93.0
91.3
44.4
33.3
66.7
0.0
0.0
0.0
0.0

33.3
0.0
50.0

50.0
49.3
51.7
20.7
51.5
44.1
69.0
21.3
20.3
22.4
13.8
25.2
21.7
29.3
3.2
4.3
1.8
3.6
5.7
4.5
7.3
Arithmetic Mean
4.92
6.14
3.46
2.80
1.04
1.19
-
0.934
3.39
2.58
4.36
-
112
133
90.2
81.9
242
196
293
597
-
-
47.0
-
-
-
-

-
-
70.3

142
-
110
-
79.3
-
85.2
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Std. Dev.
8.94
11.2
4.77
4.04
1.77
1.71
-
1.48
7.63
4.75
9.99
-
219
292
85.4
145
690
645
739
1,250
-
-
56.0
-
-
-
-

-
-
95.1

205
-
88.8
-
93.7
-
66.1
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Geometric
Mean
2.06
2.79
1.43
0.898
0.413
0.552
-
0.299
1.03
0.969
1.10
-
59.9
65.8
54.1
41.5
66.2
59.4
74.5
110
-
-
27.8
-
-
-
-

-
-
20.7

96.5
-
86.3
-
51.8
-
62.1
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Log Std. Dev.
1.39
1.23
1.50
1.82
1.37
1.34
-
1.64
1.45
1.36
1.56
-
1.10
1.06
1.13
1.09
1.65
1.56
1.75
2.14
-
-
1.25
-
-
-
-

-
-
2.68

0.757
-
0.667
-
0.860
-
0.836
-
-
-
-
-
-
-
-
-
-
-
-
-
-
a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do not
enter into the descriptive statistics.  Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     J-64

-------
Table J-31b.  Pentachlorophenol (87-86-5):  Range of Reported Concentrations in OH
                multimedia samples collected from the homes and day care centers of
                preschool children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
123
67
56
22
106
56
50
13
127
69
58
16
119
62
57
23
119
62
57
23
9
6
3
3
3
1
2

3
1
2

96
67
29
29
97
68
29
127
69
58
29
127
69
58
126
69
57
28
122
67
55
Minimum

-------
Table J-32a.   c/s-Permethrin (61949-76-6): Summaries of concentrations in OH  multimedia
                 samples collected from the  homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
125
69
56
22
127
69
58
16
127
69
58
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
125
69
56
29



125
68
57
28



% Detected
21.6
15.9
28.6
27.3
23.6
23.2
24.1
6.3
6.3
10.1
1.7
0.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
71.4
60.0
100.0
66.7
38.5
33.3
50.0

69.2
55.6
100.0

87.6
86.8
89.7
79.3
77.3
73.9
85.7
31.2
23.2
41.1
24.1



0.0
0.0
0.0
0.0



Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
2,320
1,360
3,380
1,460
8,250
3,740
13,200
7,750
2,800
350
8,930
41.4
-
-
1,960

349
156
782

1,390
987
2,330
1,470
582
433
951
-
-
-
-



-
-
-
-



Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
8,050
3,170
11,200
1,300
43,200
14,000
60,800
13,600
1 1 ,300
528
21,100
31.6
-
-
3,890

813
380
1,380

3,000
1,990
4,480
2,890
1,650
1,130
2,510
-
-
-
-



-
-
-
-



Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
572
515
643
968
627
459
886
2,570
107
63.2
401
25.9
-
-
53.4

40.7
19.4
216

388
331
564
344
133
112
204
-
-
-
-



-
-
-
-



Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
1.47
1.25
1.68
0.967
2.01
1.85
2.14
1.60
2.52
2.30
2.79
1.45
-
-
3.48

2.23
2.08
1.73

1.59
1.48
1.78
1.87
1.68
1.64
1.71
-
-
-
-



-
-
-
-



a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do not
enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     J-66

-------
Table J-32b.  c/s-Permethrin (61949-76-6):  Range of Reported Concentrations in OH
                multimedia samples collected from the homes and day care centers of
                preschool children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
125
69
56
22
127
69
58
16
127
69
58
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
125
69
56
29



125
68
57
28



Minimum

-------
Table J-33a.   frans-Permethrin (61949-77-7): Summaries of concentrations in OH
                 multimedia samples collected from the homes and day care  centers of
                 preschool  children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
N
125
69
56
22
127
69
58
16
124
67
57
14
118
62
56
22
118
62
56
22
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
125
69
56
29



125
68
57
28



% Detected
18.4
13.0
25.0
22.7
20.5
17.4
24.1
0.0
6.5
10.4
1.8
0.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
71.4
60.0
100.0
66.7
38.5
33.3
50.0

69.2
55.6
100.0

87.6
86.8
89.7
79.3
77.3
73.9
85.7
31.2
23.2
41.1
24.1



0.0
0.0
0.0
0.0



Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
2,340
1,420
3,360
1,260
7,640
3,260
12,500
7,260
2,810
376
8,890
38.8
-
-
1,990

292
76.5
775

1,350
877
2,440
1,490
586
356
1,150
-
-
-
-



-
-
-
-



Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
8,320
4,220
11,200
1,220
42,600
1 1 ,000
60,600
14,000
11,200
565
21,000
31.2
-
-
3,950

790
170
1,400

3,360
1,970
5,270
3,250
1,970
944
3,340
-
-
-
-



-
-
-
-



Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
453
409
508
784
475
350
665
2,020
106
63.6
385
24.4
-
-
54.6

33.1
15.4
185

321
260
526
302
113
93.3
183
-
-
-
-



-
-
-
-



Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
1.60
1.38
1.82
1.02
2.08
1.94
2.18
1.75
2.56
2.34
2.83
1.41
-
-
3.49

2.11
1.81
1.83

1.60
1.46
1.80
1.86
1.65
1.57
1.77
-
-
-
-



-
-
-
-



a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Reported measures of 0 ng/mL in liquid food do not
enter into the descriptive statistics.  Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     J-68

-------
Table J-33b.  frans-Permethrin (61949-77-7):  Range of Reported Concentrations in OH
                multimedia samples collected from the homes and day care centers of
                preschool children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
125
69
56
22
127
69
58
16
124
67
57
14
118
62
56
22
118
62
56
22
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
125
69
56
29



125
68
57
28



Minimum

-------
Table J-34a.   PCB 44 (41464-39-5): Summaries of concentrations in OH multimedia
                 samples collected from the homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
125
69
56
22
126
69
57
16
126
69
57
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
126
69
57
29










% Detected
31.2
27.5
35.7
31.8
15.9
18.8
12.3
12.5
14.3
11.6
17.5
18.8
27.5
30.2
24.6
8.7
27.5
30.2
24.6
8.7
9.5
0.0
33.3
0.0
7.7
11.1
0.0

15.4
22.2
0.0

10.3
11.8
6.9
3.4
6.2
8.7
0.0
0.0
0.0
0.0
0.0










Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-










Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-










Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-










Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-










a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Means and standard deviations are not reported
when the percentage of detected results is below 50%.
                                                    J-70

-------
Table J-34b.  PCB 44 (41464-39-5):  Range of Reported Concentrations in OH multimedia
                samples  collected from the homes and day care centers of preschool
                children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
N
125
69
56
22
126
69
57
16
126
69
57
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
126
69
57
29










Minimum

-------
Table J-35a.   PCB 52 (35693-99-3): Summaries of concentrations in OH multimedia
                 samples collected from the homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
125
69
56
22
125
69
56
15
126
69
57
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

12
8
4

96
67
29
29
97
69
28
126
69
57
29










% Detected
86.4
82.6
91.1
95.5
63.2
63.8
62.5
86.7
20.6
15.9
26.3
18.8
46.7
49.2
43.9
69.6
46.7
49.2
43.9
69.6
38.1
33.3
50.0
33.3
7.7
11.1
0.0

50.0
37.5
75.0

17.7
22.4
6.9
10.3
22.7
26.1
14.3
5.6
4.3
7.0
6.9










Arithmetic Mean
0.662
0.643
0.686
0.575
0.145
0.146
0.145
0.192
-
-
-
-
-
-
-
10.5
-
-
-
61.0
-
-
8.08
-
-
-
-

22.1
-
19.7

-
-
-
-
-
-
-
-
-
-
-










Std. Dev.
0.922
0.831
1.03
0.411
0.131
0.126
0.137
0.265
-
-
-
-
-
-
-
10.7
-
-
-
82.1
-
-
3.90
-
-
-
-

23.5
-
19.9

-
-
-
-
-
-
-
-
-
-
-










Geometric
Mean
0.342
0.317
0.375
0.460
0.093
0.095
0.091
0.112
-
-
-
-
-
-
-
7.18
-
-
-
19.1
-
-
7.34
-
-
-
-

13.0
-
14.2

-
-
-
-
-
-
-
-
-
-
-










Log Std. Dev.
1.26
1.35
1.16
0.787
1.00
0.996
1.01
1.02
-
-
-
-
-
-
-
0.919
-
-
-
1.82
-
-
0.477
-
-
-
-

1.06
-
0.886

-
-
-
-
-
-
-
-
-
-
-










a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Means and standard deviations are not reported
when the percentage of detected results is below 50%.
                                                    J-72

-------
Table J-35b.  PCB 52 (35693-99-3):  Range of Reported Concentrations in OH multimedia
                samples  collected from the homes and day care centers of preschool
                children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
125
69
56
22
125
69
56
15
126
69
57
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

12
8
4

96
67
29
29
97
69
28
126
69
57
29










Minimum

-------
Table J-36a.  PCB 70(32698-11-1): Summaries of concentrations in OH multimedia
                samples collected from the homes and day care centers of preschool
                children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
125
69
56
22
126
69
57
16
126
69
57
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

95
66
29
29
97
69
28
126
69
57
29










% Detected
34.4
39.1
28.6
45.5
14.3
15.9
12.3
12.5
18.3
13.0
24.6
25.0
25.8
30.2
21.1
21.7
25.8
30.2
21.1
21.7
52.4
53.3
50.0
33.3
15.4
11.1
25.0

23.1
22.2
25.0

17.9
21.2
10.3
13.8
11.3
13.0
7.1
0.0
0.0
0.0
0.0










Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
7.26
6.47
9.26
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-










Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
3.65
1.72
6.18
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-










Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
6.69
6.26
7.89
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-










Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
0.385
0.261
0.597
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-










a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations.  This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries.  Means and standard deviations are not reported
when the percentage of detected results is below 50%.
                                                    J-74

-------
Table J-36b.  PCB 70(32698-11-1):  Range of Reported Concentrations in OH multimedia
                samples collected from the homes and day care centers of preschool
                children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
125
69
56
22
126
69
57
16
126
69
57
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

95
66
29
29
97
69
28
126
69
57
29










Minimum

-------
Table J-37a.  PCB 77(32598-13-3): Summaries of concentrations in OH multimedia
                samples collected from the homes and day care centers of preschool
                children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
125
69
56
22
127
69
58
16
126
69
57
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

97
69
28
97
68
29
29
126
69
57
29










% Detected
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.8
0.0
1.8
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0

0.0
0.0
0.0

0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0










Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-










Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-










Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-










Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-










a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations.  This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries.  Means and standard deviations are not reported
when the percentage of detected results is below 50%.
                                                    J-76

-------
Table J-37b.  PCB 77(32598-13-3):  Range of Reported Concentrations in OH multimedia
                samples collected from the homes and day care centers of preschool
                children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
125
69
56
22
127
69
58
16
126
69
57
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

97
69
28
97
68
29
29
126
69
57
29










Minimum

-------
Table J-38a.   PCB 95 (38379-99-6): Summaries of concentrations in OH multimedia
                 samples collected from the homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
N
125
69
56
22
127
69
58
16
126
69
57
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
126
69
57
29










% Detected
60.0
59.4
60.7
77.3
35.4
34.8
36.2
43.8
23.0
17.4
29.8
25.0
37.5
39.7
35.1
65.2
37.5
39.7
35.1
65.2
4.8
6.7
0.0
0.0
0.0
0.0
0.0

30.8
33.3
25.0

7.2
8.8
3.4
0.0
10.3
8.7
14.3
0.8
1.4
0.0
0.0










Arithmetic Mean
0.222
0.198
0.251
0.157
-
-
-
-
-
-
-
-
-
-
-
6.29
-
-
-
34.2
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-










Std. Dev.
0.469
0.347
0.588
0.186
-
-
-
-
-
-
-
-
-
-
-
4.49
-
-
-
40.4
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-










Geometric
Mean
0.094
0.093
0.096
0.097
-
-
-
-
-
-
-
-
-
-
-
4.87
-
-
-
12.9
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-










Log Std. Dev.
1.17
1.14
1.23
0.970
-
-
-
-
-
-
-
-
-
-
-
0.769
-
-
-
1.65
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-










a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Means and standard deviations are not reported
when the percentage of detected results is below 50%.
                                                    J-78

-------
Table J-38b.  PCB 95 (38379-99-6):  Range of Reported Concentrations in OH multimedia
                samples  collected from the homes and day care centers of preschool
                children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
125
69
56
22
127
69
58
16
126
69
57
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
126
69
57
29










Minimum

-------
Table J-39a.   PCB 101 (37680-73-2): Summaries of concentrations in OH multimedia
                 samples collected from the homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
N
125
69
56
22
127
69
58
16
126
69
57
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
126
69
57
29










% Detected
52.8
47.8
58.9
68.2
23.6
15.9
32.8
37.5
25.4
20.3
31.6
25.0
41.7
44.4
38.6
60.9
41.7
44.4
38.6
60.9
9.5
0.0
33.3
0.0
0.0
0.0
0.0

46.2
44.4
50.0

11.3
11.8
10.3
3.4
12.4
13.0
10.7
0.8
1.4
0.0
0.0










Arithmetic Mean
0.226
-
0.280
0.165
-
-
-
-
-
-
-
-
-
-
-
7.63
-
-
-
41.8
-
-
-
-
-
-
-

-
-
9.78

-
-
-
-
-
-
-
-
-
-
-










Std. Dev.
0.594
-
0.805
0.225
-
-
-
-
-
-
-
-
-
-
-
6.63
-
-
-
53.4
-
-
-
-
-
-
-

-
-
8.31

-
-
-
-
-
-
-
-
-
-
-










Geometric
Mean
0.085
-
0.097
0.089
-
-
-
-
-
-
-
-
-
-
-
5.31
-
-
-
14.1
-
-
-
-
-
-
-

-
-
7.88

-
-
-
-
-
-
-
-
-
-
-










Log Std. Dev.
1.22
-
1.26
1.10
-
-
-
-
-
-
-
-
-
-
-
0.910
-
-
-
1.72
-
-
-
-
-
-
-

-
-
0.706

-
-
-
-
-
-
-
-
-
-
-










a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Means and standard deviations are not reported
when the percentage of detected results is below 50%.
                                                    J-80

-------
Table J-39b.  PCB 101  (37680-73-2):  Range of Reported Concentrations in OH multimedia
                samples  collected from the homes and day care centers of preschool
                children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
125
69
56
22
127
69
58
16
126
69
57
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
126
69
57
29










Minimum

-------
Table J-40a.   PCB 105 (32598-14-4): Summaries of concentrations in OH  multimedia
                 samples collected from the homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
N
125
69
56
22
127
69
58
16
126
69
57
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
126
69
57
29










% Detected
4.8
4.3
5.4
9.1
2.4
1.4
3.4
6.3
20.6
15.9
26.3
12.5
13.3
15.9
10.5
17.4
13.3
15.9
10.5
17.4
14.3
13.3
16.7
0.0
0.0
0.0
0.0

7.7
11.1
0.0

5.2
7.4
0.0
0.0
1.0
1.4
0.0
0.0
0.0
0.0
0.0










Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-










Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-










Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-










Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-










a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Means and standard deviations are not reported
when the percentage of detected results is below 50%.
                                                    J-82

-------
Table J-40b.  PCB 105 (32598-14-4):  Range of Reported Concentrations in OH multimedia
                samples collected from the homes and day care centers of preschool
                children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
125
69
56
22
127
69
58
16
126
69
57
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
126
69
57
29










Minimum

-------
Table J-41a.   PCB 110 (38380-03-9): Summaries of concentrations in OH  multimedia
                 samples collected from the homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
N
125
69
56
22
126
69
57
16
126
69
57
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

96
67
29
29
97
69
28
126
69
57
29










% Detected
46.4
44.9
48.2
27.3
19.8
21.7
17.5
31.3
31.7
26.1
38.6
25.0
45.0
46.0
43.9
60.9
45.0
46.0
43.9
60.9
42.9
40.0
50.0
33.3
0.0
0.0
0.0

46.2
44.4
50.0

11.5
13.4
6.9
6.9
13.4
14.5
10.7
0.8
1.4
0.0
0.0










Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
8.93
-
-
-
51.8
-
-
8.83
-
-
-
-

-
-
10.0

-
-
-
-
-
-
-
-
-
-
-










Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
9.41
-
-
-
76.4
-
-
7.30
-
-
-
-

-
-
7.87

-
-
-
-
-
-
-
-
-
-
-










Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
5.92
-
-
-
15.7
-
-
7.25
-
-
-
-

-
-
8.40

-
-
-
-
-
-
-
-
-
-
-










Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
0.946
-
-
-
1.77
-
-
0.620
-
-
-
-

-
-
0.638

-
-
-
-
-
-
-
-
-
-
-










a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Means and standard deviations are not reported
when the percentage of detected results is below 50%.
                                                    J-84

-------
Table J-41b.  PCB 110 (38380-03-9):  Range of Reported Concentrations in OH multimedia
                samples collected from the homes and day care centers of preschool
                children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
125
69
56
22
126
69
57
16
126
69
57
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

96
67
29
29
97
69
28
126
69
57
29










Minimum

-------
Table J-42a.   PCB 118 (31508-00-6): Summaries of concentrations in OH  multimedia
                 samples collected from the homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
N
125
69
56
22
126
69
57
16
126
69
57
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
126
69
57
29










% Detected
24.0
21.7
26.8
18.2
6.3
5.8
7.0
25.0
30.2
26.1
35.1
25.0
40.0
41.3
38.6
47.8
40.0
41.3
38.6
47.8
19.0
20.0
16.7
0.0
0.0
0.0
0.0

23.1
22.2
25.0

10.3
11.8
6.9
6.9
7.2
5.8
10.7
1.6
2.9
0.0
0.0










Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-










Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-










Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-










Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-










a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Means and standard deviations are not reported
when the percentage of detected results is below 50%.
                                                    J-86

-------
Table J-42b.  PCB 118 (31508-00-6):  Range of Reported Concentrations in OH multimedia
                samples collected from the homes and day care centers of preschool
                children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
125
69
56
22
126
69
57
16
126
69
57
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
126
69
57
29










Minimum

-------
Table J-43a.   PCB 138 (35065-28-2): Summaries of concentrations in OH multimedia
                 samples collected from the homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
N
125
69
56
22
127
69
58
16
126
69
57
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
126
69
57
29










% Detected
8.8
5.8
12.5
13.6
1.6
2.9
0.0
12.5
31.7
29.0
35.1
25.0
28.3
30.2
26.3
26.1
28.3
30.2
26.3
26.1
0.0
0.0
0.0
0.0
0.0
0.0
0.0

7.7
11.1
0.0

2.1
2.9
0.0
0.0
1.0
0.0
3.6
0.8
1.4
0.0
0.0










Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-










Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-










Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-










Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-










a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Means and standard deviations are not reported
when the percentage of detected results is below 50%.
                                                    J-8

-------
Table J-43b.  PCB 138 (35065-28-2):  Range of Reported Concentrations in OH multimedia
                samples collected from the homes and day care centers of preschool
                children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
125
69
56
22
127
69
58
16
126
69
57
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
126
69
57
29










Minimum

-------
Table J-44a.   PCB 153 (35065-27-1): Summaries of concentrations in OH  multimedia
                 samples collected from the homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
N
125
69
56
22
127
69
58
16
126
69
57
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
126
69
57
29










% Detected
16.8
15.9
17.9
18.2
0.0
0.0
0.0
12.5
34.1
29.0
40.4
31.3
40.0
41.3
38.6
47.8
40.0
41.3
38.6
47.8
4.8
0.0
16.7
0.0
0.0
0.0
0.0

23.1
22.2
25.0

4.1
4.4
3.4
0.0
2.1
1.4
3.6
1.6
1.4
1.8
0.0










Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-










Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-










Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-










Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-










a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Means and standard deviations are not reported
when the percentage of detected results is below 50%.
                                                    J-90

-------
Table J-44b.  PCB 153 (35065-27-1):  Range of Reported Concentrations in OH multimedia
                samples collected from the homes and day care centers of preschool
                children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
125
69
56
22
127
69
58
16
126
69
57
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
126
69
57
29










Minimum

-------
Table J-45a.   PCB 180 (35065-29-3): Summaries of concentrations in OH  multimedia
                 samples collected from the homes and day care centers of preschool
                 children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
125
69
56
22
127
69
58
16
126
69
57
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
126
69
57
29










% Detected
2.4
0.0
5.4
4.5
0.0
0.0
0.0
0.0
22.2
17.4
28.1
18.8
16.7
20.6
12.3
13.0
16.7
20.6
12.3
13.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0

0.0
0.0
0.0

0.0
0.0
0.0
0.0
1.0
0.0
3.6
0.0
0.0
0.0
0.0










Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-










Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-










Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-










Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-










a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries. Means and standard deviations are not reported
when the percentage of detected results is below 50%.
                                                    J-92

-------
Table J-45b.  PCB 180 (35065-29-3):  Range of Reported Concentrations in OH multimedia
                samples collected from the homes and day care centers of preschool
                children who stay at home or attend day care during the day.a
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
125
69
56
22
127
69
58
16
126
69
57
16
120
63
57
23
120
63
57
23
21
15
6
3
13
9
4

13
9
4

97
68
29
29
97
69
28
126
69
57
29










Minimum

-------
Table J-46a.   2.4.5-T (2.4.5-trichlorophenoxyacetic acid) (93-76-5): Summaries of
                 concentrations in OH multimedia samples collected from the homes and day
                 care centers of preschool children who stay at home or attend day care
                 during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
N
123
67
56
22
121
67
54
15
127
69
58
16
119
62
57
23
119
62
57
23
9
6
3
3
3
1
2

3
1
2

96
67
29
29
97
68
29
127
69
58
29
127
69
58
126
69
57
28
122
67
55
% Detected
0.0
0.0
0.0
0.0
0.8
0.0
1.9
0.0
3.9
2.9
5.2
0.0
3.4
3.2
3.5
0.0
3.4
3.2
3.5
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0

0.0
0.0
0.0

1.0
1.5
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.8
0.0
1.8
Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-

-
-
-

-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries.  Reported measures of 0 ng/mL in liquid food do not
enter into the descriptive statistics. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                    J-94

-------
Table J-46b.  2.4.5-T (2.4.5-trichlorophenoxyacetic acid) (93-76-5):  Range of Reported
                Concentrations in OH multimedia samples collected from the homes and
                day care centers of preschool children who stay at home or attend day care
                during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
123
67
56
22
121
67
54
15
127
69
58
16
119
62
57
23
119
62
57
23
9
6
3
3
3
1
2

3
1
2

96
67
29
29
97
68
29
127
69
58
29
127
69
58
126
69
57
28
122
67
55
Minimum

-------
Table J-47a.   3.5.6-TCP (3.5.6-trichloro-2-pyridinol) (6515-38-4): Summaries of
                 concentrations in OH multimedia samples collected from the homes and day
                 care centers of preschool children who stay at home or attend day care
                 during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust (ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal Wipe
(Children)
(ng/m2)
Dermal Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
Day care children - at day care
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
All children - at home
Home children - at home
Day care children - at home
Day care children - at day care
All children -at home
Home children - at home
Day care children - at home
N
123
69
54
21
118
64
54
15
127
69
58
16
120
63
57
23
120
63
57
23
9
6
3
3
3
1
2

3
1
2

98
69
29
29
94
65
29
127
69
58
29
127
69
58
126
69
57
28
122
67
55
% Detected
100.0
100.0
100.0
100.0
88.1
93.8
81.5
86.7
80.3
78.3
82.8
81.3
99.2
98.4
100.0
100.0
99.2
98.4
100.0
100.0
88.9
83.3
100.0
100.0
66.7
100.0
50.0

33.3
0.0
50.0

96.9
95.7
100.0
89.7
92.6
93.8
89.7
99.2
100.0
98.3
100.0
99.2
100.0
98.3
33.3
34.8
31.6
53.6
35.2
41.8
27.3
Arithmetic Mean
2.05
2.30
1.73
1.50
0.338
0.373
0.295
0.204
3.99
5.02
2.76
1.15
153
127
180
93.8
436
176
723
493
49.5
61.5
25.6
10.6
7.15
8.97
6.23

-
-
13.9

154
167
124
116
53.7
55.8
48.9
2.55
2.90
2.15
2.81
3.74
4.62
2.69
-
-
-
0.188
-
-
-
Std. Dev.
4.97
6.02
3.20
1.25
0.504
0.618
0.322
0.137
15.3
19.2
8.66
1.57
348
271
418
105
2,360
395
3,390
867
105
130
22.7
4.23
2.08

1.92

-
-
15.2

120
134
70.9
73.7
40.1
44.4
28.3
2.60
3.04
1.89
4.97
5.98
6.46
5.22
-
-
-
0.309
-
-
-
Geometric
Mean
0.815
0.791
0.847
1.01
0.226
0.248
0.202
0.161
0.821
0.799
0.847
0.601
51.0
46.5
56.6
62.3
55.9
41.5
77.9
165
16.2
15.0
18.9
10.0
6.93
8.97
6.09

-
-
8.74

121
128
107
95.8
42.5
43.1
40.9
1.70
2.01
1.39
1.66
2.05
2.76
1.44
-
-
-
0.072
-
-
-
Log Std. Dev.
1.14
1.21
1.05
0.976
0.814
0.783
0.844
0.763
1.47
1.58
1.35
1.15
1.31
1.29
1.33
0.890
1.77
1.68
1.83
1.64
1.32
1.54
0.994
0.377
0.315

0.312

-
-
1.46

0.686
0.730
0.558
0.662
0.687
0.709
0.644
0.990
0.898
1.06
0.871
1.08
0.975
1.09
-
-
-
1.52
-
-
-
a Not detected results are replaced by the method detection limit (MDL) divided by 10 for liquid food samples and by the square root of 2 for all
other samples. Multiple or replicate sample results at a given location have been log-transformed, averaged, and exponentiated back to regular
units prior to summarizing the data across locations. This result is labeled as "detected" if any measurement entering into the calculation was
detected.  Thus, N specifies the number of locations having data entering into the summaries.  Reported measures of 0 ng/mL in liquid food do not
enter into the descriptive statistics.  Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     J-96

-------
Table J-47b.  3.5.6-TCP (3.5.6-trichloro-2-pyridinol) (6515-38-4):  Range of Reported
                Concentrations in OH multimedia samples collected from the homes and
                day care centers of preschool children who stay at home or attend day care
                during the day.3
Medium
Indoor Air
(ng/m3)
Outdoor Air
(ng/m3)
Soil
(ng/g)
Indoor Floor
Dust
(ng/g)
Indoor Floor
Dust
(ng/m2)
Hard Floor
Surface
Wipes
(ng/m2)
Food
Preparation
Surface
Wipes
(ng/m2)
Transferable
Residues
(ng/m2)
Dermal
Wipe
(Children)
(ng/m2)
Dermal
Wipe
(Adults)
(ng/m2)
Solid Food
(Children)
(ng/g)
Solid Food
(Adults)
(ng/g)
Liquid Food
(Children)
(ng/mL)
Liquid Food
(Adults)
(ng/mL)
Group
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children - at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children -at home
Home Children - at home
Day care Children - at home
All Children -at home
Home Children - at home
Day care Children - at home
Day care Children - at day care
All Children - at home
Home Children - at home
Day care Children - at home
N
123
69
54
21
118
64
54
15
127
69
58
16
120
63
57
23
120
63
57
23
9
6
3
3
3
1
2

3
1
2

98
69
29
29
94
65
29
127
69
58
29
127
69
58
126
69
57
28
122
67
55
Minimum
0.090
0.090
0.110
0.150

-------

-------
                                   Appendix K
Detailed Results of Statistical Analyses to Test for Significant Differences in Multimedia
      Pollutant Measurements Between Selected Strata, by State and Media Type
                                       K-l

-------
K-2

-------
Table K-l. Estimated Ratio Between Selected Strata of Geometric Mean Pollutant Levels
          in NC Multimedia Samples, and 95% Confidence Intervals on This Ratio, for
          Pollutants Detected in At Least 50% of Samples
Medium
Estimated Ratio of Geometric Means (95% CI)
Urban vs.
Rural
Low Income
vs. Mid/High
Income
Home vs.
Day Care
Environ-
ments
Home
Environment
(for Home
Children) vs.
Day Care
Environment
Home
Environment
(for Home
Children) vs.
Home
Environment
(for Day Care
Children)
Home
Environment
(for Day Care
Children) vs.
Day Care
Environment
Benz [a] anthracene
Outdoor Air
Soil
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface
Wipes
Transferable Residues
1.58*
(1.04,2.40)
1.30
(0.52,3.26)
0.92
(0.54,1.59)
0.78
(0.39,1.55)
2.20
(0.36,13.28)
0.20
(0.03,1.28)
0.95
(0.69,1.31)
2.55**
(1.27,5.13)
0.54**
(0.36,0.83)
1.57
(0.92,2.68)
1.19
(0.27,5.20)
0.54
(0.11,2.56)
1.49
(0.88,2.50)
0.48
(0.15,1.51)
0.52
(0.27,1.01)
0.12**
(0.05,0.27)


1.67
(0.87,3.21)
0.47
(0.11,1.99)
0.49
(0.21,1.12)
0.12**
(0.04,0.33)


1.27
(0.85,1.89)
0.97
(0.40,2.32)
0.89
(0.53,1.50)
0.97
(0.50,1.90)
0.22*
(0.05,0.94)
1.90
(0.42,8.69)
1.32
(0.69,2.54)
0.49
(0.12,2.07)
0.55
(0.24,1.28)
0.12**
(0.04,0.35)


Benzo [6]fluoranthene
Indoor Air
Outdoor Air
Soil
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface
Wipes
Transferable Residues
1.44
(0.92,2.24)
1.48
(0.89,2.47)
1.27
(0.47,3.39)
0.91
(0.53,1.58)
0.77
(0.38,1.56)
1.73
(0.30,10.08)
0.72
(0.06,8.28)
1.95**
(1.39,2.74)
1.15
(0.78,1.70)
2.54*
(1.20,5.37)
0.57**
(0.37,0.86)
1.63
(0.94,2.81)
1.70
(0.40,7.21)
0.62
(0.08,4.83)
1.08
(0.61,1.90)
1.41
(0.75,2.65)
0.50
(0.15,1.72)
0.55
(0.28,1.07)
0.12**
(0.05,0.29)


1.13
(0.56,2.31)
1.62
(0.73,3.57)
0.51
(0.11,2.39)
0.48
(0.21,1.12)
0.12**
(0.04,0.34)


1.11
(0.73,1.69)
1.32
(0.81,2.13)
1.04
(0.41,2.64)
0.78
(0.46,1.33)
0.86
(0.43,1.70)
0.14**
(0.03,0.60)
0.65
(0.09,4.88)
1.02
(0.50,2.09)
1.23
(0.56,2.73)
0.50
(0.11,2.32)
0.62
(0.26,1.44)
0.13**
(0.05,0.40)


Benzo [&]fluoranthene
Outdoor Air
Soil
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface
Wipes
1.28
(0.93,1.76)
1.30
(0.55,3.08)
0.87
(0.50,1.49)
0.73
(0.36,1.48)
2.14
(0.42,10.88)
1.15
(0.90,1.46)
2.21*
(1.15,4.26)
0.56**
(0.37,0.86)
1.62
(0.93,2.80)
1.80
(0.47,6.82)
1.42
(0.96,2.12)
0.49
(0.17,1.42)
0.57
(0.29,1.10)
0.13**
(0.05,0.30)

1.63
(0.99,2.69)
0.50
(0.13,1.90)
0.52
(0.23,1.20)
0.12**
(0.04,0.36)

1.32
(0.97,1.79)
1.04
(0.46,2.35)
0.84
(0.50,1.43)
0.92
(0.46,1.83)
0.31
(0.08,1.15)
1.24
(0.75,2.05)
0.48
(0.12,1.85)
0.62
(0.27,1.44)
0.13**
(0.04,0.40)

                                        K-3

-------
Table K-l. (cont.)
Medium
Transferable Residues
Estimated Ratio of Geometric Means (95% CI)
Urban vs.
Rural
0.62
(0.10,3.82)
Low Income
vs. Mid/High
Income
0.58
(0.12,2.68)
Home vs.
Day Care
Environ-
ments

Home
Environment
(for Home
Children) vs.
Day Care
Environment

Home
Environment
(for Home
Children) vs.
Home
Environment
(for Day Care
Children)
0.66
(0.15,2.95)
Home
Environment
(for Day Care
Children) vs.
Day Care
Environment

Benzo [g/i j]perylene
Indoor Air
Outdoor Air
Soil
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface
Wipes
Transferable Residues
1.34
(0.90,2.01)
1.37
(0.88,2.15)
1.19
(0.49,2.89)
0.99
(0.60,1.65)
0.84
(0.42,1.69)
2.16
(0.46,10.20)
0.79
(0.16,4.03)
1.76**
(1.29,2.40)
1.41
(1.00,1.98)
2.49**
(1.27,4.90)
0.57**
(0.38,0.84)
1.64
(0.95,2.82)
1.66
(0.47,5.93)
0.62
(0.16,2.44)
1.39
(0.84,2.30)
1.41
(0.81,2.46)
0.54
(0.18,1.63)
0.55
(0.29,1.02)
0.12**
(0.05,0.29)


1.49
(0.79,2.81)
1.72
(0.86,3.47)
0.54
(0.14,2.16)
0.52
(0.24,1.14)
0.12**
(0.04,0.36)


1.15
(0.78,1.70)
1.50
(0.97,2.30)
1.00
(0.43,2.31)
0.91
(0.55,1.49)
0.99
(0.50,1.96)
0.28*
(0.08,0.97)
1.33
(0.35,5.10)
1.29
(0.68,2.45)
1.15
(0.57,2.33)
0.54
(0.13,2.18)
0.58
(0.26,1.27)
0.12**
(0.04,0.37)


Benzo[a]pyrene
Indoor Air
Outdoor Air
Soil
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface
Wipes
Transferable Residues
1.16
(0.78,1.72)
1.47*
(1.01,2.15)
1.20
(0.48,3.01)
1.07
(0.63,1.82)
0.90
(0.45,1.79)
1.88
(0.33,10.75)
1.27
(0.13,11.96)
1.94**
(1.43,2.62)
1.13
(0.84,1.50)
2.30*
(1.14,4.63)
0.55**
(0.37,0.84)
1.59
(0.93,2.72)
1.20
(0.29,5.02)
0.46
(0.07,3.07)
1.42
(0.86,2.34)
1.39
(0.87,2.21)
0.50
(0.16,1.58)
0.57
(0.30,1.09)
0.13**
(0.06,0.30)


1.48
(0.79,2.76)
1.62
(0.90,2.90)
0.48
(0.11,2.02)
0.54
(0.24,1.21)
0.13**
(0.04,0.36)


1.08
(0.74,1.58)
1.36
(0.95,1.94)
0.92
(0.38,2.19)
0.89
(0.53,1.49)
0.97
(0.50,1.89)
0.25
(0.06,1.03)
0.53
(0.08,3.40)
1.37
(0.73,2.57)
1.19
(0.66,2.15)
0.52
(0.12,2.22)
0.61
(0.27,1.38)
0.13**
(0.04,0.38)


Benzo[e]pyrene
Outdoor Air
Soil
Dust (ng/g)
Dust (ng/m2)
1.26
(0.87,1.84)
1.15
(0.47,2.79)
0.94
(0.56,1.59)
0.79
(0.39,1.60)
1.21
(0.91,1.60)
2.49**
(1.27,4.88)
0.60*
(0.40,0.90)
1.72
(1.00,2.96)
1.45
(0.91,2.30)
0.55
(0.18,1.66)
0.55
(0.29,1.05)
0.12**
(0.05,0.29)
1.71
(0.96,3.06)
0.53
(0.13,2.13)
0.51
(0.23,1.15)
0.12**
(0.04,0.36)
1.40
(0.98,1.99)
0.93
(0.40,2.16)
0.87
(0.52,1.45)
0.95
(0.48,1.88)
1.22
(0.68,2.20)
0.57
(0.14,2.29)
0.59
(0.26,1.34)
0.13**
(0.04,0.38)
       K-4

-------
Table K-l. (cont.)
Medium
Hard Floor Surface
Wipes
Transferable Residues
Estimated Ratio of Geometric Means (95% CI)
Urban vs.
Rural
2.11
(0.40,11.03)
1.22
(0.18,8.36)
Low Income
vs. Mid/High
Income
1.59
(0.41,6.18)
0.54
(0.11,2.74)
Home vs.
Day Care
Environ-
ments


Home
Environment
(for Home
Children) vs.
Day Care
Environment


Home
Environment
(for Home
Children) vs.
Home
Environment
(for Day Care
Children)
0.29
(0.08,1.12)
0.56
(0.11,2.73)
Home
Environment
(for Day Care
Children) vs.
Day Care
Environment


Benzylbutylphthalate
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface
Wipes
Food Preparation Surface
Wipes
Transferable Residues
0.82
(0.53,1.27)
0.58
(0.27,1.25)
2.86
(0.59,13.79)
0.76
(0.14,4.08)
8.94
(0.05,1626.9)
1.76**
(1.23,2.50)
4.75**
(2.62,8.64)
1.50
(0.41,5.44)
0.57
(0.14,2.34)
13.44
(0.19,941.47)
0.48**
(0.34,0.67)
0.10**
(0.04,0.25)



0.49**
(0.32,0.77)
0.10**
(0.03,0.32)



1.06
(0.64,1.73)
1.01
(0.48,2.14)
0.72
(0.20,2.56)
0.67
(0.17,2.70)
3.62
(0.07,175.15)
0.47**
(0.29,0.74)
0.10**
(0.03,0.32)



Bisphenol-A
Indoor Air
Hard Floor Surface
Wipes
Food Preparation Surface
Wipes
Transferable Residues
Solid Food (Children)
Liquid Food (Children)
1.11
(0.69,1.78)
1.31
(0.28,5.99)
0.68
(0.17,2.75)
0.90
(0.29,2.83)
0.96
(0.53,1.75)
1.03
(0.50,2.09)
1.37
(0.96,1.97)
1.10
(0.31,3.82)
1.08
(0.33,3.52)
0.70
(0.27,1.83)
0.86
(0.54,1.35)
1.04
(0.60,1.79)
1.77
(0.98,3.19)



1.30
(0.65,2.60)
0.53
(0.24,1.14)
2.05
(0.98,4.27)



1.15
(0.48,2.75)
0.63
(0.24,1.68)
1.33
(0.85,2.09)
0.23*
(0.07,0.81)
1.28
(0.40,4.06)
1.14
(0.44,2.92)
0.78
(0.44,1.38)
1.42
(0.71,2.85)
1.53
(0.73,3.22)



1.47
(0.61,3.56)
0.44
(0.16,1.19)
a4>/ia-Chlordane
Indoor Air
Outdoor Air
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface
Wipes
Food Preparation Surface
Wipes
0.68
(0.34,1.37)
1.25
(0.76,2.03)
0.77
(0.39,1.53)
0.64
(0.25,1.63)
1.40
(0.30,6.45)
1.90
(0.32,11.20)
1.53
(0.90,2.60)
1.36
(0.94,1.98)
0.72
(0.42,1.23)
2.13*
(1.03,4.41)
1.38
(0.39,4.81)
2.55
(0.57,11.32)
1.35
(0.56,3.25)
0.44**
(0.24,0.81)
0.42*
(0.19,0.97)
0.09**
(0.03,0.29)


1.32
(0.44,3.97)
0.42*
(0.20,0.90)
0.49
(0.17,1.38)
0.11**
(0.03,0.46)


0.96
(0.49,1.86)
0.89
(0.56,1.42)
1.33
(0.69,2.58)
1.40
(0.56,3.46)
0.93
(0.27,3.22)
1.78
(0.41,7.68)
1.38
(0.46,4.17)
0.47
(0.22,1.01)
0.37
(0.13,1.06)
0.08**
(0.02,0.34)


       K-5

-------
Table K-l. (cont.)
Medium
Estimated Ratio of Geometric Means (95% CI)
Urban vs.
Rural
Low Income
vs. Mid/High
Income
Home vs.
Day Care
Environ-
ments
Home
Environment
(for Home
Children) vs.
Day Care
Environment
Home
Environment
(for Home
Children) vs.
Home
Environment
(for Day Care
Children)
Home
Environment
(for Day Care
Children) vs.
Day Care
Environment
g«»i»ia-Chlordane
Indoor Air
Outdoor Air
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface
Wipes
Food Preparation Surface
Wipes
0.70
(0.34,1.44)
1.21
(0.70,2.10)
0.76
(0.38,1.54)
0.62
(0.24,1.61)
1.59
(0.30,8.27)
2.42
(0.31,18.59)
1.58
(0.90,2.75)
1.60*
(1.05,2.43)
0.73
(0.42,1.26)
2.09
(0.99,4.40)
1.98
(0.51,7.66)
3.29
(0.59,18.31)
1.31
(0.52,3.29)
0.41*
(0.21,0.80)
0.40*
(0.17,0.95)
0.09**
(0.03,0.28)


1.30
(0.41,4.15)
0.38*
(0.16,0.88)
0.47
(0.16,1.37)
0.10**
(0.02,0.44)


1.00
(0.50,2.00)
0.85
(0.50,1.44)
1.34
(0.68,2.66)
1.37
(0.54,3.47)
1.09
(0.29,4.14)
2.16
(0.40,11.63)
1.31
(0.41,4.19)
0.44
(0.19,1.04)
0.35
(0.12,1.04)
0.07**
(0.02,0.33)


Chlorpyrifos
Indoor Air
Outdoor Air
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface
Wipes
Food Preparation Surface
Wipes
Transferable Residues
Solid Food (Children)
0.94
(0.50,1.77)
0.73
(0.41,1.31)
0.76
(0.41,1.42)
0.62
(0.25,1.52)
0.78
(0.16,3.75)
0.85
(0.10,7.47)
1.45
(0.19,10.80)
1.20
(0.69,2.11)
1.36
(0.84,2.21)
0.64*
(0.41,1.00)
0.94
(0.58,1.53)
2.88**
(1.43,5.80)
1.12
(0.31,4.06)
4.28
(0.69,26.65)
1.80
(0.33,9.77)
1.37
(0.89,2.09)
1.78
(0.81,3.92)
1.45
(0.70,3.00)
1.01
(0.46,2.22)
0.27*
(0.09,0.84)



1.39
(0.72,2.69)
1.54
(0.57,4.15)
1.05
(0.42,2.62)
0.93
(0.35,2.50)
0.25
(0.06,1.06)



1.54
(0.67,3.51)
0.75
(0.41,1.38)
0.53*
(0.30,0.92)
0.86
(0.47,1.56)
0.91
(0.38,2.16)
1.39
(0.39,4.95)
1.11
(0.19,6.67)
1.30
(0.25,6.83)
1.21
(0.71,2.08)
2.05
(0.76,5.57)
2.00
(0.80,5.00)
1.09
(0.40,2.96)
0.28
(0.07,1.19)



1.26
(0.55,2.90)
Chrysene
Indoor Air
Outdoor Air
Soil
Dust (ng/g)
Dust (ng/m2)
1.34
(0.91,1.98)
1.49
(0.99,2.22)
1.21
(0.48,3.03)
0.96
(0.54,1.68)
0.81
(0.39,1.65)
1.76**
(1.31,2.37)
1.09
(0.80,1.49)
2.53**
(1.26,5.09)
0.59*
(0.38,0.91)
1.69
(0.97,2.96)
1.28
(0.78,2.12)
1.21
(0.74,2.00)
0.49
(0.16,1.53)
0.55
(0.28,1.10)
0.12**
(0.05,0.30)
1.46
(0.78,2.74)
1.33
(0.71,2.50)
0.48
(0.11,2.00)
0.49
(0.21,1.18)
0.12**
(0.04,0.35)
1.30
(0.90,1.89)
1.21
(0.83,1.78)
0.95
(0.40,2.28)
0.81
(0.47,1.40)
0.88
(0.44,1.77)
1.13
(0.60,2.12)
1.10
(0.59,2.07)
0.50
(0.12,2.12)
0.61
(0.26,1.47)
0.13**
(0.04,0.40)
       K-6

-------
Table K-l. (cont.)
Medium
Hard Floor Surface
Wipes
Food Preparation Surface
Wipes
Transferable Residues
Estimated Ratio of Geometric Means (95% CI)
Urban vs.
Rural
2.17
(0.40,11.59)
0.99
(0.41,2.41)
0.76
(0.09,6.83)
Low Income
vs. Mid/High
Income
1.95
(0.49,7.70)
1.42
(0.67,3.00)
0.71
(0.11,4.51)
Home vs.
Day Care
Environ-
ments



Home
Environment
(for Home
Children) vs.
Day Care
Environment



Home
Environment
(for Home
Children) vs.
Home
Environment
(for Day Care
Children)
0.44
(0.11,1.69)
1.22
(0.59,2.55)
0.98
(0.16,6.01)
Home
Environment
(for Day Care
Children) vs.
Day Care
Environment



Cyfluthrin
Transferable Residues
0.87
(0.09,8.35)
1.60
(0.24,10.72)


1.77
(0.28,11.40)

Diazinon
Indoor Air
Outdoor Air
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface
Wipes
Food Preparation Surface
Wipes
Transferable Residues
0.95
(0.43,2.11)
1.16
(0.69,1.94)
0.86
(0.40,1.85)
0.70
(0.27,1.81)
0.69
(0.08,6.28)
1.06
(0.06,20.46)
0.79
(0.03,22.00)
3.59**
(1.95,6.61)
0.90
(0.61,1.34)
2.06*
(1.14,3.72)
6.32**
(3.02,13.23)
0.97
(0.16,5.88)
1.98
(0.16,23.83)
0.21
(0.01,3.51)
0.82
(0.30,2.24)
1.41
(0.74,2.69)
0.36*
(0.14,0.96)
0.10**
(0.03,0.33)



0.92
(0.26,3.23)
1.40
(0.62,3.13)
0.45
(0.13,1.53)
0.12**
(0.03,0.57)



1.25
(0.58,2.68)
0.98
(0.60,1.60)
1.55
(0.74,3.23)
1.64
(0.66,4.11)
2.66
(0.45,15.85)
1.17
(0.10,13.41)
0.54
(0.03,8.45)
0.73
(0.21,2.61)
1.43
(0.63,3.21)
0.29
(0.09,1.00)
0.08**
(0.02,0.35)



Dibenzo [a,h] anthracene
Soil
Dust (ng/g)
Dust (ng/m2)
1.39
(0.66,2.90)
0.79
(0.46,1.36)
0.67
(0.32,1.37)
1.69
(0.96,2.96)
0.57**
(0.37,0.87)
1.64
(0.94,2.87)
0.58
(0.23,1.45)
0.52*
(0.27,1.00)
0.12**
(0.05,0.28)
0.53
(0.17,1.69)
0.49
(0.21,1.12)
0.12**
(0.04,0.35)
0.85
(0.42,1.71)
0.91
(0.54,1.53)
0.99
(0.49,2.00)
0.63
(0.20,2.00)
0.54
(0.23,1.25)
0.12**
(0.04,0.36)
Di-n-butylphthalate
Indoor Air
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface
Wipes
Food Preparation Surface
Wipes
1.08
(0.80,1.44)
1.17
(0.82,1.66)
0.92
(0.47,1.79)
1.85
(0.72,4.78)
0.52
(0.07,3.79)
1.04
(0.83,1.30)
0.91
(0.69,1.21)
2.56**
(1.52,4.32)
1.14
(0.52,2.48)
1.89
(0.36,9.98)
0.56**
(0.39,0.80)
0.50**
(0.34,0.73)
0.10**
(0.05,0.23)


0.48**
(0.30,0.75)
0.54**
(0.34,0.85)
0.11**
(0.04,0.30)


0.72*
(0.54,0.95)
1.15
(0.80,1.64)
1.11
(0.58,2.14)
0.60
(0.28,1.29)
0.83
(0.16,4.23)
0.66
(0.42,1.04)
0.47**
(0.29,0.75)
0.10**
(0.04,0.27)


       K-7

-------
Table K-l. (cont.)
Medium
Transferable Residues
Estimated Ratio of Geometric Means (95% CI)
Urban vs.
Rural
5.93
(0.10,352.99)
Low Income
vs. Mid/High
Income
2.34
(0.12,45.67)
Home vs.
Day Care
Environ-
ments

Home
Environment
(for Home
Children) vs.
Day Care
Environment

Home
Environment
(for Home
Children) vs.
Home
Environment
(for Day Care
Children)
3.06
(0.19,50.52)
Home
Environment
(for Day Care
Children) vs.
Day Care
Environment

/>,/>'-DDE
Solid Food (Children)
1.12
(0.68,1.85)
1.20
(0.82,1.75)
0.94
(0.54,1.64)
1.05
(0.52,2.12)
1.25
(0.77,2.03)
0.84
(0.42,1.71)
2,4-D (2,4-dichlorophenoxyacetic acid)
Dust (ng/g)
Dust (ng/m2)
Solid Food (Children)
Solid Food (Adults)
3.20**
(1.52,6.74)
2.64*
(1.15,6.07)
1.60*
(1.07,2.41)
1.37
(0.82,2.26)
0.22**
(0.13,0.39)
0.65
(0.34,1.23)
1.11
(0.82,1.52)
1.19
(0.81,1.75)
1.79
(0.76,4.25)
0.40
(0.15,1.05)
1.27
(0.87,1.86)

2.85
(0.97,8.41)
0.65
(0.19,2.20)
1.20
(0.74,1.95)

2.53**
(1.24,5.17)
2.67*
(1.20,5.93)
0.89
(0.59,1.35)
1.05
(0.71,1.53)
1.13
(0.37,3.40)
0.24*
(0.07,0.84)
1.35
(0.83,2.18)

Heptachlor
Indoor Air
Outdoor Air
0.82
(0.34,1.94)
0.99
(0.47,2.07)
1.38
(0.71,2.68)
1.26
(0.71,2.22)
0.73
(0.24,2.22)
0.54
(0.21,1.34)
0.68
(0.17,2.75)
0.52
(0.17,1.66)
0.87
(0.38,1.99)
0.96
(0.47,1.94)
0.78
(0.19,3.17)
0.55
(0.17,1.75)
Indeno [l,2,3-crf|pyrene
Indoor Air
Outdoor Air
Soil
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface
Wipes
Transferable Residues
1.22
(0.84,1.78)
1.25
(0.84,1.88)
1.20
(0.48,2.98)
1.12
(0.67,1.86)
0.94
(0.47,1.89)
1.90
(0.38,9.58)
1.20
(0.17,8.45)
1.90**
(1.42,2.54)
1.26
(0.92,1.71)
2.61**
(1.31,5.22)
0.59**
(0.40,0.88)
1.69
(0.98,2.92)
1.51
(0.40,5.67)
0.52
(0.10,2.71)
1.41
(0.87,2.27)
1.44
(0.87,2.37)
0.50
(0.16,1.54)
0.54
(0.29,1.01)
0.12**
(0.05,0.29)


1.50
(0.82,2.74)
1.71
(0.91,3.20)
0.51
(0.12,2.11)
0.55
(0.25,1.19)
0.13**
(0.04,0.38)


1.14
(0.79,1.63)
1.41
(0.96,2.07)
1.05
(0.44,2.49)
1.01
(0.62,1.66)
1.11
(0.56,2.19)
0.25*
(0.07,0.91)
0.55
(0.11,2.77)
1.32
(0.72,2.41)
1.21
(0.65,2.28)
0.48
(0.12,2.02)
0.54
(0.25,1.19)
0.12**
(0.04,0.34)


Pentachlorophenol
Indoor Air
Outdoor Air
Dust (ng/g)
0.75
(0.43,1.33)
0.67
(0.42,1.07)
0.90
(0.47,1.74)
1.77*
(1.14,2.73)
0.69*
(0.48,0.98)
0.86
(0.52,1.44)
0.83
(0.41,1.65)
0.99
(0.55,1.77)
1.07
(0.48,2.37)
0.75
(0.31,1.78)
0.83
(0.40,1.72)
1.35
(0.50,3.65)
0.81
(0.47,1.41)
0.71
(0.45,1.11)
1.59
(0.84,2.99)
0.92
(0.38,2.20)
1.17
(0.56,2.45)
0.85
(0.31,2.34)

-------
Table K-l. (cont.)
Medium
Dust (ng/m2)
Estimated Ratio of Geometric Means (95% CI)
Urban vs.
Rural
0.75
(0.29,1.91)
Low Income
vs. Mid/High
Income
2.56*
(1.24,5.30)
Home vs.
Day Care
Environ-
ments
0.24*
(0.07,0.74)
Home
Environment
(for Home
Children) vs.
Day Care
Environment
0.30
(0.07,1.28)
Home
Environment
(for Home
Children) vs.
Home
Environment
(for Day Care
Children)
1.67
(0.68,4.12)
Home
Environment
(for Day Care
Children) vs.
Day Care
Environment
0.18*
(0.04,0.79)
cis-Permethrin
Indoor Air
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface
Wipes
Food Preparation Surface
Wipes
Transferable Residues
1.00
(0.48,2.09)
1.09
(0.53,2.27)
0.90
(0.33,2.47)
0.38
(0.04,3.44)
0.81
(0.02,42.25)
0.15
(0.01,4.02)
4.17**
(2.37,7.34)
1.07
(0.61,1.89)
3.19**
(1.47,6.95)
1.39
(0.23,8.46)
13.61
(0.49,381.09)
1.27
(0.08,19.64)
2.07
(0.83,5.14)
0.82
(0.33,2.01)
0.18**
(0.05,0.62)



1.95
(0.62,6.11)
0.87
(0.28,2.68)
0.20*
(0.04,0.92)



0.89
(0.44,1.81)
1.14
(0.56,2.30)
1.20
(0.46,3.15)
1.57
(0.26,9.34)
1.72
(0.07,45.10)
2.79
(0.19,40.91)
2.19
(0.69,6.91)
0.76
(0.24,2.40)
0.16*
(0.03,0.79)



frans-Permethrin
Indoor Air
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface
Wipes
Food Preparation Surface
Wipes
Transferable Residues
1.04
(0.51,2.14)
1.04
(0.48,2.26)
0.86
(0.30,2.45)
0.38
(0.04,4.02)
1.17
(0.02,69.94)
0.17
(0.01,5.11)
3.85**
(2.22,6.68)
0.97
(0.53,1.77)
2.89*
(1.28,6.49)
1.41
(0.20,9.75)
13.15
(0.42,412.15)
1.33
(0.08,22.83)
1.88
(0.78,4.52)
0.73
(0.28,1.90)
0.16**
(0.04,0.58)



1.80
(0.60,5.43)
0.80
(0.24,2.66)
0.18*
(0.04,0.91)



0.93
(0.46,1.85)
1.22
(0.58,2.58)
1.28
(0.47,3.52)
1.86
(0.27,12.59)
1.95
(0.07,57.09)
2.93
(0.18,47.31)
1.95
(0.64,5.91)
0.66
(0.19,2.22)
0.14*
(0.03,0.73)



PCB52
Indoor Air
Outdoor Air
0.82
(0.49,1.36)
1.11
(0.75,1.64)
0.84
(0.57,1.24)
0.87
(0.65,1.18)
0.74
(0.40,1.37)
0.71
(0.44,1.16)
0.77
(0.36,1.66)
0.56
(0.31,1.04)
1.07
(0.66,1.75)
0.63*
(0.43,0.92)
0.72
(0.33,1.56)
0.90
(0.48,1.65)
PCB95
Indoor Air
0.93
(0.60,1.45)
1.11
(0.79,1.57)
1.00
(0.59,1.69)
1.02
(0.53,1.98)
1.05
(0.68,1.62)
0.97
(0.50,1.89)
PCB 101
Indoor Air
0.79
(0.49,1.27)
1.02
(0.71,1.48)
0.87
(0.49,1.56)
0.98
(0.47,2.03)
1.26
(0.79,2.00)
0.78
(0.37,1.62)
       K-9

-------
                                              Table K-l.  (cont.)
Medium
Estimated Ratio of Geometric Means (95% CI)
Urban vs.
Rural
Low Income
vs. Mid/High
Income
Home vs.
Day Care
Environ-
ments
Home
Environment
(for Home
Children) vs.
Day Care
Environment
Home
Environment
(for Home
Children) vs.
Home
Environment
(for Day Care
Children)
Home
Environment
(for Day Care
Children) vs.
Day Care
Environment
3,5,6-TCP(3,5,6-trichloro-2-pyridinol)
Indoor Air
Outdoor Air
Soil
Dust (ng/g)
Dust (ng/m2)
Solid Food (Children)
Solid Food (Adults)
1.07
(0.58,1.99)
0.85
(0.54,1.33)
0.75
(0.39,1.44)
0.75
(0.40,1.40)
0.62
(0.23,1.66)
0.94
(0.62,1.42)
1.04
(0.64,1.69)
1.03
(0.65,1.66)
0.65*
(0.46,0.92)
1.09
(0.67,1.80)
1.15
(0.71,1.88)
3.40**
(1.58,7.33)
0.48**
(0.35,0.66)
0.72
(0.49,1.04)
1.96
(0.90,4.31)
1.84*
(1.06,3.21)
2.29*
(1.02,5.15)
1.92
(0.91,4.06)
0.42
(0.12,1.40)
0.75
(0.47,1.21)

1.59
(0.60,4.25)
1.72
(0.86,3.45)
1.87
(0.68,5.18)
1.99
(0.78,5.09)
0.44
(0.10,2.02)
0.80
(0.44,1.45)

0.66
(0.36,1.18)
0.87
(0.57,1.33)
0.67
(0.36,1.24)
1.08
(0.58,1.99)
1.13
(0.44,2.95)
1.12
(0.76,1.67)
0.97
(0.67,1.40)
2.42
(0.90,6.51)
1.97
(0.98,3.97)
2.80*
(1.00,7.78)
1.85
(0.71,4.80)
0.39
(0.08,1.82)
0.71
(0.39,1.30)

* Significantly different from 1 at the 0.05 level, but not at the 0.01 level.
** Significantly different from 1 at the 0.01 level.
                                                       K-10

-------
Table K-2. Estimated Ratio Between Selected Strata of Geometric Mean Pollutant Levels
          in OH Multimedia Samples, and 95% Confidence Intervals on This Ratio, for
          Pollutants Detected in At Least 50% of Samples
Medium
Estimated Ratio of Geometric Means (95% CI)
Urban vs.
Rural
Low Income
vs. Mid/High
Income
Home vs.
Day Care
Environ-
ments
Home
Environment
(for Home
Children) vs.
Day Care
Environment
Home
Environment
(for Home
Children) vs.
Home
Environment
(for Day Care
Children)
Home
Environment
(for Day Care
Children) vs.
Day Care
Environment
Atrazine
Drinking Water
1.21
(0.56,2.60)
0.88
(0.50,1.53)
0.57
(0.27,1.20)
0.52
(0.21,1.32)
0.83
(0.43,1.63)
0.63
(0.24,1.65)
Benz [a] anthracene
Soil
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface
Wipes
Transferable Residues
0.84
(0.23,3.08)
3 97**
(2.06,7.64)
3.19**
(1.40,7.26)


1.94
(0.77,4.92)
0.58*
(0.36,0.95)
0.94
(0.51,1.74)
1.10
(0.47,2.56)
0.84
(0.11,6.34)
0.98
(0.28,3.44)
0.45*
(0.24,0.86)
0.17**
(0.07,0.37)
2.00
(0.55,7.19)

0.86
(0.18,4.15)
0.36**
(0.16,0.81)
0.11**
(0.04,0.31)
1.33
(0.27,6.53)

0.77
(0.25,2.38)
0.64
(0.36,1.15)
0.47*
(0.23,0.97)
0.44
(0.14,1.40)
0.62
(0.08,4.68)
1.11
(0.22,5.73)
0.56
(0.24,1.31)
0.24**
(0.08,0.69)
3.00
(0.53,16.90)

Benzo[6]fluoranthene
Soil
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface
Wipes
Transferable Residues
0.79
(0.21,2.96)
3.63**
(1.94,6.80)
2 92**
(1.31,6.49)


1.86
(0.72,4.80)
0.57*
(0.36,0.91)
0.92
(0.51,1.68)
1.17
(0.45,3.07)
0.50
(0.04,6.82)
0.84
(0.23,3.00)
0.44**
(0.24,0.81)
0.16**
(0.07,0.35)
0.93
(0.21,4.19)

0.78
(0.16,3.85)
0.37**
(0.17,0.80)
0.11**
(0.04,0.31)
0.66
(0.11,4.08)

0.87
(0.28,2.72)
0.70
(0.40,1.23)
0.51
(0.25,1.05)
0.50
(0.13,1.93)
0.39
(0.03,5.32)
0.90
(0.17,4.75)
0.52
(0.23,1.17)
0.22**
(0.08,0.63)
1.32
(0.18,9.50)

Benzo[&]fluoranthene
Soil
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface
Wipes
Transferable Residues
0.80
(0.25,2.60)
3.35**
(1.77,6.31)
2.70*
(1.24,5.90)


2.17
(0.94,5.03)
0.58*
(0.36,0.93)
0.94
(0.52,1.68)
1.00
(0.38,2.64)
0.62
(0.07,5.50)
0.86
(0.28,2.67)
0.43**
(0.23,0.79)
0.16**
(0.07,0.34)
1.30
(0.30,5.58)

0.77
(0.19,3.17)
0.36**
(0.17,0.79)
0.11**
(0.04,0.30)
0.88
(0.15,5.33)

0.79
(0.29,2.19)
0.73
(0.41,1.28)
0.53
(0.26,1.06)
0.46
(0.12,1.72)
0.57
(0.06,5.13)
0.97
(0.22,4.24)
0.50
(0.22,1.13)
0.22**
(0.08,0.59)
1.93
(0.27,13.64)

Benz o [ghi] pery lene
Soil
0.79
(0.22,2.81)
2.10
(0.85,5.19)
0.94
(0.28,3.18)
0.88
(0.19,4.05)
0.87
(0.29,2.60)
1.01
(0.20,4.95)
                                       K-ll

-------
Table K-2. (cont.)
Medium
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface
Wipes
Transferable Residues
Estimated Ratio of Geometric Means (95% CI)
Urban vs.
Rural
3.28**
(1.76,6.14)
2.64*
(1.18,5.88)


Low Income
vs. Mid/High
Income
0.56*
(0.35,0.89)
0.91
(0.50,1.65)
0.96
(0.36,2.55)
0.24
(0.03,2.10)
Home vs.
Day Care
Environ-
ments
0.43**
(0.23,0.79)
0.16**
(0.07,0.34)
1.21
(0.28,5.32)

Home
Environment
(for Home
Children) vs.
Day Care
Environment
0.36**
(0.17,0.78)
0.11**
(0.04,0.30)
0.78
(0.12,4.91)

Home
Environment
(for Home
Children) vs.
Home
Environment
(for Day Care
Children)
0.71
(0.41,1.24)
0.52
(0.25,1.06)
0.42
(0.11,1.57)
0.30
(0.03,2.62)
Home
Environment
(for Day Care
Children) vs.
Day Care
Environment
0.50
(0.22,1.13)
0.22**
(0.08,0.61)
1.88
(0.25,13.86)

Benzo [a] py rene
Soil
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface
Wipes
Transferable Residues
0.76
(0.20,2.86)
3.57**
(1.85,6.88)
2.87*
(1.28,6.46)


1.94
(0.76,4.99)
0.55*
(0.34,0.90)
0.89
(0.49,1.63)
1.05
(0.38,2.90)
1.62
(0.15,17.52)
0.98
(0.28,3.51)
0.49*
(0.26,0.93)
0.18**
(0.08,0.39)
1.74
(0.38,7.98)

0.87
(0.18,4.30)
0.40*
(0.18,0.90)
0.13**
(0.05,0.34)
1.10
(0.17,7.25)

0.79
(0.25,2.46)
0.68
(0.38,1.22)
0.50
(0.24,1.02)
0.40
(0.10,1.61)
0.74
(0.07,7.95)
1.11
(0.21,5.85)
0.59
(0.25,1.37)
0.25**
(0.09,0.72)
2.75
(0.36,21.22)

Benzo [e]py rene
Soil
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface
Wipes
Transferable Residues
0.80
(0.23,2.77)
3.40**
(1.83,6.33)
2.73*
(1.24,6.04)


2.00
(0.82,4.87)
0.57*
(0.36,0.90)
0.92
(0.51,1.66)
1.04
(0.39,2.73)
0.85
(0.09,8.29)
0.94
(0.28,3.12)
0.45*
(0.24,0.82)
0.16**
(0.07,0.36)
1.10
(0.26,4.75)

0.87
(0.19,3.91)
0.38**
(0.17,0.81)
0.12**
(0.04,0.31)
0.75
(0.12,4.54)

0.86
(0.29,2.51)
0.72
(0.41,1.25)
0.52
(0.26,1.06)
0.46
(0.12,1.74)
0.55
(0.06,5.32)
1.01
(0.21,4.86)
0.53
(0.24,1.17)
0.23**
(0.08,0.63)
1.62
(0.23,11.51)

Benzylbutylphthalate
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface
Wipes
Food Preparation Surface
Wipes
Transferable Residues
0.73
(0.41,1.30)
0.56
(0.25,1.28)



1.50
(0.98,2.30)
2.52**
(1.37,4.63)
3.52
(0.53,23.30)
0.67
(0.16,2.85)
0.90
(0.41,2.00)
0.41**
(0.23,0.71)
0.14**
(0.06,0.32)
0.06
(0.00,1.09)


0.38**
(0.19,0.76)
0.11**
(0.04,0.30)
0.03
(0.00,1.09)


0.86
(0.52,1.43)
0.59
(0.29,1.23)
0.27
(0.02,3.77)
0.37
(0.09,1.57)
0.53
(0.24,1.17)
0.44*
(0.21,0.91)
0.19**
(0.07,0.53)
0.11
(0.00,5.42)


       K-12

-------
Table K-2. (cont.)
Medium
Estimated Ratio of Geometric Means (95% CI)
Urban vs.
Rural
Low Income
vs. Mid/High
Income
Home vs.
Day Care
Environ-
ments
Home
Environment
(for Home
Children) vs.
Day Care
Environment
Home
Environment
(for Home
Children) vs.
Home
Environment
(for Day Care
Children)
Home
Environment
(for Day Care
Children) vs.
Day Care
Environment
Bisphenol-A
Indoor Air
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface
Wipes
Food Preparation Surface
Wipes
Transferable Residues
Solid Food (Children)
Liquid Food (Children)
1.03
(0.67,1.58)
1.18
(0.83,1.68)
0.86
(0.48,1.53)



1.15
(0.72,1.86)
1.45
(0.55,3.79)
1.29
(0.95,1.76)
0.89
(0.69,1.17)
1.47
(0.95,2.26)
2.53
(0.71,8.97)
1.53
(0.06,37.26)
10.40
(0.02,4435.5)
1.20
(0.85,1.69)
0.94
(0.49,1.82)
1.26
(0.83,1.91)
0.98
(0.70,1.38)
0.33**
(0.19,0.59)
2.80
(0.41,18.99)


1.09
(0.70,1.67)
0.67
(0.32,1.40)
1.02
(0.61,1.71)
1.13
(0.74,1.74)
0.32**
(0.15,0.65)
1.45
(0.13,15.57)


1.02
(0.59,1.75)
0.65
(0.25,1.68)
0.65*
(0.45,0.95)
1.33
(0.97,1.83)
0.91
(0.54,1.53)
0.27
(0.05,1.49)
0.13
(0.01,3.16)
1.62
(0.00,1758.9)
0.88
(0.58,1.34)
0.96
(0.42,2.19)
1.56
(0.91,2.69)
0.85
(0.54,1.33)
0.35**
(0.17,0.73)
5.44
(0.41,71.90)


1.16
(0.65,2.05)
0.68
(0.25,1.84)
«§>/ia-Chlordane
Indoor Air
Outdoor Air
Soil
Dust (ng/g)
Dust (ng/m2)
0.91
(0.46,1.77)
1.34
(0.84,2.12)
1.07
(0.38,3.05)
1.37
(0.69,2.73)
1.10
(0.42,2.91)
1.32
(0.82,2.14)
0.95
(0.68,1.32)
2.12*
(1.00,4.47)
1.24
(0.74,2.06)
2.00
(0.97,4.14)
1.82
(0.96,3.48)
1.63*
(1.05,2.54)
2.80*
(1.02,7.67)
1.12
(0.57,2.22)
0.41
(0.16,1.07)
2.00
(0.89,4.49)
1.74
(1.00,3.04)
3.30
(0.93,11.66)
1.30
(0.56,3.06)
0.41
(0.12,1.35)
1.21
(0.67,2.16)
1.14
(0.77,1.70)
1.39
(0.56,3.42)
1.35
(0.74,2.49)
0.98
(0.41,2.34)
1.66
(0.71,3.87)
1.53
(0.86,2.73)
2.37
(0.64,8.87)
0.96
(0.40,2.35)
0.41
(0.12,1.45)
ga»i»ia-Chlordane
Indoor Air
Outdoor Air
Soil
Dust (ng/g)
Dust (ng/m2)
0.93
(0.46,1.87)
1.35
(0.84,2.16)
1.06
(0.38,2.95)
1.28
(0.63,2.60)
1.03
(0.38,2.75)
1.30
(0.78,2.15)
0.97
(0.69,1.36)
2.00
(0.96,4.14)
1.28
(0.75,2.17)
2.07
(0.99,4.33)
1.82
(0.92,3.59)
1.62*
(1.02,2.55)
2.55
(0.95,6.81)
1.06
(0.52,2.13)
0.39
(0.15,1.02)
1.99
(0.85,4.66)
1.76
(0.99,3.11)
2.96
(0.86,10.13)
1.23
(0.51,2.98)
0.38
(0.11,1.30)
1.20
(0.65,2.21)
1.18
(0.79,1.78)
1.35
(0.56,3.25)
1.36
(0.73,2.56)
0.99
(0.41,2.39)
1.66
(0.68,4.04)
1.49
(0.82,2.70)
2.19
(0.61,7.92)
0.90
(0.36,2.27)
0.39
(0.11,1.39)
Chlorpyrifos
Indoor Air
1.64
(0.80,3.37)
1.63
(0.97,2.74)
0.76
(0.38,1.52)
0.75
(0.31,1.79)
0.98
(0.52,1.84)
0.76
(0.31,1.90)
       K-13

-------
Table K-2. (cont.)
Medium
Outdoor Air
Dust (ng/g)
Dust (ng/m2)
Food Preparation Surface
Wipes
Transferable Residues
Solid Food (Children)
Estimated Ratio of Geometric Means (95% CI)
Urban vs.
Rural
1.57
(0.92,2.68)
1.52
(0.67,3.44)
1.22
(0.45,3.32)


1.28
(0.75,2.19)
Low Income
vs. Mid/High
Income
0.97
(0.64,1.48)
2.09*
(1.14,3.86)
3 39**
(1.61,7.15)
7.51
(0.13,443.21)
18.35
(0.36,924.03)
2.06**
(1.39,3.04)
Home vs.
Day Care
Environ-
ments
1.74*
(1.01,3.00)
0.37*
(0.17,0.84)
0.14**
(0.05,0.37)


1.17
(0.74,1.85)
Home
Environment
(for Home
Children) vs.
Day Care
Environment
1.91
(0.96,3.79)
0.36*
(0.13,0.99)
0.11**
(0.03,0.38)


1.32
(0.75,2.34)
Home
Environment
(for Home
Children) vs.
Home
Environment
(for Day Care
Children)
1.20
(0.72,1.99)
0.92
(0.45,1.91)
0.67
(0.28,1.64)
0.40
(0.01,23.68)
0.17
(0.00,8.50)
1.28
(0.78,2.08)
Home
Environment
(for Day Care
Children) vs.
Day Care
Environment
1.59
(0.78,3.25)
0.39
(0.13,1.12)
0.17**
(0.05,0.60)


1.04
(0.56,1.91)
Chrysene
Soil
Dust (ng/g)
Dust (ng/m2)
Transferable Residues
0.92
(0.26,3.17)
3.71**
(1.96,7.04)
2 99**
(1.34,6.69)

1.79
(0.74,4.34)
0.56*
(0.35,0.90)
0.91
(0.50,1.66)
0.83
(0.08,8.64)
0.89
(0.27,2.94)
0.43**
(0.23,0.82)
0.16**
(0.07,0.35)

0.79
(0.18,3.53)
0.37**
(0.17,0.80)
0.11**
(0.04,0.31)

0.79
(0.27,2.31)
0.71
(0.40,1.25)
0.51
(0.25,1.05)
0.57
(0.06,5.99)
1.00
(0.21,4.76)
0.52
(0.23,1.18)
0.22**
(0.08,0.62)

Cyfluthrin
Dust (ng/g)
Dust (ng/m2)
2.33*
(1.14,4.77)
1.96
(0.73,5.27)
1.31
(0.76,2.26)
2.12*
(1.01,4.45)
0.62
(0.31,1.22)
0.23**
(0.09,0.60)
0.73
(0.31,1.70)
0.23*
(0.07,0.77)
1.40
(0.73,2.67)
1.02
(0.42,2.46)
0.52
(0.21,1.28)
0.23*
(0.06,0.80)
Diazinon
Indoor Air
Outdoor Air
Dust (ng/g)
Dust (ng/m2)
Transferable Residues
1.04
(0.44,2.49)
2.70**
(1.54,4.73)
1.79
(0.67,4.78)
1.45
(0.52,4.02)

1.67
(0.89,3.12)
0.60*
(0.40,0.89)
1.39
(0.67,2.88)
2.24*
(1.04,4.82)
3.32
(0.44,24.99)
0.78
(0.34,1.80)
1.68
(0.97,2.88)
0.46
(0.18,1.21)
0.17**
(0.06,0.46)

0.66
(0.23,1.88)
1.83
(0.93,3.61)
0.40
(0.12,1.33)
0.13**
(0.04,0.44)

0.72
(0.34,1.53)
1.19
(0.74,1.94)
0.75
(0.31,1.79)
0.54
(0.22,1.35)
1.92
(0.26,14.44)
0.92
(0.31,2.74)
1.53
(0.76,3.11)
0.54
(0.15,1.89)
0.23*
(0.06,0.86)

Dibenzo[«,/i]anthracene
Soil
Dust (ng/g)
0.80
(0.26,2.51)
3.66**
(1.94,6.89)
2.09
(0.93,4.72)
0.58*
(0.36,0.93)
1.14
(0.38,3.41)
0.42**
(0.22,0.78)
1.08
(0.27,4.26)
0.34**
(0.16,0.75)
0.90
(0.34,2.40)
0.69
(0.39,1.21)
1.20
(0.29,5.03)
0.50
(0.22,1.13)
       K-14

-------
Table K-2. (cont.)
Medium
Dust (ng/m2)
Estimated Ratio of Geometric Means (95% CI)
Urban vs.
Rural
2.94*
(1.30,6.66)
Low Income
vs. Mid/High
Income
0.94
(0.51,1.74)
Home vs.
Day Care
Environ-
ments
0.15**
(0.07,0.34)
Home
Environment
(for Home
Children) vs.
Day Care
Environment
0.11**
(0.04,0.29)
Home
Environment
(for Home
Children) vs.
Home
Environment
(for Day Care
Children)
0.50
(0.24,1.04)
Home
Environment
(for Day Care
Children) vs.
Day Care
Environment
0.22**
(0.08,0.62)
Di-n-butylphthalate
Indoor Air
Soil
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface
Wipes
Food Preparation Surface
Wipes
Transferable Residues
0.76
(0.49,1.18)
0.70
(0.29,1.64)
1.44
(0.99,2.12)
1.16
(0.58,2.33)



0.99
(0.72,1.35)
0.90
(0.48,1.67)
1.09
(0.82,1.44)
1.76*
(1.05,2.96)
1.34
(0.35,5.09)
0.55
(0.16,1.83)
1.47
(0.63,3.44)
0.56**
(0.37,0.86)
1.55
(0.67,3.55)
0.38**
(0.26,0.56)
0.14**
(0.07,0.28)
0.16
(0.02,1.19)


0.56*
(0.33,0.95)
2.78
(0.98,7.85)
0.41**
(0.25,0.65)
0.13**
(0.05,0.30)
0.17
(0.01,2.04)


0.99
(0.68,1.45)
3.23**
(1.53,6.83)
1.13
(0.81,1.59)
0.82
(0.44,1.53)
1.10
(0.18,6.77)
0.58
(0.17,1.96)
0.86
(0.37,2.01)
0.56*
(0.32,0.99)
0.86
(0.29,2.55)
0.36**
(0.22,0.59)
0.15**
(0.06,0.38)
0.15
(0.01,2.30)


/>,/>'-DDE
Solid Food (Children)
1.23
(0.76,1.97)
0.94
(0.66,1.33)
1.45
(0.96,2.18)
1.26
(0.75,2.11)
0.76
(0.49,1.17)
1.66
(0.95,2.88)
2,4-D (2,4-dichlorophenoxyacetic acid)
Dust (ng/g)
Dust (ng/m2)
2.38*
(1.03,5.48)
1.79
(0.67,4.80)
0.24**
(0.13,0.45)
0.39*
(0.19,0.81)
1.02
(0.46,2.28)
0.38*
(0.15,0.97)
0.99
(0.36,2.71)
0.31
(0.10,1.03)
0.94
(0.46,1.94)
0.70
(0.30,1.64)
1.05
(0.37,3.00)
0.45
(0.13,1.56)
Indeno [l,2,3-crf|pyrene
Soil
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface
Wipes
Transferable Residues
0.84
(0.23,3.06)
3.43**
(1.79,6.54)
2.75*
(1.22,6.22)


1.97
(0.78,4.98)
0.56*
(0.35,0.91)
0.91
(0.50,1.68)
0.92
(0.34,2.47)
0.24
(0.03,1.91)
0.92
(0.26,3.20)
0.41**
(0.22,0.78)
0.15**
(0.07,0.34)
1.24
(0.28,5.53)

0.85
(0.18,4.07)
0.35**
(0.16,0.78)
0.11**
(0.04,0.30)
0.82
(0.13,5.26)

0.86
(0.28,2.64)
0.72
(0.40,1.28)
0.52
(0.25,1.08)
0.44
(0.11,1.68)
0.49
(0.06,3.86)
0.99
(0.19,5.04)
0.49
(0.21,1.12)
0.21**
(0.07,0.59)
1.88
(0.25,14.08)

IMP (2-isopropyl-6-methyl-4-pyrimidinol)
Indoor Air
Outdoor Air
1.25
(0.68,2.31)
3.87**
(2.00,7.48)
1.66*
(1.07,2.58)
0.48**
(0.30,0.76)
0.95
(0.53,1.71)
1.15
(0.61,2.18)
0.91
(0.44,1.91)
1.32
(0.59,2.91)
0.92
(0.54,1.57)
1.30
(0.75,2.26)
0.99
(0.46,2.14)
1.01
(0.44,2.31)
       K-15

-------
Table K-2. (cont.)
Medium
Dust (ng/g)
Dust (ng/m2)
Solid Food (Children)
Solid Food (Adults)
Estimated Ratio of Geometric Means (95% CI)
Urban vs.
Rural
0.91
(0.39,2.15)
0.74
(0.29,1.88)
1.44
(0.88,2.37)
1.13
(0.56,2.27)
Low Income
vs. Mid/High
Income
1.19
(0.63,2.26)
1.93
(0.96,3.89)
0.86
(0.60,1.23)
0.67
(0.42,1.06)
Home vs.
Day Care
Environ-
ments
1.05
(0.46,2.43)
0.39*
(0.16,0.98)
1.30
(0.85,1.99)

Home
Environment
(for Home
Children) vs.
Day Care
Environment
0.86
(0.30,2.43)
0.27*
(0.09,0.86)
1.38
(0.81,2.35)

Home
Environment
(for Home
Children) vs.
Home
Environment
(for Day Care
Children)
0.66
(0.31,1.41)
0.48
(0.21,1.10)
1.13
(0.72,1.76)
0.90
(0.58,1.39)
Home
Environment
(for Day Care
Children) vs.
Day Care
Environment
1.30
(0.43,3.88)
0.57
(0.17,1.88)
1.23
(0.70,2.16)

Pentachlorophenol
Indoor Air
Outdoor Air
Dust (ng/g)
Dust (ng/m2)
0.59
(0.27,1.31)
1.67
(0.73,3.82)
0.89
(0.49,1.60)
0.67
(0.26,1.76)
0.93
(0.52,1.66)
0.67
(0.37,1.23)
1.11
(0.72,1.71)
1.79
(0.89,3.60)
2.16*
(1.01,4.65)
1.46
(0.64,3.33)
1.20
(0.69,2.10)
0.44
(0.17,1.09)
3.02*
(1.16,7.87)
1.80
(0.64,5.05)
1.21
(0.60,2.45)
0.38
(0.12,1.20)
1.95
(0.97,3.91)
1.51
(0.74,3.10)
1.02
(0.61,1.71)
0.76
(0.33,1.74)
1.55
(0.57,4.22)
1.19
(0.41,3.45)
1.19
(0.57,2.46)
0.50
(0.15,1.67)
cis-Permethrin
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface
Wipes
Transferable Residues
0.62
(0.29,1.31)
0.50
(0.18,1.40)


1.36
(0.78,2.39)
2.21*
(1.02,4.76)
3.46
(0.27,43.85)
7.19
(0.11,474.66)
0.55
(0.26,1.14)
0.20**
(0.07,0.55)
8.06
(0.14,463.8)

0.52
(0.21,1.32)
0.16**
(0.05,0.57)
5.03
(0.04,656.05)

0.91
(0.47,1.78)
0.66
(0.27,1.66)
0.39
(0.01,13.96)
0.26
(0.00,17.14)
0.57
(0.22,1.50)
0.25*
(0.07,0.92)
12.92
(0.07,2565.9)

fro«s-Permethrin
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface
Wipes
Transferable Residues
0.66
(0.29,1.51)
0.51
(0.18,1.49)


1.40
(0.76,2.61)
2.22
(1.00,4.93)
3.78
(0.29,49.88)
6.27
(0.14,274.20)
0.55
(0.24,1.25)
0.19**
(0.07,0.54)
8.98
(0.13,628.5)

0.54
(0.19,1.50)
0.16**
(0.04,0.58)
5.82
(0.04,896.71)

0.94
(0.45,1.97)
0.68
(0.26,1.76)
0.42
(0.01,16.55)
0.20
(0.00,8.85)
0.57
(0.20,1.66)
0.23*
(0.06,0.91)
13.86
(0.06,3300.1)

PCB52
Indoor Air
Outdoor Air
Dust (ng/g)
0.74
(0.37,1.45)
1.30
(0.75,2.24)
1.03
(0.58,1.81)
0.90
(0.55,1.45)
0.84
(0.56,1.25)
0.98
(0.64,1.51)
0.74
(0.39,1.42)
0.82
(0.48,1.41)
0.66
(0.38,1.14)
0.64
(0.29,1.43)
0.81
(0.41,1.59)
0.73
(0.37,1.45)
0.75
(0.42,1.35)
0.98
(0.61,1.57)
1.22
(0.73,2.04)
0.85
(0.37,1.98)
0.83
(0.41,1.68)
0.60
(0.29,1.23)
       K-16

-------
                                              Table K-2.  (cont.)
Medium
Dust (ng/m2)
Transferable Residues
Estimated Ratio of Geometric Means (95% CI)
Urban vs.
Rural
0.84
(0.40,1.75)

Low Income
vs. Mid/High
Income
1.59
(0.92,2.76)
2.85
(0.26,30.75)
Home vs.
Day Care
Environ-
ments
0.24**
(0.12,0.49)

Home
Environment
(for Home
Children) vs.
Day Care
Environment
0.23**
(0.09,0.55)

Home
Environment
(for Home
Children) vs.
Home
Environment
(for Day Care
Children)
0.89
(0.46,1.71)
1.42
(0.13,15.29)
Home
Environment
(for Day Care
Children) vs.
Day Care
Environment
0.26**
(0.10,0.65)

PCB95
Indoor Air
0.82
(0.40,1.65)
0.91
(0.57,1.44)
1.03
(0.56,1.89)
0.98
(0.48,1.99)
0.90
(0.50,1.63)
1.09
(0.51,2.34)
PCB 101
Indoor Air
0.68
(0.35,1.31)
0.77
(0.48,1.25)
1.07
(0.67,1.71)
0.90
(0.51,1.61)
0.71
(0.39,1.30)
1.27
(0.65,2.45)
3,5,6-TCP(3,5,6-trichloro-2-pyridinol)
Indoor Air
Outdoor Air
Soil
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface
Wipes
Solid Food (Children)
Solid Food (Adults)
1.28
(0.70,2.33)
1.22
(0.78,1.92)
2.80**
(1.32,5.96)
1.84
(0.92,3.67)
1.48
(0.57,3.84)
2.72
(0.05,151.89)
1.05
(0.62,1.79)
1.14
(0.62,2.09)
1.72*
(1.11,2.66)
0.90
(0.66,1.23)
0.90
(0.52,1.54)
1.45
(0.87,2.43)
2.35*
(1.15,4.79)
2.67
(0.33,21.31)
1.16
(0.79,1.70)
1.10
(0.72,1.69)
0.79
(0.44,1.42)
1.35
(0.89,2.06)
1.27
(0.61,2.62)
0.78
(0.40,1.54)
0.29**
(0.11,0.73)
2.52
(0.19,33.93)
0.98
(0.62,1.55)

0.83
(0.40,1.71)
1.45
(0.86,2.46)
1.17
(0.47,2.91)
0.74
(0.31,1.72)
0.23*
(0.07,0.75)
1.90
(0.07,50.12)
1.19
(0.67,2.12)

1.09
(0.64,1.86)
1.15
(0.79,1.67)
0.86
(0.45,1.64)
0.88
(0.48,1.64)
0.64
(0.28,1.50)
0.57
(0.02,15.35)
1.48
(0.93,2.38)
1.87**
(1.24,2.82)
0.75
(0.35,1.63)
1.26
(0.73,2.18)
1.37
(0.53,3.54)
0.83
(0.34,2.02)
0.36
(0.10,1.22)
3.34
(0.06,178.39)
0.80
(0.44,1.48)

* Significantly different from 1 at the 0.05 level, but not at the 0.01 level.
** Significantly different from 1 at the 0.01 level.
                                                       K-17

-------
Table K-3. Results of Statistical Analyses to Investigate the Significance of Environment,
          Urbanicity, and Income Status on Analyte Levels in Selected NC Multimedia
          Samples(a)
Medium
Significance Levels Associated with ...
Test for
Significant
Urbanicity
Effect
Test for
Significant
Income
Status Effect
Test for
Significant
Environ-
ment Effect
Test for
Significant
Difference
Between
Home and
Day Care
Environ-
ments
Results of Comparisons Between(b) ...
Home
Environ-
ment (for
Home
Children)
and Day
Care
Environ-
ment (for
Day Care
Children)
Home
Environ-
ment (for
Home
Children)
and Home
Environ-
ment (for
Day Care
Children)
Home
Environ-
ment (for
Day Care
Children)
and Day
Care
Environ-
ment
Benz [a] anthracene
Outdoor Air
Soil
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface Wipes
Transferable Residues
0.032*
0.573
0.770
0.469
0.374
0.085
0.754
0.009**
0.005**
0.101
0.807
0.412
0.121
0.448
0.129
0.001**
0.042*
0.380



0.001**





0.001**





0.995
0.042*




0.001**


Benzo [6] fluoranthene
Indoor Air
Outdoor Air
Soil
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface Wipes
Transferable Residues
0.110
0.126
0.637
0.746
0.467
0.528
0.775
0.001**
0.470
0.015*
0.009**
0.080
0.455
0.622
0.816
0.226
0.543
0.110
0.001**
0.010*
0.652




0.001**






0.001**






0.853
0.010*





0.001**


Benzo [k] fluoranthene
Outdoor Air
Soil
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface Wipes
Transferable Residues
0.133
0.546
0.602
0.380
0.345
0.578
0.274
0.018*
0.008**
0.085
0.372
0.456
0.023*
0.416
0.178
0.001**
0.077
0.557
0.081


0.001**


0.054


0.001**


0.085


0.958


0.566


0.001**


Benzo \ghi\ perylene
Indoor Air
Outdoor Air
Soil
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface Wipes
Transferable Residues
0.153
0.164
0.700
0.980
0.616
0.316
0.764
<0.001**
0.052
0.008**
0.005**
0.076
0.416
0.467
0.303
0.042*
0.547
0.146
0.001**
0.045*
0.653

0.227


0.001**



0.160


0.001**



0.070


1.000
0.045*


0.883


0.001**


                                        K-18

-------
Table K-3. (cont.)
Medium
Significance Levels Associated with ...
Test for
Significant
Urbanicity
Effect
Test for
Significant
Income
Status Effect
Test for
Significant
Environ-
ment Effect
Test for
Significant
Difference
Between
Home and
Day Care
Environ-
ments
Results of Comparisons Between(b) ...
Home
Environ-
ment (for
Home
Children)
and Day
Care
Environ-
ment (for
Day Care
Children)
Home
Environ-
ment (for
Home
Children)
and Home
Environ-
ment (for
Day Care
Children)
Home
Environ-
ment (for
Day Care
Children)
and Day
Care
Environ-
ment
Benzo [a] pyrene
Indoor Air
Outdoor Air
Soil
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface Wipes
Transferable Residues
0.454
0.043*
0.697
0.805
0.760
0.461
0.824
<0.001**
0.417
0.020*
0.005**
0.088
0.790
0.399
0.340
0.051
0.477
0.198
<0.001**
0.055
0.480




0.001**






0.001**






0.994






0.001**


Benzo [e] pyrene
Outdoor Air
Soil
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface Wipes
Transferable Residues
0.217
0.755
0.820
0.515
0.363
0.829
0.198
0.008**
0.013*
0.051
0.486
0.431
0.026*
0.558
0.151
0.001**
0.072
0.443
0.117


0.001**


0.078


0.001**


0.072


0.984


0.690


0.001**


Benzylbutylphthalate
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface Wipes
Food Preparation Surface
Wipes
Transferable Residues
0.349
0.164
0.181
0.726
0.307
0.003**
<0.001**
0.522
0.404
0.165
0.001**
0.001**
0.595
0.551
0.409
0.001**
0.001**



0.001**
0.001**



0.960
0.999



0.001**
0.001**



Bisphenol-A
Indoor Air
Hard Floor Surface Wipes
Food Preparation Surface
Wipes
Transferable Residues
Solid Food (Children)
Liquid Food (Children)
0.653
0.721
0.562
0.851
0.892
0.942
0.084
0.880
0.890
0.440
0.510
0.885
0.052
0.023*
0.655
0.770
0.447
0.131













0.023*










«§>/ia-Chlordane
Indoor Air
Outdoor Air
Dust (ng/g)
0.282
0.373
0.451
0.117
0.105
0.226
0.785
0.027*
0.081

0.009**


0.021*


0.830


0.054

       K-19

-------
Table K-3. (cont.)
Medium
Dust (ng/m2)
Hard Floor Surface Wipes
Food Preparation Surface
Wipes
Significance Levels Associated with ...
Test for
Significant
Urbanicity
Effect
0.345
0.655
0.449
Test for
Significant
Income
Status Effect
0.041*
0.604
0.200
Test for
Significant
Environ-
ment Effect
0.001**
0.908
0.410
Test for
Significant
Difference
Between
Home and
Day Care
Environ-
ments
0.001**


Results of Comparisons Between(b) ...
Home
Environ-
ment (for
Home
Children)
and Day
Care
Environ-
ment (for
Day Care
Children)
0.001**


Home
Environ-
ment (for
Home
Children)
and Home
Environ-
ment (for
Day Care
Children)
0.655


Home
Environ-
ment (for
Day Care
Children)
and Day
Care
Environ-
ment
0.001**


ga»i»ja-Chlordane
Indoor Air
Outdoor Air
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface Wipes
Food Preparation Surface
Wipes
0.328
0.497
0.444
0.323
0.568
0.370
0.110
0.030*
0.251
0.053
0.306
0.160
0.849
0.028*
0.073
0.001**
0.898
0.343

0.010*

0.001**



0.021*

0.001**



0.753

0.695



0.065

0.001**


Chlorpyrifos
Indoor Air
Outdoor Air
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface Wipes
Food Preparation Surface
Wipes
Transferable Residues
Solid Food (Children)
0.848
0.288
0.384
0.289
0.745
0.875
0.700
0.516
0.213
0.048*
0.805
0.003**
0.859
0.110
0.469
0.147
0.196
0.017*
0.828
0.074
0.603
0.901
0.738
0.416

0.310







0.990







0.020*







0.174






Chrysene
Indoor Air
Outdoor Air
Soil
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface Wipes
Food Preparation Surface
Wipes
Transferable Residues
0.139
0.053
0.684
0.877
0.552
0.351
0.981
0.794
0.001**
0.572
0.009**
0.018*
0.063
0.326
0.334
0.700
0.154
0.369
0.463
0.149
0.001**
0.218
0.567
0.986




0.001**







0.001**







0.906







0.001**



Cyfluthrin
Transferable Residues
0.899
0.603
0.521




Diazinon
       K-20

-------
Table K-3. (cont.)
Medium
Indoor Air
Outdoor Air
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface Wipes
Food Preparation Surface
Wipes
Transferable Residues
Significance Levels Associated with ...
Test for
Significant
Urbanicity
Effect
0.901
0.580
0.698
0.460
0.735
0.965
0.881
Test for
Significant
Income
Status Effect
0.001**
0.613
0.017*
<0.001**
0.971
0.566
0.256
Test for
Significant
Environ-
ment Effect
0.734
0.568
0.051
0.001**
0.269
0.892
0.641
Test for
Significant
Difference
Between
Home and
Day Care
Environ-
ments



0.001**



Results of Comparisons Between(b) ...
Home
Environ-
ment (for
Home
Children)
and Day
Care
Environ-
ment (for
Day Care
Children)



0.004**



Home
Environ-
ment (for
Home
Children)
and Home
Environ-
ment (for
Day Care
Children)



0.405



Home
Environ-
ment (for
Day Care
Children)
and Day
Care
Environ-
ment



0.001**



Dibenzo [a,h] anthracene
Soil
Dust (ng/g)
Dust (ng/m2)
0.381
0.394
0.267
0.066
0.009**
0.083
0.430
0.128
0.001**


0.001**


0.001**


1.000


0.001**
Di-n-butylphthalate
Indoor Air
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface Wipes
Food Preparation Surface
Wipes
Transferable Residues
0.624
0.381
0.803
0.194
0.494
0.259
0.744
0.519
0.001**
0.730
0.428
0.431
0.001**
0.001**
0.001**
0.180
0.805
0.293
0.002**
0.001**
0.001**



0.001**
0.006**
0.001**



0.017*
0.617
0.922



0.084
0.001**
0.001**



/>,/>'-DDE
Solid Food (Children)
0.655
0.352
0.543




2,4-D (2,4-dichlorophenoxyacetic acid)
Dust (ng/g)
Dust (ng/m2)
Solid Food (Children)
Solid Food (Adults)
0.002**
0.023*
0.024*
0.224
0.001**
0.181
0.493
0.366
0.004**
0.004**
0.340
0.817
0.182
0.063


0.059
0.677


0.007**
0.011*


0.964
0.022*


Heptachlor
Indoor Air
Outdoor Air
0.642
0.975
0.333
0.424
0.793
0.403








Indeno [1,2,3-crf] py rene
Indoor Air
Outdoor Air
Soil
0.300
0.267
0.694
0.001**
0.144
0.007**
0.263
0.040*
0.473

0.152


0.111


0.092


0.748

       K-21

-------
Table K-3. (cont.)
Medium
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface Wipes
Transferable Residues
Significance Levels Associated with ...
Test for
Significant
Urbanicity
Effect
0.663
0.862
0.420
0.846
Test for
Significant
Income
Status Effect
0.009**
0.058
0.528
0.411
Test for
Significant
Environ-
ment Effect
0.154
<0.001**
0.037*
0.445
Test for
Significant
Difference
Between
Home and
Day Care
Environ-
ments

0.001**


Results of Comparisons Between(b) ...
Home
Environ-
ment (for
Home
Children)
and Day
Care
Environ-
ment (for
Day Care
Children)

0.001**


Home
Environ-
ment (for
Home
Children)
and Home
Environ-
ment (for
Day Care
Children)

0.931
0.037*

Home
Environ-
ment (for
Day Care
Children)
and Day
Care
Environ-
ment

0.001**


Pentachlorophenol
Indoor Air
Outdoor Air
Dust (ng/g)
Dust (ng/m2)
0.324
0.097
0.759
0.538
0.011*
0.041*
0.569
0.011*
0.578
0.190
0.224
0.022*



0.014*



0.126



0.374



0.018*
cis-Permethrin
Indoor Air
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface Wipes
Food Preparation Surface
Wipes
Transferable Residues
0.998
0.807
0.843
0.374
0.909
0.239
0.001**
0.805
0.004**
0.707
0.115
0.856
0.270
0.826
0.024*
0.606
0.726
0.426


0.007**





0.036*





0.896





0.019*



fra«$-Permethrin
Indoor Air
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface Wipes
Food Preparation Surface
Wipes
Transferable Residues
0.909
0.923
0.774
0.405
0.936
0.286
<0.001**
0.917
0.011*
0.718
0.131
0.831
0.356
0.667
0.019*
0.511
0.677
0.422


0.006**





0.035*





0.826





0.015*



PCB52
Indoor Air
Outdoor Air
0.439
0.609
0.377
0.372
0.596
0.006**

0.167

0.071

0.011*

0.904
PCB95
Indoor Air
0.741
0.534
0.963




PCB 101
Indoor Air
0.329
0.897
0.455




3,5,6-TCP(3,5,6-trichloro-2-pyridinol)
Indoor Air
0.820
0.891
0.061




       K-22

-------
                                                Table K-3.  (cont.)



Medium
Outdoor Air
Soil
Dust (ng/g)
Dust (ng/m2)
Solid Food (Children)
Solid Food (Adults)
Significance Levels Associated with ...


Test for
Significant
Urbanicity
Effect
0.472
0.381
0.361
0.336
0.768
0.881


Test for
Significant
Income
Status Effect
0.015*
0.718
0.568
0.002**
0.001**
0.076


Test for
Significant
Environ-
ment Effect
0.075
0.045*
0.214
0.348
0.390
0.853


Test for
Significant
Difference
Between
Home and
Day Care
Environ-
ments

0.046*




Results of Comparisons Between(b) ...
Home
Environ-
ment (for
Home
Children)
and Day
Care
Environ-
ment (for
Day Care
Children)

0.313





Home
Environ-
ment (for
Home
Children)
and Home
Environ-
ment (for
Day Care
Children)

0.278






Home
Environ-
ment (for
Day Care
Children)
and Day
Care
Environ-
ment

0.049*




(a) For a given analyte, the media listed in this table represent those media for which statistical analysis was performed (i.e.,
having at least 50% detected results).
(b) In the last four columns of this table, significance levels are specified only when the environment effect was significant at the
0.05 level (column 4 of this table). These significance levels in these last three rows are adjusted based upon Tukey's
studentized range approach to controlling the overall Type I error rate (i.e., incorrectly declaring at least one pair of
environments significantly  different).

* Implies statistical significance at the 0.05 level, but not at the 0.01 level.
** Implies statistical significance at the 0.01 level.
                                                         K-23

-------
Table K-4. Results of Statistical Analyses to Investigate the Significance of Environment,
          Urbanicity, and Income Status on Analyte Levels in Selected OH Multimedia
          Samples(a)
Medium
Significance Levels Associated with ...
Test for
Significant
Urbanicity
Effect
Test for
Significant
Income
Status Effect
Test for
Significant
Environ-
ment Effect
Test for
Significant
Difference
Between
Home and
Day Care
Environ-
ments
Results of Comparisons Between(b) ...
Home
Environ-
ment (for
Home
Children)
and Day
Care
Environ-
ment (for
Day Care
Children)
Home
Environ-
ment (for
Home
Children)
and Home
Environ-
ment (for
Day Care
Children)
Home
Environ-
ment (for
Day Care
Children)
and Day
Care
Environ-
ment
Atrazine
Drinking Water (ng/mL)
0.629
0.639
0.253




Benz [a] anthracene
Soil
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface Wipes
Transferable Residues
0.790
0.001**
0.006**


0.161
0.029*
0.839
0.817
0.842
0.862
0.009**
0.001**
0.157
0.592

0.016*
0.001**



0.009**
0.001**



0.177
0.041*



0.239
0.005**


Benzo [6] fluoranthene
Soil
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface Wipes
Transferable Residues
0.721
0.001**
0.009**


0.195
0.019*
0.788
0.730
0.548
0.917
0.009**
0.001**
0.411
0.421

0.009**
0.001**



0.007**
0.001**



0.300
0.071



0.139
0.002**


Benzo [k] fluoranthene
Soil
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface Wipes
Transferable Residues
0.713
0.001**
0.013*


0.069
0.024*
0.824
0.995
0.617
0.829
0.010*
0.001**
0.330
0.568

0.008**
0.001**



0.007**
0.001**



0.379
0.082



0.112
0.001**


Benzo \ghi\ perylene
Soil
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface Wipes
Transferable Residues
0.717
0.001**
0.018*


0.106
0.016*
0.753
0.924
0.165
0.951
0.008**
0.001**
0.264
0.231

0.007**
0.001**



0.006**
0.001**



0.324
0.079



0.112
0.002**


Benzo [a] pyrene
Soil
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface Wipes
0.686
0.001**
0.011*

0.166
0.017*
0.705
0.914
0.881
0.023*
0.001**
0.231

0.029*
0.001**


0.023*
0.001**


0.265
0.058


0.302
0.006**

                                        K-24

-------
Table K-4. (cont.)
Medium
Transferable Residues
Significance Levels Associated with ...
Test for
Significant
Urbanicity
Effect

Test for
Significant
Income
Status Effect
0.647
Test for
Significant
Environ-
ment Effect
0.769
Test for
Significant
Difference
Between
Home and
Day Care
Environ-
ments

Results of Comparisons Between(b) ...
Home
Environ-
ment (for
Home
Children)
and Day
Care
Environ-
ment (for
Day Care
Children)

Home
Environ-
ment (for
Home
Children)
and Home
Environ-
ment (for
Day Care
Children)

Home
Environ-
ment (for
Day Care
Children)
and Day
Care
Environ-
ment

Benzo[e]pyrene
Soil
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface Wipes
Transferable Residues
0.721
<0.001**
0.014*


0.125
0.017*
0.778
0.937
0.874
0.938
0.011*
0.001**
0.344
0.551

0.010*
0.001**



0.009**
0.001**



0.331
0.078



0.142
0.002**


Benzylbutylphthalate
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface Wipes
Food Preparation Surface
Wipes
Transferable Residues
Solid Food (Children)
0.284
0.167



0.226
0.062
0.003**
0.177
0.533
0.762
0.349
0.006**
0.001**
0.059
0.148
0.099
0.290
0.002**
0.001**




0.004**
0.001**




0.761
0.209




0.024*
0.001**




Bisphenol-A
Indoor Air
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface Wipes
Food Preparation Surface
Wipes
Transferable Residues
Solid Food (Children)
Liquid Food (Children)
0.903
0.356
0.610



0.555
0.448
0.107
0.407
0.081
0.141
0.763
0.128
0.294
0.859
0.019*
0.106
0.001**
0.126
0.174
0.543
0.723
0.533
0.267

0.001**





0.996

0.001**





0.021*

0.904





0.128

0.003**





«§>/ia-Chlordane
Indoor Air
Outdoor Air
Soil
Dust (ng/g)
Dust (ng/m2)
0.772
0.216
0.897
0.364
0.847
0.255
0.754
0.049*
0.415
0.061
0.128
0.064
0.083
0.462
0.185




















ga»i»ja-Chlordane
Indoor Air
Outdoor Air
0.830
0.214
0.315
0.847
0.158
0.066








       K-25

-------
Table K-4. (cont.)
Medium
Soil
Dust (ng/g)
Dust (ng/m2)
Significance Levels Associated with ...
Test for
Significant
Urbanicity
Effect
0.906
0.494
0.960
Test for
Significant
Income
Status Effect
0.062
0.359
0.053
Test for
Significant
Environ-
ment Effect
0.115
0.493
0.157
Test for
Significant
Difference
Between
Home and
Day Care
Environ-
ments



Results of Comparisons Between(b) ...
Home
Environ-
ment (for
Home
Children)
and Day
Care
Environ-
ment (for
Day Care
Children)



Home
Environ-
ment (for
Home
Children)
and Home
Environ-
ment (for
Day Care
Children)



Home
Environ-
ment (for
Day Care
Children)
and Day
Care
Environ-
ment



Chlorpyrifos
Indoor Air
Outdoor Air
Dust (ng/g)
Dust (ng/m2)
Food Preparation Surface
Wipes
Transferable Residues
Solid Food (Children)
0.179
0.099
0.316
0.695


0.361
0.065
0.896
0.018*
0.002**
0.281
0.123
0.001**
0.724
0.086
0.054
0.001**
0.613
0.319
0.348



0.001**






0.001**






0.542






0.004**



Chrysene
Soil
Dust (ng/g)
Dust (ng/m2)
Transferable Residues
0.889
0.001**
0.008**

0.198
0.018*
0.748
0.855
0.852
0.010*
0.001**
0.594

0.010*
0.001**


0.008**
0.001**


0.323
0.076


0.142
0.002**

Cyfluthrin
Dust (ng/g)
Dust (ng/m2)
0.021*
0.182
0.320
0.047*
0.202
0.012*

0.003**

0.013*

0.999

0.017*
Diazinon
Indoor Air
Outdoor Air
Dust (ng/g)
Dust (ng/m2)
Transferable Residues
0.921
0.001**
0.239
0.478

0.107
0.012*
0.378
0.038*
0.202
0.468
0.107
0.193
0.001**
0.469



0.001**




0.001**




0.255




0.025*

Dibenzo [a,h] anthracene
Soil
Dust (ng/g)
Dust (ng/m2)
0.704
0.001**
0.010*
0.076
0.025*
0.847
0.946
0.005**
0.001**

0.006**
0.001**

0.004**
0.001**

0.257
0.066

0.115
0.002**
Di-n-butylphthalate
Indoor Air
Soil
Dust (ng/g)
0.215
0.405
0.059
0.927
0.733
0.565
0.029*
0.001**
0.001**
0.008**
0.300
0.001**
0.029*
0.055
0.001**
0.998
0.001**
0.664
0.043*
0.943
0.001**
       K-26

-------
Table K-4. (cont.)
Medium
Dust (ng/m2)
Hard Floor Surface Wipes
Food Preparation Surface
Wipes
Transferable Residues
Significance Levels Associated with ...
Test for
Significant
Urbanicity
Effect
0.669



Test for
Significant
Income
Status Effect
0.033*
0.648
0.275
0.318
Test for
Significant
Environ-
ment Effect
0.001**
0.184
0.328
0.688
Test for
Significant
Difference
Between
Home and
Day Care
Environ-
ments
0.001**



Results of Comparisons Between(b) ...
Home
Environ-
ment (for
Home
Children)
and Day
Care
Environ-
ment (for
Day Care
Children)
0.001**



Home
Environ-
ment (for
Home
Children)
and Home
Environ-
ment (for
Day Care
Children)
0.736



Home
Environ-
ment (for
Day Care
Children)
and Day
Care
Environ-
ment
0.001**



/>,/>'-DDE
Solid Food (Children)
0.400
0.722
0.085




2,4-D (2,4-dichlorophenoxyacetic acid)
Dust (ng/g)
Dust (ng/m2)
0.042*
0.247
0.001**
0.011*
0.980
0.069








Indeno [1,2,3-crf] py rene
Soil
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface Wipes
Transferable Residues
0.788
0.001**
0.015*


0.148
0.021*
0.772
0.861
0.149
0.941
0.008**
0.001**
0.309
0.444

0.007**
0.001**



0.006**
0.001**



0.360
0.089



0.104
0.002**


IMP (2-isopropyl-6-methyl-4-pyrimidinol)
Indoor Air
Outdoor Air
Dust (ng/g)
Dust (ng/m2)
Solid Food (Children)
Solid Food (Adults)
0.469
0.001**
0.835
0.522
0.146
0.724
0.025*
0.002**
0.585
0.063
0.401
0.085
0.923
0.466
0.430
0.012*
0.352
0.620



0.045*





0.022*





0.094





0.499


cis-Permethrin
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface Wipes
Transferable Residues
0.209
0.185


0.276
0.044*
0.315
0.302
0.248
0.004**
0.456
0.472

0.002**



0.002**



0.540



0.034*


fra«$-Permethrin
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface Wipes
Transferable Residues
0.322
0.216


0.279
0.051
0.290
0.288
0.347
0.005**
0.458
0.351

0.002**



0.003**



0.602



0.033*


       K-27

-------
                                                Table K-4. (cont.)
Medium
Significance Levels Associated with ...
Test for
Significant
Urbanicity
Effect
Test for
Significant
Income
Status Effect
Test for
Significant
Environ-
ment Effect
Test for
Significant
Difference
Between
Home and
Day Care
Environ-
ments
Results of Comparisons Between(b) ...
Home
Environ-
ment (for
Home
Children)
and Day
Care
Environ-
ment (for
Day Care
Children)
Home
Environ-
ment (for
Home
Children)
and Home
Environ-
ment (for
Day Care
Children)
Home
Environ-
ment (for
Day Care
Children)
and Day
Care
Environ-
ment
Pentachlorophenol
Indoor Air
Outdoor Air
Dust (ng/g)
Dust (ng/m2)
0.193
0.222
0.695
0.414
0.808
0.193
0.627
0.100
0.009**
0.242
0.801
0.137
0.048*



0.019*



0.062



0.555



PCB52
Indoor Air
Outdoor Air
Dust (ng/g)
Dust (ng/m2)
Transferable Residues
0.370
0.344
0.930
0.640

0.661
0.384
0.940
0.099
0.323
0.304
0.761
0.235
<0.001**
0.732



0.001**




0.001**




0.904




0.002**

PCB95
Indoor Air
0.565
0.680
0.907




PCB 101
Indoor Air
0.241
0.289
0.398




3,5,6-TCP(3,5,6-trichloro-2-pyridinol)
Indoor Air
Outdoor Air
Soil
Dust (ng/g)
Dust (ng/m2)
Hard Floor Surface Wipes
Solid Food (Children)
Solid Food (Adults)
0.424
0.375
0.008**
0.084
0.418
0.564
0.844
0.680
0.016*
0.510
0.693
0.156
0.019*
0.291
0.448
0.660
0.686
0.226
0.711
0.677
0.014*
0.664
0.141
0.003**




0.010*







0.010*







0.436


0.003**




0.119



(a) For a given analyte, the media listed in this table represent those media for which statistical analysis was performed (i.e.,
having at least 50% detected results).  In columns 2 through 4 of this table, cells are blank when insufficient data are available
for the given pollutant and sample medium to allow the statistical test specified in the column heading to be performed.
(b) In the last four columns of this table, significance levels are specified only when the environment effect was significant at the
0.05 level (column 4 of this table).  These significance levels in these last three rows are adjusted based upon Tukey's
studentized range approach to controlling the overall Type I error rate (i.e., incorrectly declaring at least one pair of
environments significantly different).

* Implies statistical significance at the 0.05 level, but not at the 0.01 level.
** Implies statistical significance at the 0.01  level.
                                                         K-28

-------
Table K-5. Estimated Ratio Between Selected Strata of Geometric Mean Pollutant Levels
           in NC Dermal Wipe Samples, and 95% Confidence Intervals on This Ratio, for
           Pollutants Detected in At Least 50% of Samples
Type of
Dermal
Wipe
Sample
Estimated Ratio of Geometric Means (95% CI)
Urban vs. Rural
Low Income vs.
Mid/High
Income
Home vs.
Day Care
Environments
Home
Environment
(for Home
Children) vs.
Day Care
Environment
Home
Environment
(for Home
Children)
vs. Home
Environment
(for Day Care
Children)
Home
Environment
(for Day Care
Children)
vs. Day Care
Environment
alpha-CUordane
Children
Adults
0.69(0.42,1.13)
0.73(0.39,1.37)
1.08(0.73,1.60)
0.94(0.57,1.54)
1.14(0.83,1.59)

1.02(0.61,1.71)

0.80(0.48,1.33)
0.87(0.52,1.45)
1.28(0.84,1.96)

ga»i»i«-Chlordane
Children
Adults
0.68(0.36,1.28)
0.80(0.39,1.63)
1.22(0.75,1.99)
1.00(0.57,1.74)
1.10(0.77,1.56)

0.98(0.52,1.83)

0.79(0.42,1.49)
0.90(0.50,1.59)
1.23(0.81,1.88)

Chlorpyrifos
Children
Adults
0.97(0.44,2.18)
1.47(0.66,3.26)
1.54(0.88,2.71)
1.91* (1.02,3. 57)
1.75* (1.12,2.72)

1.59(0.64,3.93)

0.83 (0.34,2.06)
0.87(0.46,1.66)
1.91** (1.27,2. 89)

Diazinon
Adults
1.26(0.57,2.78)
1.59(0.86,2.96)


0.81 (0.43,1.52)

3,5,6-TCP(3,5,6-trichloro-2-pyridinol)
Children
Adults
1.16(0.83,1.63)
0.73(0.50,1.07)
1.22(0.95,1.57)
1.47* (1.10,1. 98)
1.88** (1.43,2.47)

1.99** (1.40,2.84)

1.12(0.79,1.60)
0.83(0.61,1.13)
1.77** (1.20,2.60)

Benzylbutylphthalate
Children
Adults
0.78(0.42,1.45)
1.23(0.69,2.18)
1.64* (1.04,2. 58)
1.43(0.91,2.25)
1.41 (0.95,2.09)

1.32(0.67,2.58)

0.87(0.44,1.71)
1.47(0.92,2.34)
1.51(0.93,2.45)

Di-n-butylphthalate
Children
Adults
1.34(0.68,2.64)
2.44(1.00,5.98)
0.76(0.49,1.17)
0.91 (0.45,1.85)
0.83(0.49,1.38)

0.57(0.27,1.20)

0.48(0.23,1.00)
0.46* (0.22,0.95)
1.20(0.59,2.44)

Bisphenol-A
Children
Adults
0.94(0.46,1.91)
2.61** (1.29,5.28)
0.82(0.48,1.40)
0.85(0.49,1.49)
0.33** (0.19,0. 58)

0.39* (0.19,0.82)

1.40(0.66,2.97)
1.56(0.88,2.75)
0.28** (0.12,0.63)

cis-Permethrin
Children
Adults
0.58(0.21,1.63)
0.59(0.18,1.97)
2.00 (0.90,4.42)
1.47(0.57,3.78)
1.39(0.77,2.51)

0.91 (0.33,2.56)

0.43(0.15,1.23)
0.51 (0.20,1.36)
2.10* (1.01,4.40)

frans-Permethrin
Children
Adults
0.52(0.20,1.38)
0.45(0.13,1.47)
2.03 (0.95,4.35)
1.74(0.68,4.45)
1.45(0.83,2.54)

1.17(0.44,3.12)

0.65(0.24,1.74)
0.66(0.25,1.74)
1.80(0.93,3.49)

* Significantly different from 1 at the 0.05 level, but not at the 0.01 level.
** Significantly different from 1 at the 0.01 level.
                                          K-29

-------
Table K-6. Estimated Ratio Between Selected Strata of Geometric Mean Pollutant Levels
          in OH Dermal Wipe Samples, and 95% Confidence Intervals on This Ratio, for
          Pollutants Detected in At Least 50% of Samples
Type of
Dermal
Wipe
Sample
Estimated Ratio of Geometric Means (95% CI)
Urban vs. Rural
Low Income vs.
Mid/High Income
Home vs.
Day Care
Environments
Home
Environment
(for Home
Children) vs.
Day Care
Environment
Home
Environment
(for Home
Children)
vs. Home
Environment
(for Day Care
Children)
Home
Environment
(for Day Care
Children)
vs. Day Care
Environment
Benz [a] anthracene
Children
Adults
1.92(0.92,4.00)
1.45(0.91,2.32)
0.78(0.50,1.22)
0.83(0.59,1.17)
1.13(0.71,1.79)

0.97 (0.47,2.00)

0.73(0.35,1.52)
0.85(0.60,1.21)
1.32(0.72,2.40)

Benz o [b] fluor anthene
Children
Adults
2.33 (0.99,5.50)
1.69(0.87,3.27)
0.70(0.42,1.17)
0.70(0.43,1.15)
1.17(0.66,2.05)

1.08(0.46,2.51)

0.85(0.37,1.99)
1.02(0.62,1.70)
1.26(0.59,2.70)

Benz o [k] fluor anthene
Children
Adults
1.75(0.85,3.63)
1.39(0.82,2.36)
0.72(0.45,1.14)
0.85(0.58,1.26)
1.22(0.77,1.93)

1.00(0.49,2.06)

0.68(0.33,1.39)
1.00(0.67,1.50)
1.48(0.81,2.69)

Benzo \ghi\ perylene
Children
Adults
1.94(0.86,4.37)
1.60(0.95,2.70)
0.75(0.46,1.22)
0.70(0.48,1.04)
1.37(0.82,2.28)

1.10(0.49,2.47)

0.65(0.29,1.46)
0.97(0.65,1.44)
1.70(0.87,3.30)

Benzo[«]pyrene
Children
Adults
1.85(0.82,4.18)
1.47(0.86,2.53)
0.65(0.40,1.07)
0.81(0.54,1.21)
1.10(0.66,1.83)

0.94(0.42,2.12)

0.74(0.33,1.66)
0.99(0.65,1.49)
1.28(0.66,2.47)

Benzo [ejpyrene
Children
Adults
1.90(0.87,4.13)
1.56(0.88,2.78)
0.82(0.52,1.30)
0.83(0.55,1.28)
1.30(0.81,2.09)

1.19(0.55,2.58)

0.84(0.39,1.82)
1.17(0.75,1.81)
1.42(0.77,2.61)

Bisphenol-A
Children
Adults
1.11 (0.54,2.28)
1.40(0.72,2.75)
1.13(0.67,1.88)
1.31(0.80,2.16)
2.90** (1.74,4. 85)

3. 15** (1.57,6. 34)

1.18(0.59,2.37)
1.04(0.62,1.75)
2.67** (1.30,5.49)

Chlorpyrifos
Children
Adults
1.03(0.40,2.63)
1.79(0.72,4.48)
2. 53** (1.29,4.96)
4.08** (2.07,8.04)
1.29(0.73,2.27)

1.18(0.49,2.85)

0.84 (0.35,2.02)
0.82(0.41,1.65)
1.41(0.68,2.95)

Chrysene
Children
Adults
1.69(0.75,3.79)
1.81* (1.05,3. 12)
0.71(0.43,1.16)
0.79(0.53,1.19)
1.10(0.67,1.83)

0.89(0.40,1.98)

0.65(0.29,1.45)
0.87(0.57,1.32)
1.36(0.71,2.63)

2,4-D (2,4-dichlorophenoxyacetic acid)
Adults
1.63(0.94,2.80)
1.31(0.87,1.97)


2.25** (1.49,3. 39)

Indeno[l,2,3-crf]pyrene
Children
Adults
2.00 (0.88,4.53)
1.51 (0.88,2.60)
0.78(0.48,1.26)
0.75(0.50,1.12)
1.24(0.75,2.06)

1.02(0.45,2.30)

0.68(0.30,1.53)
0.87(0.57,1.32)
1.50(0.78,2.89)

Pentachlorophenol
Adults
0.88(0.50,1.55)
1.25(0.81,1.90)


0.80(0.52,1.22)

                                       K-30

-------
                                              Table K-6.  (cont.)
Type of
Dermal
Wipe
Sample
Estimated Ratio of Geometric Means (95% CI)
Urban vs. Rural
Low Income vs.
Mid/High Income
Home vs.
Day Care
Environments
Home
Environment
(for Home
Children) vs.
Day Care
Environment
Home
Environment
(for Home
Children)
vs. Home
Environment
(for Day Care
Children)
Home
Environment
(for Day Care
Children)
vs. Day Care
Environment
cis-Permethrin
Children
Adults
0.60(0.20,1.78)
0.36(0.12,1.11)
1.45(0.68,3.08)
1.30(0.57,2.96)
1.11 (0.63,1.97)

0.92 (0.32,2.69)

0.69(0.24,2.01)
0.58(0.25,1.37)
1.34(0.72,2.50)

frans-Permethrin
Children
Adults
0.51 (0.17,1.52)
0.39(0.13,1.19)
1.26(0.59,2.70)
1.33(0.59,2.99)
1.11 (0.63,1.93)

0.81 (0.28,2.36)

0.54(0.18,1.56)
0.57(0.24,1.31)
1.51(0.84,2.72)

3,5,6-TCP(3,5,6-trichloro-2-pyridinol)
Children
Adults
0.86(0.56,1.31)
1.12(0.72,1.75)
1.28(0.93,1.75)
1.28(0.91,1.79)
1.25(0.95,1.65)

1.45(0.97,2.18)

1.35(0.90,2.02)
1.11(0.80,1.56)
1.08(0.74,1.56)

* Significantly different from 1 at the 0.05 level, but not at the 0.01 level.
** Significantly different from 1 at the 0.01 level.
                                                       K-31

-------
Table K-7. Results of Statistical Analyses to Investigate the Significance of Environment,
              Urbanicity, and Income Status on NC Dermal Wipe Loading Data(a)
Type of
Dermal
Wipe
Sample
Significance Levels Associated with ...
Test for
Significant
Urbanicity
Effect
Test for
Significant
Income Status
Effect
Test for
Significant
Environment
Effect
Test for
Significant
Difference
Between
Home and
Day Care
Environments
Results of Comparisons Between^' ...
Home
Environment
(for Home
Children) and
Day Care
Environment
(for Day Care
Children)
Home
Environment
(for Home
Children) and
Home
Environment
(for Day Care
Children)
Home
Environment
(for Day Care
Children) and
Day Care
Environment
Benzylbutylphthalate
Children
Adults
0.424
0.487
0.032*
0.121
0.127
0.107








Bisphenol-A
Children
Adults
0.862
0.008**
0.459
0.574
0.001**
0.127
O.001**

0.010*

0.519

0.001**

alpha-CUordane
Children
Adults
0.136
0.325
0.686
0.792
0.334
0.595








ga»i»i«-Chlordane
Children
Adults
0.226
0.534
0.419
0.992
0.437
0.703








Chlorpyrifos
Children
Adults
0.948
0.344
0.130
0.044*
0.002**
0.674
0.014*

0.434

0.877

0.001**

Diazinon
Adults
0.559
0.139
0.502




Di-n-butylphthalate
Children
Adults
0.384
0.051
0.207
0.803
0.057
0.036*





0.036*


cis-Permethrin
Children
Adults
0.289
0.392
0.087
0.417
0.038*
0.177
0.274

0.975

0.135

0.047*

frans-Permethrin
Children
Adults
0.187
0.183
0.069
0.246
0.105
0.399








3,5,6-TCP(3,5,6-trichloro-2-pyridinol)
Children
Adults
0.368
0.108
0.115
0.010*
O.001**
0.230
O.001**

O.001**

0.705

0.002**

(a) For a given analyte, the media listed in this table represent those media for which statistical analysis was performed (i.e.,
having at least 50% detected results).
(b) In the last four columns of this table, significance levels are specified only when the environment effect was significant at the
0.05 level (column 4 of this table). These significance levels in these last three rows are adjusted based upon Tukey's
studentized range approach to controlling the overall Type I error rate (i.e., incorrectly declaring at least one pair of
environments significantly different).
* Implies statistical significance at the 0.05 level, but not at the 0.01 level.
** Implies statistical significance at the 0.01 level.
                                                    K-32

-------
Table K-8. Results of Statistical Analyses to Investigate the Significance of Environment,
          Urbanicity, and Income Status on OH Dermal Wipe Loading Data(a)
Type of
Dermal
Wipe
Sample
Significance Levels Associated with ...
Test for
Significant
Urbanicity
Effect
Test for
Significant
Income Status
Effect
Test for
Significant
Environment
Effect
Test for
Significant
Difference
Between
Home and
Day Care
Environments
Results of Comparisons Between^' ...
Home
Environment
(for Home
Children) and
Day Care
Environment
(for Day Care
Children)
Home
Environment
(for Home
Children) and
Home
Environment
(for Day Care
Children)
Home
Environment
(for Day Care
Children) and
Day Care
Environment
Benz [a] anthracene
Children
Adults
0.082
0.115
0.275
0.275
0.455
0.370








Benzo[6]fluoranthene
Children
Adults
0.053
0.121
0.166
0.158
0.755
0.930








Benzo[&]fluoranthene
Children
Adults
0.129
0.217
0.152
0.422
0.237
0.993








Benz o [ghi] pery lene
Children
Adults
0.108
0.076
0.231
0.075
0.153
0.875








Benzo[«]pyrene
Children
Adults
0.139
0.160
0.089
0.292
0.565
0.948








Benzo[e]pyrene
Children
Adults
0.104
0.128
0.388
0.401
0.396
0.490








Bisphenol-A
Children
Adults
0.774
0.319
0.644
0.279
O.001**
0.867
O.001**

0.001**

0.836

0.005**

Chlorpyrifos
Children
Adults
0.948
0.210
0.008**
O.001**
0.539
0.577








Chrysene
Children
Adults
0.199
0.033*
0.169
0.254
0.360
0.508








2,4-D (2,4-dichlorophenoxyacetic acid)
Adults
0.079
0.199
O.001**


O.001**

Indeno [l,2,3-crf|pyrene
Children
Adults
0.095
0.135
0.298
0.159
0.283
0.503








Pentachlorophenol
Adults
0.663
0.308
0.295




                                       K-33

-------
                                                Table K-8.  (cont.)
Type of
Dermal
Wipe
Sample
Significance Levels Associated with ...
Test for
Significant
Urbanicity
Effect
Test for
Significant
Income Status
Effect
Test for
Significant
Environment
Effect
Test for
Significant
Difference
Between
Home and
Day Care
Environments
Results of Comparisons Between*6' ...
Home
Environment
(for Home
Children) and
Day Care
Environment
(for Day Care
Children)
Home
Environment
(for Home
Children) and
Home
Environment
(for Day Care
Children)
Home
Environment
(for Day Care
Children) and
Day Care
Environment
cis-Permethrin
Children
Adults
0.354
0.075
0.330
0.536
0.465
0.211








frans-Permethrin
Children
Adults
0.223
0.097
0.544
0.490
0.159
0.181








3,5,6-TCP(3,5,6-trichloro-2-pyridinol)
Children
Adults
0.469
0.617
0.125
0.150
0.083
0.527








(a) For a given analyte, the media listed in this table represent those media for which statistical analysis was performed (i.e.,
having at least 50% detected results).
(b) In the last four columns of this table, significance levels are specified only when the environment effect was significant at the
0.05 level (column 4 of this table). These significance levels in these last three rows are adjusted based upon Tukey's
studentized range approach to controlling the overall Type I error rate (i.e., incorrectly declaring at least one pair of
environments significantly  different).

* Implies statistical significance at the 0.05 level, but not at the 0.01 level.
** Implies statistical significance at the 0.01 level.
                                                         K-34

-------
                                    Appendix L
Descriptive Statistics of Potential Exposure Level and Potential Absorbed Dose Estimates
                  for Target Pollutants in Participating NC Children
                                        L-l

-------
L-2

-------
This appendix contains tables of descriptive statistics of potential exposure and potential absorbed dose
estimates (expressed in both ng and pmole units) in NC children for the following pollutants and
metabolites:
Pollutant/Metabolite
Benz[a]anthracene
Benzo[£>]fluoranthene
Benzo[/(]fluoranthene
Benzo[g/?/]perylene
Benzo[a]pyrene
Benzo[e]pyrene
Benzylbutylphthalate
Bisphenol-A
a/p/?a-Chlordane
gamma-Chlordane
Chlorpyrifos
Chrysene
Cyfluthrin
Diazinon
Dibenzo[a,/?]anthracene
Di-n-butylphthalate
p,p'-DDE
2,4-D (2,4-dichlorophenoxyacetic acid)
Heptachlor
lndeno[1 ,2,3-cd]pyrene
Pentachlorophenol
c/s-Permethrin
frans-Permethrin
PCS 52
PCB95
PCS 101
3,5,6-TCP (3,5,6-trichloro-2-pvridinol)
Table Numbers for
Potential Exposure
Summaries
Tables L-1 a, L-1b
Tables L-2a, L-2b
Tables L-3a, L-3b
Tables L-4a, L-4b
Tables L-5a, L-5b
Tables L-6a, L-6b
Tables L-7a, L-7b
Tables L-8a, L-8b
Tables L-9a, L-9b
Tables L-1 Oa, L-1 Ob
Tables L-1 1 a, L-11b
Tables L-1 2a, L-12b
Tables L-1 3a, L-13b
Tables L-1 4a, L-14b
Tables L-1 5a, L-15b
Tables L-16a, L-16b
Tables L-1 7a, L-17b
Tables L-1 8a, L-18b
Tables L-1 9a, L-19b
Tables L-20a, L-20b
Tables L-21 a, L-21b
Tables L-22a, L-22b
Tables L-23a, L-23b
Tables L-24a, L-24b
Tables L-25a, L-25b
Tables L-26a, L-26b
Tables L-27a, L-27b
Table Numbers for
Potential Absorbed
Dose Summaries
Tables L-1 c, L-1d
Tables L-2c, L-2d
Tables L-3c, L-3d
Tables L-4c, L-4d
Tables L-5c, L-5d
Tables L-6c, L-6d
Tables L-7c, L-7d
Tables L-8c, L-8d
Tables L-9c, L-9d
Tables L-1 Oc, L-10d
Tables L-1 1c, L-11d
Tables L-12c, L-12d
Tables L-1 3c, L-1 3d
Tables L-14c, L-14d
Tables L-1 5c, L-15d
Tables L-1 6c, L-16d
Tables L-1 7c, L-17d
Tables L-1 8c, L-18d
Tables L-1 9c, L-19d
Tables L-20c, L-20d
Tables L-21 c, L-21d
Tables L-22c, L-22d
Tables L-23c, L-24d
Tables L-24c, L-24d
Tables L-25c, L-25d
Tables L-26c, L-26d
Tables L-27c, L-27d
Descriptive statistics are presented separately for the following groups of NC child participants:
        All participants
        Participants from urban areas
        Participants from rural areas
        Participants from low-income areas
        Participants from middle/upper-income areas
        Stay-at-home children
        Day care children
                                                  L-3

-------
Table L-1a.     Benzralanthracene (56-55-3):  Estimates of Potential Exposure in NC Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54
81.5
82.5
76.2
83.6
80.0
69.2
94.9
41.4
39.3
52.4
44.8
37.9
37.9
45.2
100.0
100.0
100.0
100.0
100.0
100.0
100.0
1.58
1.68
1.10
1.59
1.54
1.83
1.31
-
-
51.4
-
-
-
-
19.8
18.1
27.4
11.9
27.6
13.2
27.4
2.58
2.73
1.59
1.84
3.07
3.30
1.38
-
-
38.1
-
-
-
-
45.8
42.6
58.9
20.6
59.9
26.2
60.4
0.973
1.02
0.777
1.07
0.892
1.01
0.934
-
-
41.3
-
-
-
-
6.85
6.90
6.64
5.90
8.20
5.60
8.63
0.843
0.870
0.667
0.803
0.853
0.918
0.758
-
-
0.667
-
-
-
-
1.26
1.21
1.52
1.14
1.36
1.17
1.33
Potential Exposure in NC Preschool Children (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54
81.5
82.5
76.2
83.6
80.0
69.2
94.9
41.4
39.3
52.4
44.8
37.9
37.9
45.2
100.0
100.0
100.0
100.0
100.0
100.0
100.0
6.93
7.36
4.80
6.95
6.74
8.00
5.74
-
-
225
-
-
-
-
86.6
79.2
120
52.0
121
57.7
120
11.3
12.0
6.95
8.04
13.4
14.5
6.04
-
-
167
-
-
-
-
201
187
258
90.0
262
115
265
4.26
4.46
3.40
4.69
3.91
4.43
4.09
-
-
181
-
-
-
-
30.0
30.2
29.1
25.9
35.9
24.5
37.8
0.843
0.870
0.667
0.803
0.853
0.918
0.758
-
-
0.667
-
-
-
-
1.26
1.21
1.52
1.14
1.36
1.17
1.33
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                    L-4

-------
Table L-1b.     Benzralanthracene (56-55-3): Range of Potential Exposure in NC Preschool
                Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54

-------
Table L-1c.     Benzralanthracene (56-55-3):  Estimates of Potential Absorbed Dose in NC
                 Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54
81.5
82.5
76.2
83.6
80.0
69.2
94.9
41.4
39.3
52.4
44.8
37.9
37.9
45.2
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.050
0.054
0.031
0.054
0.047
0.061
0.037
-
-
1.45
-
-
-
-
0.620
0.556
0.907
0.353
0.884
0.471
0.791
0.086
0.093
0.041
0.093
0.083
0.112
0.040
-
-
1.13
-
-
-
-
1.43
1.30
1.96
0.637
1.87
1.01
1.80
0.029
0.031
0.022
0.031
0.028
0.032
0.026
-
-
1.16
-
-
-
-
0.203
0.206
0.186
0.166
0.255
0.176
0.239
0.888
0.916
0.689
0.914
0.867
0.967
0.787
-
-
0.646
-
-
-
-
1.32
1.25
1.64
1.19
1.40
1.27
1.37
Potential Absorbed Dose in NC Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54
81.5
82.5
76.2
83.6
80.0
69.2
94.9
41.4
39.3
52.4
44.8
37.9
37.9
45.2
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.219
0.236
0.134
0.236
0.205
0.269
0.163
-
-
6.33
-
-
-
-
2.72
2.44
3.97
1.55
3.87
2.06
3.47
0.378
0.406
0.179
0.407
0.363
0.492
0.176
-
-
4.93
-
-
-
-
6.28
5.68
8.58
2.79
8.21
4.44
7.87
0.127
0.135
0.096
0.134
0.122
0.141
0.114
-
-
5.08
-
-
-
-
0.888
0.904
0.817
0.729
1.12
0.769
1.05
0.888
0.916
0.689
0.914
0.867
0.967
0.787
-
-
0.646
-
-
-
-
1.32
1.25
1.64
1.19
1.40
1.27
1.37
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      L-6

-------
Table L-1d.     Benzralanthracene (56-55-3): Range of Potential Absorbed Dose in NC Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54

-------
Table L-2a.     Benzorfrlfluoranthene (205-99-2):  Estimates of Potential Exposure in NC Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54
80.6
79.6
85.7
92.7
69.2
75.4
86.4
45.3
44.9
47.6
44.8
47.0
36.4
54.8
100.0
100.0
100.0
100.0
100.0
100.0
100.0
2.08
2.19
1.50
2.51
1.73
1.98
2.19
-
-
-
-
-
-
42.3
50.0
41.0
90.7
32.6
67.7
28.7
74.5
2.17
2.28
1.43
2.18
2.17
2.42
1.86
-
-
-
-
-
-
19.0
130
86.4
244
55.3
171
53.3
179
1.39
1.46
1.11
1.79
1.12
1.26
1.55
-
-
-
-
-
-
38.7
17.5
17.5
17.3
16.0
19.9
13.7
23.0
0.870
0.889
0.748
0.837
0.866
0.887
0.845
-
-
-
-
-
-
0.429
1.25
1.18
1.57
1.16
1.33
1.13
1.34
Potential Exposure in NC Preschool Children (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54
80.6
79.6
85.7
92.7
69.2
75.4
86.4
45.3
44.9
47.6
44.8
47.0
36.4
54.8
100.0
100.0
100.0
100.0
100.0
100.0
100.0
8.23
8.70
5.94
9.96
6.87
7.83
8.67
-
-
-
-
-
-
168
198
163
359
129
269
114
295
8.59
9.03
5.65
8.64
8.60
9.61
7.38
-
-
-
-
-
-
75.4
514
343
966
219
680
211
709
5.51
5.77
4.39
7.09
4.42
4.98
6.16
-
-
-
-
-
-
153
69.2
69.3
68.7
63.5
78.7
54.4
91.1
0.870
0.889
0.748
0.837
0.866
0.887
0.845
-
-
-
-
-
-
0.429
1.25
1.18
1.57
1.16
1.33
1.13
1.34
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.

-------
Table L-2b.     Benzorfrlfluoranthene (205-99-2):  Range of Potential Exposure in NC Preschool
                Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54

-------
Table L-2c.     Benzorfrlfluoranthene (205-99-2):  Estimates of Potential Absorbed Dose in NC
                 Preschool Children. Summarized  by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54
80.6
79.6
85.7
92.7
69.2
75.4
86.4
45.3
44.9
47.6
44.8
47.0
36.4
54.8
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.066
0.071
0.041
0.079
0.055
0.068
0.063
-
-
-
-
-
-
1.20
1.55
1.24
2.93
0.964
2.14
0.993
2.19
0.084
0.090
0.037
0.102
0.068
0.104
0.055
-
-
-
-
-
-
0.558
4.04
2.56
111
1.69
5.34
1.91
5.51
0.041
0.044
0.031
0.051
0.035
0.040
0.043
-
-
-
-
-
-
1.08
0.516
0.523
0.486
0.452
0.618
0.431
0.636
0.908
0.932
0.726
0.907
0.903
0.939
0.878
-
-
-
-
-
-
0.455
1.30
1.22
1.67
1.21
1.36
1.22
1.37
Potential Absorbed Dose in NC Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54
80.6
79.6
85.7
92.7
69.2
75.4
86.4
45.3
44.9
47.6
44.8
47.0
36.4
54.8
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.260
0.280
0.163
0.315
0.219
0.270
0.249
-
-
-
-
-
-
4.75
6.14
4.93
11.6
3.82
8.48
3.93
8.67
0.334
0.358
0.145
0.405
0.268
0.414
0.219
-
-
-
-
-
-
2.21
16.0
10.2
30.8
6.71
21.2
7.58
21.8
0.164
0.174
0.123
0.203
0.138
0.158
0.172
-
-
-
-
-
-
4.30
2.05
2.07
1.93
1.79
2.45
1.71
2.52
0.908
0.932
0.726
0.907
0.903
0.939
0.878
-
-
-
-
-
-
0.455
1.30
1.22
1.67
1.21
1.36
1.22
1.37
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected.  Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      L-10

-------
Table L-2d.     Benzorfrlfluoranthene (205-99-2):  Range of Potential Absorbed Dose in NC
                 Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54

-------
Table L-3a.     Benzorftlfluoranthene (207-08-9):  Estimates of Potential Exposure in NC Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54
67.7
68.0
66.7
72.7
61.5
60.0
76.3
21.9
20.6
28.6
31.0
13.6
19.7
24.2
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.825
0.842
0.741
0.962
0.703
0.819
0.831
-
-
-
-
-
-
-
17.3
14.6
29.2
11.4
23.2
11.0
24.4
0.601
0.624
0.476
0.725
0.463
0.699
0.476
-
-
-
-
-
-
-
40.7
30.8
69.7
19.6
53.0
21.2
54.5
0.707
0.717
0.660
0.809
0.622
0.680
0.739
-
-
-
-
-
-
-
6.10
6.05
6.33
5.40
7.07
4.98
7.70
0.502
0.515
0.438
0.536
0.449
0.530
0.471
-
-
-
-
-
-
-
1.26
1.20
1.53
1.20
1.31
1.15
1.34
Potential Exposure in NC Preschool Children (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54
67.7
68.0
66.7
72.7
61.5
60.0
76.3
21.9
20.6
28.6
31.0
13.6
19.7
24.2
100.0
100.0
100.0
100.0
100.0
100.0
100.0
3.27
3.34
2.94
3.81
2.79
3.25
3.30
-
-
-
-
-
-
-
68.4
57.9
116
45.0
92.0
43.5
96.9
2.38
2.47
1.89
2.87
1.83
2.77
1.89
-
-
-
-
-
-
-
161
122
276
77.8
210
84.2
216
2.80
2.84
2.62
3.21
2.47
2.69
2.93
-
-
-
-
-
-
-
24.2
24.0
25.1
21.4
28.0
19.7
30.5
0.502
0.515
0.438
0.536
0.449
0.530
0.471
-
-
-
-
-
-
-
1.26
1.20
1.53
1.20
1.31
1.15
1.34
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                   L-12

-------
Table L-3b.     Benzorftlfluoranthene (207-08-9): Range of Potential Exposure in NC Preschool
                Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54

-------
Table L-3c.     Benzorftlfluoranthene (207-08-9):  Estimates of Potential Absorbed Dose in NC
                 Preschool Children. Summarized  by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54
67.7
68.0
66.7
72.7
61.5
60.0
76.3
21.9
20.6
28.6
31.0
13.6
19.7
24.2
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.026
0.027
0.021
0.029
0.023
0.028
0.024
-
-
-
-
-
-
-
0.540
0.448
0.955
0.337
0.744
0.388
0.714
0.024
0.025
0.012
0.030
0.017
0.030
0.013
-
-
-
-
-
-
-
1.28
0.937
2.26
0.598
1.67
0.801
1.66
0.021
0.022
0.019
0.023
0.019
0.022
0.021
-
-
-
-
-
-
-
0.180
0.181
0.178
0.152
0.220
0.156
0.213
0.558
0.580
0.425
0.613
0.515
0.600
0.512
-
-
-
-
-
-
-
1.31
1.23
1.64
1.25
1.35
1.25
1.37
Potential Absorbed Dose in NC Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54
67.7
68.0
66.7
72.7
61.5
60.0
76.3
21.9
20.6
28.6
31.0
13.6
19.7
24.2
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.102
0.106
0.082
0.117
0.090
0.110
0.093
-
-
-
-
-
-
-
2.14
1.78
3.79
1.34
2.95
1.54
2.83
0.094
0.101
0.048
0.120
0.067
0.120
0.053
-
-
-
-
-
-
-
5.08
3.71
8.95
2.37
6.63
3.17
6.59
0.084
0.086
0.074
0.092
0.077
0.086
0.082
-
-
-
-
-
-
-
0.715
0.717
0.704
0.603
0.871
0.619
0.844
0.558
0.580
0.425
0.613
0.515
0.600
0.512
-
-
-
-
-
-
-
1.31
1.23
1.64
1.25
1.35
1.25
1.37
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected.  Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      L-14

-------
Table L-3d.     Benzorftlfluoranthene (207-08-9):  Range of Potential Absorbed Dose in NC
                 Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54

-------
Table L-4a.     Benzorq/i/lperylene (191-24-2):  Estimates of Potential Exposure in NC Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54
79.8
81.6
71.4
92.7
67.7
73.8
86.4
1.6
1.9
0.0
1.7
1.5
1.5
1.6
100.0
100.0
100.0
100.0
100.0
100.0
100.0
1.76
1.84
1.37
1.99
1.58
1.86
1.65
-
-
-
-
-
-
-
25.4
20.7
46.6
17.3
33.5
16.1
36.0
2.00
2.11
1.33
1.62
2.31
2.44
1.38
-
-
-
-
-
-
-
64.1
37.0
129
27.7
84.9
26.5
88.9
1.21
1.25
1.02
1.51
0.991
1.16
1.26
-
-
-
-
-
-
-
9.87
10.0
9.20
8.70
11.4
8.30
12.0
0.806
0.820
0.731
0.744
0.825
0.882
0.718
-
-
-
-
-
-
-
1.19
1.11
1.53
1.15
1.24
1.08
1.29
Potential Exposure in NC Preschool Children (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54
79.8
81.6
71.4
92.7
67.7
73.8
86.4
1.6
1.9
0.0
1.7
1.5
1.5
1.6
100.0
100.0
100.0
100.0
100.0
100.0
100.0
6.38
6.66
4.98
7.22
5.71
6.74
5.98
-
-
-
-
-
-
-
91.9
74.9
169
62.5
121
58.3
130
7.24
7.63
4.81
5.85
8.37
8.82
5.00
-
-
-
-
-
-
-
232
134
467
100
307
96.0
322
4.37
4.52
3.70
5.47
3.58
4.18
4.58
-
-
-
-
-
-
-
35.7
36.3
33.3
31.5
41.3
30.1
43.6
0.806
0.820
0.731
0.744
0.825
0.882
0.718
-
-
-
-
-
-
-
1.19
1.11
1.53
1.15
1.24
1.08
1.29
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                    L-16

-------
Table L-4b.     Benzorq/i/lperylene (191-24-2): Range of Potential Exposure in NC Preschool
                Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54

-------
Table L-4c.     Benzorq/i/lperylene (191-24-2):  Estimates of Potential Absorbed Dose in NC
                 Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54
79.8
81.6
71.4
92.7
67.7
73.8
86.4
1.6
1.9
0.0
1.7
1.5
1.5
1.6
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.056
0.060
0.037
0.061
0.053
0.064
0.047
-
-
-
-
-
-
-
0.793
0.636
1.50
0.516
1.07
0.559
1.06
0.074
0.079
0.034
0.064
0.083
0.095
0.037
-
-
-
-
-
-
-
2.02
1.12
4.10
0.848
2.67
0.962
2.76
0.036
0.038
0.029
0.043
0.031
0.037
0.035
-
-
-
-
-
-
-
0.292
0.300
0.258
0.245
0.355
0.260
0.333
0.854
0.879
0.696
0.788
0.905
0.941
0.754
-
-
-
-
-
-
-
1.25
1.16
1.64
1.21
1.28
1.18
1.32
Potential Absorbed Dose in NC Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54
79.8
81.6
71.4
92.7
67.7
73.8
86.4
1.6
1.9
0.0
1.7
1.5
1.5
1.6
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.202
0.216
0.136
0.219
0.192
0.233
0.169
-
-
-
-
-
-
-
2.87
2.30
5.44
1.87
3.87
2.02
3.84
0.267
0.286
0.123
0.233
0.300
0.344
0.136
-
-
-
-
-
-
-
7.29
4.06
14.8
3.07
9.66
3.48
9.98
0.130
0.136
0.104
0.157
0.112
0.133
0.128
-
-
-
-
-
-
-
1.06
1.09
0.935
0.887
1.28
0.942
1.21
0.854
0.879
0.696
0.788
0.905
0.941
0.754
-
-
-
-
-
-
-
1.25
1.16
1.64
1.21
1.28
1.18
1.32
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      L-18

-------
Table L-4d.     Benzorq/i/lperylene (191-24-2):  Range of Potential Absorbed Dose in NC
                 Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54

-------
Table L-5a.     BenzoMpyrene (50-32-8): Estimates of Potential Exposure in NC Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54
75.0
73.8
81.0
81.8
67.7
63.1
88.1
24.2
25.2
19.0
24.1
22.7
24.2
24.2
100.0
100.0
100.0
100.0
100.0
100.0
100.0
1.49
1.47
1.60
1.90
1.13
1.47
1.51
-
-
-
-
-
-
-
27.3
22.8
47.6
16.7
37.8
16.9
39.2
1.69
1.58
2.20
1.85
1.49
1.92
1.40
-
-
-
-
-
-
-
68.1
46.0
127
26.7
90.5
28.0
94.3
1.02
1.03
0.987
1.35
0.797
0.951
1.11
-
-
-
-
-
-
-
9.83
10.1
8.79
8.44
11.7
8.17
12.2
0.795
0.778
0.893
0.809
0.706
0.830
0.753
-
-
-
-
-
-
-
1.24
1.15
1.60
1.11
1.34
1.14
1.32
Potential Exposure in NC Preschool Children (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54
75.0
73.8
81.0
81.8
67.7
63.1
88.1
24.2
25.2
19.0
24.1
22.7
24.2
24.2
100.0
100.0
100.0
100.0
100.0
100.0
100.0
5.90
5.81
6.36
7.52
4.47
5.84
5.97
-
-
-
-
-
-
-
108
90.4
189
66.2
150
67.0
155
6.69
6.24
8.71
7.33
5.91
7.63
5.53
-
-
-
-
-
-
-
270
182
504
106
359
111
374
4.06
4.09
3.91
5.33
3.16
3.77
4.40
-
-
-
-
-
-
-
39.0
39.9
34.8
33.4
46.4
32.4
48.2
0.795
0.778
0.893
0.809
0.706
0.830
0.753
-
-
-
-
-
-
-
1.24
1.15
1.60
1.11
1.34
1.14
1.32
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                    L-20

-------
Table L-5b.     BenzoMpyrene (50-32-8): Range of Potential Exposure in NC Preschool Children.
                Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54

-------
Table L-5c.     BenzoMpyrene (50-32-8): Estimates of Potential Absorbed Dose in NC Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54
75.0
73.8
81.0
81.8
67.7
63.1
88.1
24.2
25.2
19.0
24.1
22.7
24.2
24.2
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.046
0.046
0.044
0.057
0.037
0.049
0.043
-
-
-
-
-
-
-
0.854
0.703
1.54
0.501
1.20
0.593
1.15
0.056
0.057
0.057
0.059
0.055
0.068
0.039
-
-
-
-
-
-
-
2.13
1.40
4.05
0.825
2.83
1.05
2.90
0.031
0.031
0.028
0.039
0.025
0.030
0.031
-
-
-
-
-
-
-
0.291
0.302
0.247
0.238
0.364
0.256
0.336
0.829
0.822
0.877
0.858
0.768
0.870
0.790
-
-
-
-
-
-
-
1.30
1.19
1.72
1.17
1.38
1.23
1.37
Potential Absorbed Dose in NC Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54
75.0
73.8
81.0
81.8
67.7
63.1
88.1
24.2
25.2
19.0
24.1
22.7
24.2
24.2
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.183
0.184
0.174
0.224
0.148
0.194
0.170
-
-
-
-
-
-
-
3.39
2.79
6.09
1.98
4.77
2.35
4.57
0.224
0.224
0.227
0.234
0.217
0.271
0.156
-
-
-
-
-
-
-
8.45
5.54
16.0
3.27
11.2
4.17
11.5
0.121
0.124
0.110
0.153
0.099
0.120
0.123
-
-
-
-
-
-
-
1.15
1.20
0.978
0.943
1.44
1.02
1.33
0.829
0.822
0.877
0.858
0.768
0.870
0.790
-
-
-
-
-
-
-
1.30
1.19
1.72
1.17
1.38
1.23
1.37
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      L-22

-------
Table L-5d.     BenzoMpyrene (50-32-8):  Range of Potential Absorbed Dose in NC Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54

-------
Table L-6a.     Benzorelpyrene (192-97-2): Estimates of Potential Exposure in NC Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54
73.4
73.8
71.4
83.6
63.1
66.2
81.4
36.7
36.4
38.1
41.4
31.8
33.3
40.3
100.0
100.0
100.0
100.0
100.0
100.0
100.0
1.04
1.05
0.979
1.28
0.840
0.988
1.10
-
-
-
-
-
-
-
27.0
21.8
50.2
17.6
36.4
16.2
39.3
0.817
0.800
0.913
0.936
0.660
0.856
0.775
-
-
-
-
-
-
-
70.2
43.3
137
28.3
93.4
28.7
97.3
0.845
0.858
0.785
1.04
0.704
0.786
0.916
-
-
-
-
-
-
-
9.78
9.80
9.67
8.88
11.1
8.01
12.3
0.608
0.611
0.603
0.622
0.544
0.616
0.594
-
-
-
-
-
-
-
1.22
1.14
1.55
1.15
1.29
1.10
1.32
Potential Exposure in NC Preschool Children (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54
73.4
73.8
71.4
83.6
63.1
66.2
81.4
36.7
36.4
38.1
41.4
31.8
33.3
40.3
100.0
100.0
100.0
100.0
100.0
100.0
100.0
4.13
4.18
3.88
5.06
3.33
3.92
4.36
-
-
-
-
-
-
-
107
86.6
199
69.6
144
64.3
156
3.24
3.17
3.62
3.71
2.62
3.39
3.07
-
-
-
-
-
-
-
278
172
545
112
370
114
386
3.35
3.40
3.11
4.12
2.79
3.12
3.63
-
-
-
-
-
-
-
38.7
38.8
38.3
35.2
43.9
31.8
48.7
0.608
0.611
0.603
0.622
0.544
0.616
0.594
-
-
-
-
-
-
-
1.22
1.14
1.55
1.15
1.29
1.10
1.32
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected.  Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                    L-24

-------
Table L-6b.     Benzorelpyrene (192-97-2): Range of Potential Exposure in NC Preschool
                Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54

-------
Table L-6c.     Benzorelpyrene (192-97-2):  Estimates of Potential Absorbed Dose in NC Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54
73.4
73.8
71.4
83.6
63.1
66.2
81.4
36.7
36.4
38.1
41.4
31.8
33.3
40.3
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.032
0.033
0.027
0.038
0.027
0.033
0.031
-
-
-
-
-
-
-
0.842
0.669
1.62
0.521
1.16
0.569
1.15
0.028
0.029
0.023
0.032
0.023
0.032
0.022
-
-
-
-
-
-
-
2.20
1.30
4.38
0.863
2.93
1.06
3.01
0.025
0.026
0.022
0.030
0.022
0.025
0.026
-
-
-
-
-
-
-
0.289
0.293
0.271
0.250
0.345
0.251
0.340
0.639
0.650
0.576
0.664
0.601
0.655
0.626
-
-
-
-
-
-
-
1.27
1.19
1.65
1.20
1.33
1.19
1.35
Potential Absorbed Dose in NC Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54
73.4
73.8
71.4
83.6
63.1
66.2
81.4
36.7
36.4
38.1
41.4
31.8
33.3
40.3
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.127
0.131
0.106
0.150
0.108
0.129
0.124
-
-
-
-
-
-
-
3.34
2.65
6.43
2.06
4.60
2.25
4.58
0.110
0.114
0.092
0.129
0.092
0.128
0.088
-
-
-
-
-
-
-
8.73
5.17
17.3
3.42
11.6
4.21
11.9
0.100
0.103
0.087
0.118
0.087
0.099
0.101
-
-
-
-
-
-
-
1.15
1.16
1.08
0.992
1.37
0.996
1.35
0.639
0.650
0.576
0.664
0.601
0.655
0.626
-
-
-
-
-
-
-
1.27
1.19
1.65
1.20
1.33
1.19
1.35
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      L-26

-------
Table L-6d.     Benzorelpyrene (192-97-2): Range of Potential Absorbed Dose in NC Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54

-------
Table L-7a.     Benzylbutylphthalate (85-68-7):  Estimates of Potential Exposure in NC Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
81
65
16
34
44
48
33
111
95
16
45
62
63
48
44.4
47.6
28.6
54.5
36.9
36.9
52.5
14.8
15.4
12.5
11.8
18.2
8.3
24.2
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
1,570
-
-
714
-
-
-
-
-
-
-
2,430
2,280
3,310
3,740
1,590
2,170
2,770
-
-
-
5,820
-
-
827
-
-
-
-
-
-
-
3,540
3,390
4,380
4,340
2,610
3,340
3,800
-
-
-
624
-
-
529
-
-
-
-
-
-
-
1,060
1,010
1,480
1,710
798
846
1,430
-
-
-
0.924
-
-
0.670
-
-
-
-
-
-
-
1.31
1.31
1.32
1.44
1.11
1.38
1.16
Potential Exposure in NC Preschool Children (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
81
65
16
34
44
48
33
111
95
16
45
62
63
48
44.4
47.6
28.6
54.5
36.9
36.9
52.5
14.8
15.4
12.5
11.8
18.2
8.3
24.2
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
5,020
-
-
2,290
-
-
-
-
-
-
-
7,790
7,310
10,600
12,000
5,100
6,960
8,870
-
-
-
18,600
-
-
2,650
-
-
-
-
-
-
-
1 1 ,300
10,800
14,000
13,900
8,370
10,700
12,200
-
-
-
2,000
-
-
1,690
-
-
-
-
-
-
-
3,400
3,220
4,730
5,470
2,550
2,710
4,590
-
-
-
0.924
-
-
0.670
-
-
-
-
-
-
-
1.31
1.31
1.32
1.44
1.11
1.38
1.16
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                    L-28

-------
Table L-7b.     Benzylbutylphthalate (85-68-7):  Range of Potential Exposure in NC Preschool
                Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
81
65
16
34
44
48
33
111
95
16
45
62
63
48

-------
Table L-7c.     Benzylbutylphthalate (85-68-7): Estimates of Potential Absorbed Dose in NC
                 Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
81
65
16
34
44
48
33
111
95
16
45
62
63
48
44.4
47.6
28.6
54.5
36.9
36.9
52.5
14.8
15.4
12.5
11.8
18.2
8.3
24.2
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
46.2
-
-
20.3
-
-
-
-
-
-
-
76.1
71.9
101
110
55.3
72.7
80.5
-
-
-
165
-
-
24.7
-
-
-
-
-
-
-
119
113
152
137
103
117
123
-
-
-
17.9
-
-
14.8
-
-
-
-
-
-
-
31.9
30.4
42.9
48.6
25.1
26.7
40.3
-
-
-
0.998
-
-
0.698
-
-
-
-
-
-
-
1.35
1.35
1.33
1.47
1.16
1.44
1.18
Potential Absorbed Dose in NC Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
81
65
16
34
44
48
33
111
95
16
45
62
63
48
44.4
47.6
28.6
54.5
36.9
36.9
52.5
14.8
15.4
12.5
11.8
18.2
8.3
24.2
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
148
-
-
65.0
-
-
-
-
-
-
-
244
230
322
351
177
233
258
-
-
-
527
-
-
79.1
-
-
-
-
-
-
-
382
363
485
439
329
375
394
-
-
-
57.2
-
-
47.2
-
-
-
-
-
-
-
102
97.2
137
156
80.5
85.5
129
-
-
-
0.998
-
-
0.698
-
-
-
-
-
-
-
1.35
1.35
1.33
1.47
1.16
1.44
1.18
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      L-30

-------
Table L-7d.     Benzylbutylphthalate (85-68-7):  Range of Potential Absorbed Dose in NC
                 Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
81
65
16
34
44
48
33
111
95
16
45
62
63
48

-------
Table L-8a.     Bisphenol-A (80-05-7):  Estimates of Potential Exposure in NC Preschool Children.
                 Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Potential Exposure
-Aggregated
(ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
129
108
21
59
66
66
63
107
87
20
42
61
63
44
102
82
20
38
60
62
40
82.3
80.6
90.5
87.3
80.0
81.5
83.1
98.4
98.1
100.0
98.3
98.5
97.0
100.0
41.1
39.1
50.0
54.8
34.4
22.2
68.2
100.0
100.0
100.0
100.0
100.0
100.0
100.0
Potential Exposure in NC
Potential Exposure
via Inhalation
(p moles/day)
Potential Exposure
via Dietary
Ingestion
(p moles/day)
Potential Exposure
via Indirect
Ingestion
(p moles/day)
Potential Exposure
-Aggregated
(p moles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
129
108
21
59
66
66
63
107
87
20
42
61
63
44
102
82
20
38
60
62
40
82.3
80.6
90.5
87.3
80.0
81.5
83.1
98.4
98.1
100.0
98.3
98.5
97.0
100.0
41.1
39.1
50.0
54.8
34.4
22.2
68.2
100.0
100.0
100.0
100.0
100.0
100.0
100.0
32.7
34.6
23.4
25.6
38.3
43.7
20.5
4,540
4,550
4,470
4,190
5,000
2,900
6,250
-
-
5.08
2.02
-
-
2.03
4,190
4,090
4,580
3,860
4,530
3,040
5,960
Preschool Children
143
151
103
112
168
191
89.9
19,900
19,900
19,600
18,400
21,900
12,700
27,400
-
-
22.2
8.87
-
-
8.88
18,300
17,900
20,100
16,900
19,800
13,300
26,100
119
130
26.3
34.2
161
162
24.4
6,690
7,130
3,770
3,490
8,740
3,070
8,750
-
-
15.4
2.83
-
-
2.12
6,190
6,660
3,830
3,280
7,630
3,120
8,880
15.5
15.6
15.3
16.7
14.4
16.5
14.6
2,640
2,560
3,120
2,910
2,530
1,710
4,150
-
-
1.33
1.16
-
-
1.37
2,500
2,350
3,220
2,660
2,490
1,850
3,980
0.911
0.923
0.875
0.840
0.939
1.03
0.762
1.06
1.08
0.931
0.947
1.14
1.09
0.823
-
-
1.29
0.995
-
-
0.855
1.03
1.06
0.919
0.949
1.08
1.05
0.814
pmoles/day)
521
569
115
150
706
711
107
29,300
31 ,200
16,500
15,300
38,300
13,400
38,300
-
-
67.4
12.4
-
-
9.31
27,100
29,200
16,800
14,300
33,400
13,700
38,900
68.1
68.2
67.2
73.1
63.2
72.1
63.9
1 1 ,600
11,200
13,700
12,700
11,100
7,510
18,200
-
-
5.83
5.06
-
-
6.02
10,900
10,300
14,100
11,700
10,900
8,100
17,400
0.911
0.923
0.875
0.840
0.939
1.03
0.762
1.06
1.08
0.931
0.947
1.14
1.09
0.823
-
-
1.29
0.995
-
-
0.855
1.03
1.06
0.919
0.949
1.08
1.05
0.814
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                    L-32

-------
Table L-8b.    Bisphenol-A (80-05-7):  Range of Potential Exposure in NC Preschool Children.
                Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Potential Exposure
- Aggregated
(ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
129
108
21
59
66
66
63
107
87
20
42
61
63
44
102
82
20
38
60
62
40
Potential E
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Potential Exposure
-Aggregated
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
129
108
21
59
66
66
63
107
87
20
42
61
63
44
102
82
20
38
60
62
40

-------
Table L-8c.     Bisphenol-A (80-05-7):  Estimates of Potential Absorbed Dose in NC Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Potential Absorbed
Dose - Aggregated
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
129
108
21
59
66
66
63
107
87
20
42
61
63
44
102
82
20
38
60
62
40
82.3
80.6
90.5
87.3
80.0
81.5
83.1
98.4
98.1
100.0
98.3
98.5
97.0
100.0
41.1
39.1
50.0
54.8
34.4
22.2
68.2
100.0
100.0
100.0
100.0
100.0
100.0
100.0
Potential Absorbed Dose in NC
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose - Aggregated
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
129
108
21
59
66
66
63
107
87
20
42
61
63
44
102
82
20
38
60
62
40
82.3
80.6
90.5
87.3
80.0
81.5
83.1
98.4
98.1
100.0
98.3
98.5
97.0
100.0
41.1
39.1
50.0
54.8
34.4
22.2
68.2
100.0
100.0
100.0
100.0
100.0
100.0
100.0
1.02
1.08
0.679
0.797
1.20
1.39
0.598
135
137
123
123
151
92.8
179
-
-
0.188
0.065
-
-
0.060
125
125
126
109
141
97.7
169
3.65
3.99
0.772
1.12
4.94
4.97
0.751
186
199
102
111
237
99.0
240
-
-
0.630
0.099
-
-
0.066
175
189
104
90.5
215
101
246
0.464
0.471
0.431
0.477
0.450
0.523
0.406
78.8
77.2
87.7
83.1
79.1
54.3
116
-
-
0.038
0.033
-
-
0.039
75.6
72.4
90.6
76.4
78.9
59.1
111
0.964
0.976
0.921
0.940
0.973
1.07
0.814
1.06
1.09
0.899
0.975
1.13
1.10
0.873
-
-
1.38
1.10
-
-
0.911
1.03
1.06
0.885
0.958
1.07
1.07
0.851
Preschool Children (pmoles/kg/day)
4.45
4.75
2.97
3.49
5.27
6.11
2.62
591
601
539
537
660
406
784
-
-
0.825
0.286
-
-
0.263
550
549
554
477
616
428
738
16.0
17.5
3.38
4.89
21.6
21.8
3.29
815
870
447
486
1,040
434
1,050
-
-
2.76
0.436
-
-
0.289
767
827
456
397
944
441
1,080
2.03
2.06
1.89
2.09
1.97
2.29
1.78
345
338
384
364
347
238
510
-
-
0.164
0.145
-
-
0.169
331
317
397
335
346
259
485
0.964
0.976
0.921
0.940
0.973
1.07
0.814
1.06
1.09
0.899
0.975
1.13
1.10
0.873
-
-
1.38
1.10
-
-
0.911
1.03
1.06
0.885
0.958
1.07
1.07
0.851
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      L-34

-------
Table L-8d.     Bisphenol-A (80-05-7): Range of Potential Absorbed Dose in NC Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Potential Absorbed
Dose - Aggregated
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
129
108
21
59
66
66
63
107
87
20
42
61
63
44
102
82
20
38
60
62
40

-------
Table L-9a.     a/p/ia-Chlordane (5103-71-9):  Estimates of Potential Exposure in NC Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
125
104
21
57
64
65
60
120
99
21
52
64
66
54
98.4
98.1
100.0
100.0
98.5
96.9
100.0
28.8
29.8
23.8
36.8
20.3
16.9
41.7
96.7
97.0
95.2
100.0
93.8
93.9
100.0
28.0
25.8
38.8
29.2
22.3
29.1
26.8
-
-
-
-
-
-
-
4.81
4.51
6.22
4.43
5.15
4.03
5.75
56.6
56.1
59.1
50.6
41.7
65.0
46.1
-
-
-
-
-
-
-
7.44
7.70
6.06
6.04
8.55
6.63
8.29
10.2
9.43
14.8
12.7
8.49
8.58
12.3
-
-
-
-
-
-
-
1.71
1.53
2.94
1.74
1.67
1.40
2.20
1.33
1.29
1.46
1.19
1.34
1.46
1.15
-
-
-
-
-
-
-
1.51
1.50
1.49
1.48
1.56
1.50
1.49
Potential Exposure in NC Preschool Children (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
125
104
21
57
64
65
60
120
99
21
52
64
66
54
98.4
98.1
100.0
100.0
98.5
96.9
100.0
28.8
29.8
23.8
36.8
20.3
16.9
41.7
96.7
97.0
95.2
100.0
93.8
93.9
100.0
68.3
62.9
94.8
71.4
54.5
70.9
65.4
-
-
-
-
-
-
-
11.7
11.0
15.2
10.8
12.6
9.85
14.0
138
137
144
124
102
159
112
-
-
-
-
-
-
-
18.2
18.8
14.8
14.7
20.9
16.2
20.2
24.8
23.0
36.0
31.0
20.7
20.9
30.0
-
-
-
-
-
-
-
4.18
3.73
7.18
4.25
4.07
3.41
5.37
1.33
1.29
1.46
1.19
1.34
1.46
1.15
-
-
-
-
-
-
-
1.51
1.50
1.49
1.48
1.56
1.50
1.49
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                    L-36

-------
Table L-9b.     a/p/ia-Chlordane (5103-71-9):  Range of Potential Exposure in NC Preschool
                Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
125
104
21
57
64
65
60
120
99
21
52
64
66
54

-------
Table L-9c.     a/p/ia-Chlordane (5103-71-9):  Estimates of Potential Absorbed Dose in NC
                 Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
125
104
21
57
64
65
60
120
99
21
52
64
66
54
98.4
98.1
100.0
100.0
98.5
96.9
100.0
28.8
29.8
23.8
36.8
20.3
16.9
41.7
96.7
97.0
95.2
100.0
93.8
93.9
100.0
0.822
0.766
1.10
0.845
0.735
0.866
0.774
-
-
-
-
-
-
-
0.145
0.138
0.179
0.122
0.167
0.130
0.164
1.53
1.49
1.70
1.42
1.43
1.68
1.35
-
-
-
-
-
-
-
0.227
0.237
0.174
0.159
0.274
0.199
0.259
0.304
0.285
0.415
0.364
0.265
0.272
0.342
-
-
-
-
-
-
-
0.051
0.046
0.083
0.049
0.052
0.044
0.061
1.34
1.32
1.45
1.21
1.38
1.47
1.19
-
-
-
-
-
-
-
1.54
1.54
1.52
1.48
1.63
1.56
1.52
Potential Absorbed Dose in NC Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
125
104
21
57
64
65
60
120
99
21
52
64
66
54
98.4
98.1
100.0
100.0
98.5
96.9
100.0
28.8
29.8
23.8
36.8
20.3
16.9
41.7
96.7
97.0
95.2
100.0
93.8
93.9
100.0
2.01
1.87
2.68
2.06
1.79
2.11
1.89
-
-
-
-
-
-
-
0.354
0.336
0.438
0.298
0.408
0.317
0.400
3.73
3.64
4.14
3.47
3.49
4.11
3.29
-
-
-
-
-
-
-
0.554
0.579
0.424
0.389
0.670
0.484
0.631
0.741
0.696
1.01
0.888
0.646
0.665
0.835
-
-
-
-
-
-
-
0.125
0.113
0.202
0.120
0.128
0.108
0.149
1.34
1.32
1.45
1.21
1.38
1.47
1.19
-
-
-
-
-
-
-
1.54
1.54
1.52
1.48
1.63
1.56
1.52
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      L-38

-------
Table L-9d.     a/p/ia-Chlordane (5103-71-9):  Range of Potential Absorbed Dose in NC Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
125
104
21
57
64
65
60
120
99
21
52
64
66
54

-------
Table L-10a.    qa/n/na-Chlordane (5103-74-2): Estimates of Potential Exposure in NC Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
125
104
21
57
64
65
60
119
98
21
51
64
65
54
100.0
100.0
100.0
100.0
100.0
100.0
100.0
21.6
21.2
23.8
28.1
14.1
15.4
28.3
98.3
99.0
95.2
100.0
96.9
96.9
100.0
50.3
44.5
78.7
56.3
37.6
52.4
48.0
-
-
-
-
-
-
-
7.05
6.32
10.5
7.30
6.90
6.23
8.04
94.7
88.4
119
93.5
58.5
112
72.5
-
-
-
-
-
-
-
10.3
10.1
10.9
10.1
10.7
10.2
10.5
18.2
16.7
27.7
23.2
14.9
15.1
22.3
-
-
-
-
-
-
-
2.54
2.24
4.50
2.62
2.44
2.05
3.27
1.38
1.34
1.55
1.28
1.38
1.52
1.19
-
-
-
-
-
-
-
1.53
1.50
1.58
1.56
1.54
1.56
1.48
Potential Exposure in NC Preschool Children (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
125
104
21
57
64
65
60
119
98
21
51
64
65
54
100.0
100.0
100.0
100.0
100.0
100.0
100.0
21.6
21.2
23.8
28.1
14.1
15.4
28.3
98.3
99.0
95.2
100.0
96.9
96.9
100.0
123
109
192
137
91.9
128
117
-
-
-
-
-
-
-
17.2
15.4
25.6
17.8
16.8
15.2
19.6
231
216
292
228
143
272
177
-
-
-
-
-
-
-
25.2
24.6
26.7
24.7
26.1
24.8
25.7
44.4
40.7
67.7
56.7
36.5
36.9
54.4
-
-
-
-
-
-
-
6.19
5.48
11.0
6.40
5.96
5.01
7.99
1.38
1.34
1.55
1.28
1.38
1.52
1.19
-
-
-
-
-
-
-
1.53
1.50
1.58
1.56
1.54
1.56
1.48
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                   L-40

-------
Table L-10b.   qa/n/na-Chlordane (5103-74-2): Range of Potential Exposure in NC Preschool
                Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
125
104
21
57
64
65
60
119
98
21
51
64
65
54
1.00
1.00
3.29
3.10
1.00
1.00
3.41

-------
Table L-10c.   qa/n/na-Chlordane (5103-74-2):  Estimates of Potential Absorbed Dose in NC
                 Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
125
104
21
57
64
65
60
119
98
21
51
64
65
54
100.0
100.0
100.0
100.0
100.0
100.0
100.0
21.6
21.2
23.8
28.1
14.1
15.4
28.3
98.3
99.0
95.2
100.0
96.9
96.9
100.0
1.48
1.33
2.19
1.63
1.24
1.56
1.39
-
-
-
-
-
-
-
0.213
0.195
0.297
0.202
0.226
0.201
0.227
2.51
2.32
3.28
2.67
1.99
2.80
2.16
-
-
-
-
-
-
-
0.312
0.311
0.312
0.277
0.346
0.307
0.321
0.543
0.504
0.779
0.665
0.466
0.480
0.621
-
-
-
-
-
-
-
0.076
0.068
0.126
0.074
0.077
0.065
0.091
1.39
1.36
1.53
1.29
1.42
1.52
1.24
-
-
-
-
-
-
-
1.56
1.54
1.59
1.55
1.61
1.60
1.50
Potential Absorbed Dose in NC Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
125
104
21
57
64
65
60
119
98
21
51
64
65
54
100.0
100.0
100.0
100.0
100.0
100.0
100.0
21.6
21.2
23.8
28.1
14.1
15.4
28.3
98.3
99.0
95.2
100.0
96.9
96.9
100.0
3.60
3.25
5.34
3.97
3.02
3.80
3.38
-
-
-
-
-
-
-
0.520
0.476
0.725
0.494
0.552
0.491
0.554
6.12
5.65
7.99
6.51
4.87
6.84
5.26
-
-
-
-
-
-
-
0.762
0.758
0.760
0.675
0.845
0.749
0.783
1.32
1.23
1.90
1.62
1.14
1.17
1.52
-
-
-
-
-
-
-
0.185
0.165
0.308
0.180
0.188
0.159
0.221
1.39
1.36
1.53
1.29
1.42
1.52
1.24
-
-
-
-
-
-
-
1.56
1.54
1.59
1.55
1.61
1.60
1.50
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected.  Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      L-42

-------
Table L-10d.    qa/n/na-Chlordane (5103-74-2): Range of Potential Absorbed Dose in NC Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
125
104
21
57
64
65
60
119
98
21
51
64
65
54
0.041
0.041
0.102
0.081
0.041
0.041
0.060

-------
Table L-11a.    Chlorpyrifos (2921-88-2): Estimates of Potential Exposure in NC Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Potential Exposure
-Aggregated
(ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
125
104
21
57
64
65
60
117
97
20
51
62
65
52
109
89
20
45
60
63
46
100.0
100.0
100.0
100.0
100.0
100.0
100.0
78.4
80.8
66.7
82.5
75.0
70.8
86.7
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
Potential Exposure in NC
Potential Exposure
via Inhalation
(p moles/day)
Potential Exposure
via Dietary
Ingestion
(p moles/day)
Potential Exposure
via Indirect
Ingestion
(p moles/day)
Potential Exposure
-Aggregated
(p moles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
125
104
21
57
64
65
60
117
97
20
51
62
65
52
109
89
20
45
60
63
46
100.0
100.0
100.0
100.0
100.0
100.0
100.0
78.4
80.8
66.7
82.5
75.0
70.8
86.7
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
121
120
124
135
111
109
134
209
229
108
275
159
268
145
15.5
13.4
25.5
19.4
12.4
13.8
17.7
359
381
264
483
279
398
305
Preschool Children
345
343
354
384
318
311
382
596
654
309
786
453
765
414
44.2
38.3
72.7
55.4
35.5
39.3
50.4
1,020
1,090
753
1,380
797
1,140
871
216
227
156
241
201
191
242
676
740
82.9
963
261
926
149
29.0
21.4
51.9
36.9
21.4
23.6
34.7
801
878
250
1,150
409
1,010
343
56.0
54.1
66.3
65.5
48.7
46.3
69.2
85.3
87.5
75.3
98.2
77.2
74.8
98.4
6.23
5.96
7.78
6.96
5.48
5.46
7.36
174
172
183
211
152
156
203
1.18
1.17
1.23
1.17
1.20
1.26
1.05
1.15
1.19
0.944
1.16
1.15
1.33
0.902
1.30
1.24
1.58
1.42
1.22
1.29
1.31
1.06
1.10
0.883
1.13
1.03
1.18
0.863
pmoles/day)
617
649
445
688
574
546
691
1,930
2,110
236
2,750
745
2,640
426
82.7
61.0
148
105
60.9
67.4
98.9
2,280
2,500
713
3,280
1,170
2,890
980
160
154
189
187
139
132
197
243
250
215
280
220
213
281
17.8
17.0
22.2
19.8
15.6
15.6
21.0
497
492
522
601
434
445
578
1.18
1.17
1.23
1.17
1.20
1.26
1.05
1.15
1.19
0.944
1.16
1.15
1.33
0.902
1.30
1.24
1.58
1.42
1.22
1.29
1.31
1.06
1.10
0.883
1.13
1.03
1.18
0.863
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                    L-44

-------
Table L-11b.   Chlorpyrifos (2921-88-2): Range of Potential Exposure in NC Preschool Children.
                Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Potential Exposure
- Aggregated
(ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
125
104
21
57
64
65
60
117
97
20
51
62
65
52
109
89
20
45
60
63
46
Potential E
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Potential Exposure
-Aggregated
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
125
104
21
57
64
65
60
117
97
20
51
62
65
52
109
89
20
45
60
63
46
2.57
3.47
2.57
2.57
3.47
2.57
6.23

-------
Table L-11c.   Chlorpyrifos (2921-88-2):  Estimates of Potential Absorbed Dose in NC Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Potential Absorbed
Dose - Aggregated
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
125
104
21
57
64
65
60
117
97
20
51
62
65
52
109
89
20
45
60
63
46
100.0
100.0
100.0
100.0
100.0
100.0
100.0
78.4
80.8
66.7
82.5
75.0
70.8
86.7
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
Potential Absorbed Dose in NC
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose - Aggregated
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
125
104
21
57
64
65
60
117
97
20
51
62
65
52
109
89
20
45
60
63
46
100.0
100.0
100.0
100.0
100.0
100.0
100.0
78.4
80.8
66.7
82.5
75.0
70.8
86.7
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
3.61
3.68
3.25
3.89
3.46
3.25
4.00
6.14
6.78
2.95
7.97
4.78
8.00
4.12
0.456
0.409
0.683
0.528
0.403
0.426
0.494
10.6
11.4
7.02
13.9
8.57
11.9
8.81
6.65
7.11
3.75
7.50
6.11
5.43
7.81
20.0
21.9
2.24
28.6
7.45
27.5
4.30
0.798
0.646
1.31
0.946
0.683
0.709
0.902
23.8
26.1
6.07
34.3
11.9
29.9
10.8
1.67
1.64
1.86
1.88
1.52
1.47
1.93
2.54
2.64
2.11
2.79
2.42
2.37
2.74
0.186
0.180
0.217
0.196
0.173
0.173
0.203
5.18
5.20
5.12
5.89
4.77
4.96
5.50
1.17
1.17
1.19
1.16
1.21
1.23
1.10
1.13
1.18
0.889
1.17
1.11
1.30
0.927
1.31
1.26
1.57
1.42
1.25
1.30
1.34
1.05
1.10
0.833
1.14
1.01
1.14
0.929
Preschool Children (pmoles/kg/day)
10.3
10.5
9.27
11.1
9.88
9.28
11.4
17.5
19.3
8.41
22.7
13.6
22.8
11.8
1.30
1.17
1.95
1.51
1.15
1.21
1.41
30.2
32.5
20.0
39.6
24.5
34.0
25.1
19.0
20.3
10.7
21.4
17.4
15.5
22.3
57.2
62.5
6.38
81.7
21.2
78.3
12.3
2.28
1.84
3.73
2.70
1.95
2.02
2.57
67.8
74.5
17.3
97.7
34.1
85.3
30.7
4.77
4.67
5.31
5.35
4.33
4.19
5.50
7.25
7.53
6.03
7.97
6.90
6.76
7.82
0.530
0.513
0.620
0.558
0.494
0.493
0.580
14.8
14.8
14.6
16.8
13.6
14.1
15.7
1.17
1.17
1.19
1.16
1.21
1.23
1.10
1.13
1.18
0.889
1.17
1.11
1.30
0.927
1.31
1.26
1.57
1.42
1.25
1.30
1.34
1.05
1.10
0.833
1.14
1.01
1.14
0.929
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      L-46

-------
Table L-11d.   Chlorpyrifos (2921-88-2):  Range of Potential Absorbed Dose in NC Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Potential Absorbed
Dose - Aggregated
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
125
104
21
57
64
65
60
117
97
20
51
62
65
52
109
89
20
45
60
63
46
0.064
0.142
0.064
0.064
0.142
0.064
0.146

-------
Table L-12a.    Chrysene (218-01-9):  Estimates of Potential Exposure in NC Preschool Children.
                 Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54
87.1
89.3
76.2
92.7
81.5
80.0
94.9
44.5
43.0
52.4
44.8
43.9
45.5
43.5
100.0
100.0
100.0
100.0
100.0
100.0
100.0
1.67
1.71
1.49
1.99
1.39
1.80
1.52
-
-
46.5
-
-
-
-
30.2
24.9
54.2
17.6
42.8
17.0
45.4
2.04
1.96
2.46
2.08
2.00
2.53
1.31
-
-
28.7
-
-
-
-
81.1
58.7
145
30.8
108
34.1
112
1.14
1.18
0.937
1.39
0.957
1.12
1.16
-
-
39.4
-
-
-
-
9.49
9.56
9.18
8.39
11.1
7.50
12.4
0.792
0.789
0.795
0.807
0.735
0.872
0.700
-
-
0.594
-
-
-
-
1.29
1.21
1.63
1.17
1.39
1.15
1.39
Potential Exposure in NC Preschool Children (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54
87.1
89.3
76.2
92.7
81.5
80.0
94.9
44.5
43.0
52.4
44.8
43.9
45.5
43.5
100.0
100.0
100.0
100.0
100.0
100.0
100.0
7.31
7.47
6.54
8.71
6.08
7.89
6.67
-
-
204
-
-
-
-
132
109
237
77.0
187
74.6
199
8.94
8.57
10.8
9.12
8.75
11.1
5.76
-
-
126
-
-
-
-
355
257
633
135
473
149
490
4.98
5.18
4.11
6.07
4.19
4.89
5.08
-
-
173
-
-
-
-
41.6
41.9
40.2
36.8
48.5
32.9
54.5
0.792
0.789
0.795
0.807
0.735
0.872
0.700
-
-
0.594
-
-
-
-
1.29
1.21
1.63
1.17
1.39
1.15
1.39
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                    L-48

-------
Table L-12b.   Chrysene (218-01-9):  Range of Potential Exposure in NC Preschool Children.
                Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54

-------
Table L-12c.   Chrysene (218-01-9):  Estimates of Potential Absorbed Dose in NC Preschool
                 Children. Summarized by Exposure  Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54
87.1
89.3
76.2
92.7
81.5
80.0
94.9
44.5
43.0
52.4
44.8
43.9
45.5
43.5
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.052
0.055
0.041
0.064
0.043
0.061
0.043
-
-
1.29
-
-
-
-
0.938
0.754
1.77
0.517
1.35
0.599
1.33
0.072
0.074
0.063
0.090
0.055
0.093
0.039
-
-
0.787
-
-
-
-
2.52
1.75
4.63
0.949
3.36
1.28
3.41
0.034
0.036
0.026
0.040
0.030
0.035
0.032
-
-
1.11
-
-
-
-
0.281
0.286
0.258
0.236
0.344
0.235
0.344
0.834
0.833
0.808
0.910
0.753
0.918
0.735
-
-
0.563
-
-
-
-
1.33
1.23
1.74
1.19
1.43
1.22
1.42
Potential Absorbed Dose in NC Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54
87.1
89.3
76.2
92.7
81.5
80.0
94.9
44.5
43.0
52.4
44.8
43.9
45.5
43.5
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.229
0.239
0.181
0.282
0.188
0.265
0.190
-
-
5.67
-
-
-
-
4.11
3.30
7.75
2.26
5.93
2.63
5.81
0.317
0.325
0.276
0.392
0.240
0.405
0.169
-
-
3.45
-
-
-
-
11.1
7.65
20.3
4.16
14.7
5.62
15.0
0.149
0.156
0.115
0.174
0.131
0.155
0.141
-
-
4.85
-
-
-
-
1.23
1.25
1.13
1.04
1.51
1.03
1.51
0.834
0.833
0.808
0.910
0.753
0.918
0.735
-
-
0.563
-
-
-
-
1.33
1.23
1.74
1.19
1.43
1.22
1.42
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      L-50

-------
Table L-12d.    Chrysene (218-01-9): Range of Potential Absorbed Dose in NC Preschool Children.
                 Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54

-------
Table L-13a.    Cyfluthrin (68359-37-5):  Estimates of Potential Exposure in NC Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
120
100
20
55
61
64
56
118
97
21
52
62
66
52
6.5
6.8
4.8
12.7
1.5
0.0
13.6
8.3
9.0
5.0
14.5
3.3
4.7
12.5
60.2
60.8
57.1
65.4
56.5
56.1
65.4
-
-
-
-
-
-
-
-
-
-
-
-
-
-
15.9
14.2
23.6
15.1
17.3
16.5
15.2
-
-
-
-
-
-
-
-
-
-
-
-
-
-
33.3
29.1
48.5
33.7
34.3
37.3
27.9
-
-
-
-
-
-
-
-
-
-
-
-
-
-
4.04
4.07
3.91
3.75
4.25
4.01
4.07
-
-
-
-
-
-
-
-
-
-
-
-
-
-
1.69
1.62
2.01
1.77
1.68
1.67
1.73
Potential Exposure in NC Preschool Children (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
120
100
20
55
61
64
56
118
97
21
52
62
66
52
6.5
6.8
4.8
12.7
1.5
0.0
13.6
8.3
9.0
5.0
14.5
3.3
4.7
12.5
60.2
60.8
57.1
65.4
56.5
56.1
65.4
-
-
-
-
-
-
-
-
-
-
-
-
-
-
36.6
32.8
54.2
34.7
39.8
37.9
34.9
-
-
-
-
-
-
-
-
-
-
-
-
-
-
76.8
67.1
112
77.6
78.9
85.8
64.3
-
-
-
-
-
-
-
-
-
-
-
-
-
-
9.30
9.36
9.00
8.63
9.79
9.24
9.37
-
-
-
-
-
-
-
-
-
-
-
-
-
-
1.69
1.62
2.01
1.77
1.68
1.67
1.73
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                    L-52

-------
Table L-13b.   Cyfluthrin (68359-37-5):  Range of Potential Exposure in NC Preschool Children.
                Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
120
100
20
55
61
64
56
118
97
21
52
62
66
52

-------
Table L-13c.   Cyfluthrin (68359-37-5):  Estimates of Potential Absorbed Dose in NC Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
120
100
20
55
61
64
56
118
97
21
52
62
66
52
6.5
6.8
4.8
12.7
1.5
0.0
13.6
8.3
9.0
5.0
14.5
3.3
4.7
12.5
60.2
60.8
57.1
65.4
56.5
56.1
65.4
-
-
-
-
-
-
-
-
-
-
-
-
-
-
0.527
0.471
0.784
0.491
0.582
0.581
0.459
-
-
-
-
-
-
-
-
-
-
-
-
-
-
1.22
1.08
1.76
1.29
1.21
1.44
0.875
-
-
-
-
-
-
-
-
-
-
-
-
-
-
0.120
0.123
0.110
0.106
0.134
0.127
0.112
-
-
-
-
-
-
-
-
-
-
-
-
-
-
1.74
1.67
2.10
1.82
1.73
1.71
1.79
Potential Absorbed Dose in NC Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
120
100
20
55
61
64
56
118
97
21
52
62
66
52
6.5
6.8
4.8
12.7
1.5
0.0
13.6
8.3
9.0
5.0
14.5
3.3
4.7
12.5
60.2
60.8
57.1
65.4
56.5
56.1
65.4
-
-
-
-
-
-
-
-
-
-
-
-
-
-
1.21
1.09
1.81
1.13
1.34
1.34
1.06
-
-
-
-
-
-
-
-
-
-
-
-
-
-
2.82
2.48
4.04
2.96
2.79
3.33
2.01
-
-
-
-
-
-
-
-
-
-
-
-
-
-
0.277
0.283
0.253
0.243
0.309
0.293
0.259
-
-
-
-
-
-
-
-
-
-
-
-
-
-
1.74
1.67
2.10
1.82
1.73
1.71
1.79
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      L-54

-------
Table L-13d.   Cyfluthrin (68359-37-5):  Range of Potential Absorbed Dose in NC Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
120
100
20
55
61
64
56
118
97
21
52
62
66
52

-------
Table L-14a.    Diazinon (333-41-5):  Estimates of Potential Exposure in NC Preschool Children.
                 Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Potential Exposure
-Aggregated
(ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
124
103
21
57
63
64
60
118
97
21
52
62
66
52
109
88
21
46
59
63
46
100.0
100.0
100.0
100.0
100.0
100.0
100.0
31.5
32.0
28.6
42.1
22.2
21.9
41.7
97.5
96.9
100.0
100.0
95.2
95.5
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
Potential Exposure in NC
Potential Exposure
via Inhalation
(p moles/day)
Potential Exposure
via Dietary
Ingestion
(p moles/day)
Potential Exposure
via Indirect
Ingestion
(p moles/day)
Potential Exposure
-Aggregated
(p moles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
124
103
21
57
63
64
60
118
97
21
52
62
66
52
109
88
21
46
59
63
46
100.0
100.0
100.0
100.0
100.0
100.0
100.0
31.5
32.0
28.6
42.1
22.2
21.9
41.7
97.5
96.9
100.0
100.0
95.2
95.5
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
255
296
56.1
144
363
293
214
-
-
-
-
-
-
-
21.7
25.5
4.04
30.7
15.3
19.1
25.1
354
413
106
224
473
374
327
Preschool Children
839
973
184
472
1,190
962
704
-
-
-
-
-
-
-
71.3
83.9
13.3
101
50.4
62.6
82.3
1,160
1,360
349
737
1,560
1,230
1,070
1,440
1,570
105
312
1,970
1,680
1,120
-
-
-
-
-
-
-
81.9
89.9
5.85
94.9
72.1
84.1
79.6
1,720
1,910
148
436
2,310
1,930
1,410
23.7
23.7
23.7
47.3
13.5
17.9
32.5
-
-
-
-
-
-
-
1.56
1.52
1.76
3.28
0.824
1.22
2.14
68.1
68.2
68.0
97.8
52.2
55.3
90.8
1.65
1.73
1.23
1.42
1.63
1.69
1.56
-
-
-
-
-
-
-
1.98
2.09
1.42
1.97
1.82
1.91
2.04
1.21
1.28
0.868
1.15
1.21
1.26
1.07
pmoles/day)
4,720
5,170
346
1,030
6,460
5,530
3,680
-
-
-
-
-
-
-
269
295
19.2
312
237
276
261
5,650
6,280
486
1,430
7,590
6,330
4,630
78.0
78.0
78.0
155
44.5
58.7
107
-
-
-
-
-
-
-
5.13
4.99
5.79
10.8
2.71
3.99
7.04
224
224
223
321
171
182
298
1.65
1.73
1.23
1.42
1.63
1.69
1.56
-
-
-
-
-
-
-
1.98
2.09
1.42
1.97
1.82
1.91
2.04
1.21
1.28
0.868
1.15
1.21
1.26
1.07
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                    L-56

-------
Table L-14b.   Diazinon (333-41-5): Range of Potential Exposure in NC Preschool Children.
                Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Potential Exposure
- Aggregated
(ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
124
103
21
57
63
64
60
118
97
21
52
62
66
52
109
88
21
46
59
63
46
Potential E
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Potential Exposure
-Aggregated
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
124
103
21
57
63
64
60
118
97
21
52
62
66
52
109
88
21
46
59
63
46
2.48
2.48
3.81
4.79
2.48
2.48
2.52

-------
Table L-14c.    Diazinon (333-41-5):  Estimates of Potential Absorbed Dose in NC Preschool
                  Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Potential Absorbed
Dose - Aggregated
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
124
103
21
57
63
64
60
118
97
21
52
62
66
52
109
88
21
46
59
63
46
100.0
100.0
100.0
100.0
100.0
100.0
100.0
31.5
32.0
28.6
42.1
22.2
21.9
41.7
97.5
96.9
100.0
100.0
95.2
95.5
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
Potential Absorbed Dose in NC
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose - Aggregated
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
124
103
21
57
63
64
60
118
97
21
52
62
66
52
109
88
21
46
59
63
46
100.0
100.0
100.0
100.0
100.0
100.0
100.0
31.5
32.0
28.6
42.1
22.2
21.9
41.7
97.5
96.9
100.0
100.0
95.2
95.5
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
7.40
8.59
1.54
4.14
10.6
8.38
6.32
-
-
-
-
-
-
-
0.613
0.718
0.125
0.819
0.474
0.550
0.692
10.2
11.9
2.90
6.30
13.8
10.8
9.41
41.3
45.2
2.74
9.32
56.4
47.6
33.4
-
-
-
-
-
-
-
2.28
2.50
0.224
2.53
2.13
2.30
2.28
49.4
54.9
3.83
13.0
66.2
54.5
41.9
0.708
0.717
0.666
1.35
0.422
0.567
0.905
-
-
-
-
-
-
-
0.047
0.046
0.049
0.092
0.026
0.039
0.059
2.02
2.04
1.91
2.74
1.63
1.74
2.46
1.64
1.71
1.23
1.42
1.65
1.65
1.60
-
-
-
-
-
-
-
1.99
2.10
1.41
1.95
1.88
1.91
2.07
1.18
1.25
0.834
1.13
1.20
1.23
1.09
Preschool Children (pmoles/kg/day)
24.3
28.2
5.07
13.6
34.7
27.5
20.8
-
-
-
-
-
-
-
2.01
2.36
0.411
2.69
1.56
1.81
2.27
33.5
39.2
9.54
20.7
45.3
35.3
30.9
136
149
9.00
30.6
185
156
110
-
-
-
-
-
-
-
7.49
8.22
0.735
8.31
7.00
7.54
7.48
162
180
12.6
42.7
217
179
138
2.33
2.36
2.19
4.45
1.39
1.86
2.97
-
-
-
-
-
-
-
0.153
0.151
0.163
0.303
0.085
0.127
0.194
6.63
6.72
6.27
9.01
5.34
5.73
8.10
1.64
1.71
1.23
1.42
1.65
1.65
1.60
-
-
-
-
-
-
-
1.99
2.10
1.41
1.95
1.88
1.91
2.07
1.18
1.25
0.834
1.13
1.20
1.23
1.09
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      L-58

-------
Table L-14d.   Diazinon (333-41-5):  Range of Potential Absorbed Dose in NC Preschool Children.
                 Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Potential Absorbed
Dose - Aggregated
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
124
103
21
57
63
64
60
118
97
21
52
62
66
52
109
88
21
46
59
63
46
0.059
0.059
0.113
0.129
0.059
0.088
0.059

-------
Table L-15a.    Dibenzora./ilanthracene (53-70-3):  Estimates of Potential Exposure in NC
                 Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
117
96
21
52
61
63
54
9.7
11.7
0.0
12.7
7.7
10.8
8.5
0.0
0.0
0.0
0.0
0.0
0.0
0.0
98.3
97.9
100.0
100.0
98.4
96.8
100.0
-
-
-
-
-
-
-
-
-
-
-
-
-
-
5.62
5.02
8.36
4.10
7.20
3.90
7.63
-
-
-
-
-
-
-
-
-
-
-
-
-
-
12.2
9.69
20.1
6.48
15.7
6.62
16.3
-
-
-
-
-
-
-
-
-
-
-
-
-
-
2.28
2.23
2.50
2.08
2.59
1.88
2.85
-
-
-
-
-
-
-
-
-
-
-
-
-
-
1.22
1.20
1.35
1.20
1.26
1.18
1.25
Potential Exposure in NC Preschool Children (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
117
96
21
52
61
63
54
9.7
11.7
0.0
12.7
7.7
10.8
8.5
0.0
0.0
0.0
0.0
0.0
0.0
0.0
98.3
97.9
100.0
100.0
98.4
96.8
100.0
-
-
-
-
-
-
-
-
-
-
-
-
-
-
20.2
18.0
30.0
14.7
25.9
14.0
27.4
-
-
-
-
-
-
-
-
-
-
-
-
-
-
43.7
34.8
72.2
23.3
56.2
23.8
58.5
-
-
-
-
-
-
-
-
-
-
-
-
-
-
8.18
8.01
8.98
7.48
9.31
6.74
10.2
-
-
-
-
-
-
-
-
-
-
-
-
-
-
1.22
1.20
1.35
1.20
1.26
1.18
1.25
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                   L-60

-------
Table L-15b.   Dibenzora./ilanthracene (53-70-3):  Range of Potential Exposure in NC Preschool
                Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
117
96
21
52
61
63
54

-------
Table L-15c.   Dibenzora./ilanthracene (53-70-3): Estimates of Potential Absorbed Dose in NC
                 Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
117
96
21
52
61
63
54
9.7
11.7
0.0
12.7
7.7
10.8
8.5
0.0
0.0
0.0
0.0
0.0
0.0
0.0
98.3
97.9
100.0
100.0
98.4
96.8
100.0
-
-
-
-
-
-
-
-
-
-
-
-
-
-
0.176
0.155
0.270
0.122
0.231
0.136
0.222
-
-
-
-
-
-
-
-
-
-
-
-
-
-
0.382
0.295
0.648
0.200
0.490
0.243
0.495
-
-
-
-
-
-
-
-
-
-
-
-
-
-
0.067
0.067
0.070
0.059
0.081
0.059
0.079
-
-
-
-
-
-
-
-
-
-
-
-
-
-
1.28
1.24
1.44
1.24
1.30
1.27
1.28
Potential Absorbed Dose in NC Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
117
96
21
52
61
63
54
9.7
11.7
0.0
12.7
7.7
10.8
8.5
0.0
0.0
0.0
0.0
0.0
0.0
0.0
98.3
97.9
100.0
100.0
98.4
96.8
100.0
-
-
-
-
-
-
-
-
-
-
-
-
-
-
0.631
0.557
0.970
0.437
0.829
0.489
0.796
-
-
-
-
-
-
-
-
-
-
-
-
-
-
1.37
1.06
2.33
0.717
1.76
0.874
1.78
-
-
-
-
-
-
-
-
-
-
-
-
-
-
0.242
0.240
0.252
0.211
0.290
0.212
0.283
-
-
-
-
-
-
-
-
-
-
-
-
-
-
1.28
1.24
1.44
1.24
1.30
1.27
1.28
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected.  Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      L-62

-------
Table L-15d.    Dibenzora./ilanthracene (53-70-3):  Range of Potential Absorbed Dose in NC
                 Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
117
96
21
52
61
63
54

-------
Table L-16a.    Di-n-butylphthalate (84-74-2):  Estimates of Potential Exposure in NC Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Potential Exposure
-Aggregated
(ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
86
69
17
38
46
51
35
117
96
21
51
62
63
54
78
61
17
32
44
47
31
100.0
100.0
100.0
100.0
100.0
100.0
100.0
61.6
63.8
52.9
50.0
69.6
49.0
80.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
Potential Exposure in NC
Potential Exposure
via Inhalation
(p moles/day)
Potential Exposure
via Dietary
Ingestion
(p moles/day)
Potential Exposure
via Indirect
Ingestion
(p moles/day)
Potential Exposure
-Aggregated
(p moles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
86
69
17
38
46
51
35
117
96
21
51
62
63
54
78
61
17
32
44
47
31
100.0
100.0
100.0
100.0
100.0
100.0
100.0
61.6
63.8
52.9
50.0
69.6
49.0
80.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
2,400
2,520
1,810
2,680
2,150
1,710
3,150
70,900
68,000
82,500
66,700
68,600
-
79,600
539
563
427
560
493
544
533
72,900
69,600
84,700
71,500
67,800
65,300
84,300
Preschool Children
8,610
9,040
6,490
9,630
7,710
6,150
1 1 ,300
255,000
244,000
296,000
240,000
247,000
-
286,000
1,940
2,020
1,530
2,010
1,770
1,950
1,920
262,000
250,000
304,000
257,000
243,000
235,000
303,000
1,770
1,900
685
2,150
1,330
908
2,150
78,000
73,200
96,700
80,000
67,100
-
71 ,400
724
775
411
624
753
903
439
76,600
70,500
96,800
79,300
64,400
82,300
66,600
1,980
2,040
1,680
2,190
1,810
1,500
2,670
43,000
41,700
48,900
38,500
44,800
-
54,400
339
349
299
354
327
302
390
47,100
45,900
51,600
44,300
46,700
38,700
63,400
0.606
0.636
0.409
0.585
0.611
0.528
0.545
1.00
1.00
1.02
1.02
0.965
-
0.902
0.911
0.922
0.872
0.980
0.797
0.974
0.820
0.927
0.917
0.987
0.962
0.880
0.973
0.777
pmoles/day)
6,360
6,820
2,460
7,730
4,770
3,260
7,730
280,000
263,000
348,000
287,000
241,000
-
256,000
2,600
2,780
1,480
2,240
2,710
3,240
1,580
275,000
253,000
348,000
285,000
231,000
296,000
239,000
7,100
7,340
6,030
7,870
6,500
5,400
9,600
155,000
150,000
176,000
138,000
161,000
-
195,000
1,220
1,250
1,070
1,270
1,170
1,080
1,400
169,000
165,000
186,000
159,000
168,000
139,000
228,000
0.606
0.636
0.409
0.585
0.611
0.528
0.545
1.00
1.00
1.02
1.02
0.965
-
0.902
0.911
0.922
0.872
0.980
0.797
0.974
0.820
0.927
0.917
0.987
0.962
0.880
0.973
0.777
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                    L-64

-------
Table L-16b.   Di-n-butylphthalate (84-74-2):  Range of Potential Exposure in NC Preschool
                Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Potential Exposure
- Aggregated
(ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
86
69
17
38
46
51
35
117
96
21
51
62
63
54
78
61
17
32
44
47
31
Potential E
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Potential Exposure
-Aggregated
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
86
69
17
38
46
51
35
117
96
21
51
62
63
54
78
61
17
32
44
47
31
313
313
551
806
313
313
1,190

-------
Table L-16c.   Di-n-butylphthalate (84-74-2): Estimates of Potential Absorbed Dose in NC
                 Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Potential Absorbed
Dose - Aggregated
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
86
69
17
38
46
51
35
117
96
21
51
62
63
54
78
61
17
32
44
47
31
Potential Absor
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose - Aggregated
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
86
69
17
38
46
51
35
117
96
21
51
62
63
54
78
61
17
32
44
47
31
100.0
100.0
100.0
100.0
100.0
100.0
100.0
61.6
63.8
52.9
50.0
69.6
49.0
80.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
bed Dose in NC
100.0
100.0
100.0
100.0
100.0
100.0
100.0
61.6
63.8
52.9
50.0
69.6
49.0
80.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
72.9
77.3
51.6
81.6
65.8
56.7
90.8
2,090
2,020
2,370
1,660
2,290
-
2,160
16.9
17.7
13.1
16.5
16.3
18.2
15.3
2,100
2,010
2,430
1,730
2,190
1,990
2,260
57.5
61.5
22.2
74.3
37.1
41.3
67.2
2,340
2,260
2,740
1,700
2,540
-
1,940
24.1
25.6
15.3
18.4
27.1
30.5
13.4
2,190
2,030
2,740
1,500
2,340
2,450
1,760
59.0
61.8
47.2
62.7
56.4
47.8
74.4
1,260
1,240
1,380
1,050
1,390
-
1,480
10.1
10.5
8.39
9.95
10.2
9.50
10.8
1,360
1,340
1,450
1,180
1,440
1,190
1,690
0.628
0.651
0.448
0.668
0.586
0.577
0.605
1.00
0.994
1.05
0.948
1.01
-
0.895
0.976
0.981
0.955
1.05
0.848
1.06
0.867
0.921
0.898
1.03
0.893
0.912
0.976
0.799
Preschool Children (pmoles/kg/day)
262
278
185
293
236
204
326
7,510
7,270
8,500
5,970
8,220
-
7,770
60.5
63.5
47.0
59.4
58.7
65.4
54.9
7,540
7,200
8,730
6,200
7,890
7,160
8,110
207
221
79.7
267
133
148
242
8,420
8,100
9,830
6,120
9,140
-
6,990
86.6
92.0
54.8
66.1
97.2
110
48.1
7,880
7,300
9,850
5,380
8,410
8,810
6,310
212
222
169
225
203
172
267
4,530
4,440
4,940
3,780
5,010
-
5,330
36.2
37.7
30.1
35.8
36.7
34.1
38.7
4,900
4,810
5,220
4,250
5,160
4,260
6,060
0.628
0.651
0.448
0.668
0.586
0.577
0.605
1.00
0.994
1.05
0.948
1.01
-
0.895
0.976
0.981
0.955
1.05
0.848
1.06
0.867
0.921
0.898
1.03
0.893
0.912
0.976
0.799
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      L-66

-------
Table L-16d.   Di-n-butylphthalate (84-74-2):  Range of Potential Absorbed Dose in NC Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Potential Absorbed
Dose - Aggregated
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
86
69
17
38
46
51
35
117
96
21
51
62
63
54
78
61
17
32
44
47
31
9.31
9.31
16.0
22.8
9.31
9.31
22.7

-------
Table L-17a.    p.p'-DDE (72-55-9):  Estimates of Potential Exposure in NC Preschool Children.
                 Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
125
104
21
57
64
65
60
120
99
21
52
64
66
54
36.3
35.0
42.9
49.1
26.2
30.8
42.4
76.8
77.9
71.4
78.9
75.0
70.8
83.3
56.7
52.5
76.2
73.1
45.3
42.4
74.1
-
-
-
-
-
-
-
126
124
138
131
121
104
150
0.624
0.575
0.853
0.699
-
-
0.757
-
-
-
-
-
-
-
112
110
124
113
112
94.7
125
1.49
1.48
1.55
1.89
-
-
1.93
-
-
-
-
-
-
-
84.4
83.7
88.5
89.4
80.3
68.5
106
0.241
0.224
0.339
0.273
-
-
0.272
-
-
-
-
-
-
-
0.942
0.923
1.06
0.922
0.951
0.959
0.877
1.27
1.24
1.38
1.23
-
-
1.31
Potential Exposure in NC Preschool Children (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
125
104
21
57
64
65
60
120
99
21
52
64
66
54
36.3
35.0
42.9
49.1
26.2
30.8
42.4
76.8
77.9
71.4
78.9
75.0
70.8
83.3
56.7
52.5
76.2
73.1
45.3
42.4
74.1
-
-
-
-
-
-
-
397
389
435
412
381
328
470
1.96
1.81
2.68
2.20
-
-
2.38
-
-
-
-
-
-
-
352
346
390
356
351
298
392
4.69
4.66
4.87
5.93
-
-
6.06
-
-
-
-
-
-
-
266
263
278
281
252
216
333
0.758
0.705
1.07
0.858
-
-
0.855
-
-
-
-
-
-
-
0.942
0.923
1.06
0.922
0.951
0.959
0.877
1.27
1.24
1.38
1.23
-
-
1.31
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                    L-68

-------
Table L-17b.   p.p'-DDE (72-55-9):  Range of Potential Exposure in NC Preschool Children.
                Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
125
104
21
57
64
65
60
120
99
21
52
64
66
54

-------
Table L-17c.   p.p'-DDE (72-55-9): Estimates of Potential Absorbed Dose in NC Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
125
104
21
57
64
65
60
120
99
21
52
64
66
54
36.3
35.0
42.9
49.1
26.2
30.8
42.4
76.8
77.9
71.4
78.9
75.0
70.8
83.3
56.7
52.5
76.2
73.1
45.3
42.4
74.1
-
-
-
-
-
-
-
3.81
3.78
3.92
3.92
3.72
3.39
4.26
0.020
0.018
0.029
0.020
-
-
0.021
-
-
-
-
-
-
-
3.41
3.38
3.63
3.57
3.33
3.12
3.67
0.048
0.045
0.062
0.057
-
-
0.058
-
-
-
-
-
-
-
2.52
2.52
2.48
2.54
2.51
2.17
2.95
0.007
0.007
0.010
0.008
-
-
0.008
-
-
-
-
-
-
-
0.960
0.946
1.05
0.998
0.924
0.996
0.901
1.31
1.27
1.48
1.24
-
-
1.32
Potential Absorbed Dose in NC Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
125
104
21
57
64
65
60
120
99
21
52
64
66
54
36.3
35.0
42.9
49.1
26.2
30.8
42.4
76.8
77.9
71.4
78.9
75.0
70.8
83.3
56.7
52.5
76.2
73.1
45.3
42.4
74.1
-
-
-
-
-
-
-
12.0
11.9
12.3
12.3
11.7
10.7
13.4
0.061
0.055
0.090
0.063
-
-
0.067
-
-
-
-
-
-
-
10.7
10.6
11.4
11.2
10.5
9.82
11.5
0.152
0.141
0.195
0.179
-
-
0.183
-
-
-
-
-
-
-
7.91
7.93
7.81
7.99
7.91
6.82
9.28
0.023
0.021
0.030
0.024
-
-
0.024
-
-
-
-
-
-
-
0.960
0.946
1.05
0.998
0.924
0.996
0.901
1.31
1.27
1.48
1.24
-
-
1.32
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      L-70

-------
Table L-17d.   p.p'-DDE (72-55-9): Range of Potential Absorbed Dose in NC Preschool Children.
                 Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
125
104
21
57
64
65
60
120
99
21
52
64
66
54

-------
Table L-18a.   2.4-D (2.4-dichlorophenoxyacetic acid) (94-75-7): Estimates of Potential Exposure
                in NC Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Potential Exposure
-Aggregated
(ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
122
101
21
54
64
65
57
124
106
18
58
62
65
59
116
96
20
50
62
65
51
105
88
17
45
56
63
42
63.1
62.4
66.7
75.9
54.7
46.2
82.5
65.3
68.9
44.4
67.2
61.3
47.7
84.7
88.8
93.8
65.0
80.0
95.2
87.7
90.2
96.2
97.7
88.2
95.6
96.4
93.7
100.0
Potential Exposure in NC
Potential Exposure
via Inhalation
(p moles/day)
Potential Exposure
via Dietary
Ingestion
(p moles/day)
Potential Exposure
via Indirect
Ingestion
(p moles/day)
Potential Exposure
-Aggregated
(p moles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
122
101
21
54
64
65
57
124
106
18
58
62
65
59
116
96
20
50
62
65
51
105
88
17
45
56
63
42
63.1
62.4
66.7
75.9
54.7
46.2
82.5
65.3
68.9
44.4
67.2
61.3
47.7
84.7
88.8
93.8
65.0
80.0
95.2
87.7
90.2
96.2
97.7
88.2
95.6
96.4
93.7
100.0
6.30
6.59
4.89
8.54
4.63
-
9.27
271
288
-
254
284
-
305
10.1
11.9
1.52
1.02
14.2
14.4
4.62
279
298
180
265
282
264
301
Preschool Children
28.5
29.8
22.1
38.6
20.9
-
41.9
1,230
1,300
-
1,150
1,290
-
1,380
45.6
53.6
6.87
4.60
64.0
64.9
20.9
1,260
1,350
814
1,200
1,280
1,190
1,360
7.12
7.38
5.63
8.43
5.38
-
8.26
303
321
-
207
378
-
294
34.5
37.7
3.24
1.10
43.0
44.2
13.6
302
322
127
208
368
344
227
3.34
3.45
2.85
4.91
2.51
-
5.61
179
186
-
189
166
-
225
1.59
2.05
0.457
0.586
2.92
2.51
0.884
188
197
150
200
172
162
236
1.17
1.19
1.04
1.16
1.09
-
1.13
0.892
0.930
-
0.792
0.991
-
0.756
1.79
1.75
1.48
1.13
1.77
1.81
1.61
0.871
0.911
0.591
0.776
0.947
0.941
0.707
pmoles/day)
32.2
33.4
25.5
38.1
24.4
-
37.4
1,370
1,450
-
935
1,710
-
1,330
156
171
14.6
4.99
194
200
61.6
1,370
1,460
573
939
1,660
1,560
1,020
15.1
15.6
12.9
22.2
11.4
-
25.4
811
843
-
853
749
-
1,020
7.17
9.30
2.07
2.65
13.2
11.4
4.00
852
891
679
904
778
734
1,070
1.17
1.19
1.04
1.16
1.09
-
1.13
0.892
0.930
-
0.792
0.991
-
0.756
1.79
1.75
1.48
1.13
1.77
1.81
1.61
0.871
0.911
0.591
0.776
0.947
0.941
0.707
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                   L-72

-------
Table L-18b.   2.4-D (2.4-dichlorophenoxyacetic acid) (94-75-7):  Range of Potential Exposure in
                NC Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Potential Exposure
- Aggregated
(ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
122
101
21
54
64
65
57
124
106
18
58
62
65
59
116
96
20
50
62
65
51
105
88
17
45
56
63
42
Potential E
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Potential Exposure
-Aggregated
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
122
101
21
54
64
65
57
124
106
18
58
62
65
59
116
96
20
50
62
65
51
105
88
17
45
56
63
42

-------
Table L-18c.   2.4-D (2.4-dichlorophenoxyacetic acid) (94-75-7): Estimates of Potential Absorbed
                 Dose in NC Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Potential Absorbed
Dose - Aggregated
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
122
101
21
54
64
65
57
124
106
18
58
62
65
59
116
96
20
50
62
65
51
105
88
17
45
56
63
42
63.1
62.4
66.7
75.9
54.7
46.2
82.5
65.3
68.9
44.4
67.2
61.3
47.7
84.7
88.8
93.8
65.0
80.0
95.2
87.7
90.2
96.2
97.7
88.2
95.6
96.4
93.7
100.0
Potential Absorbed Dose in NC
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose - Aggregated
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
122
101
21
54
64
65
57
124
106
18
58
62
65
59
116
96
20
50
62
65
51
105
88
17
45
56
63
42
63.1
62.4
66.7
75.9
54.7
46.2
82.5
65.3
68.9
44.4
67.2
61.3
47.7
84.7
88.8
93.8
65.0
80.0
95.2
87.7
90.2
96.2
97.7
88.2
95.6
96.4
93.7
100.0
0.189
0.200
0.137
0.249
0.146
-
0.270
8.10
8.67
-
7.31
8.80
-
8.54
0.320
0.376
0.051
0.033
0.463
0.466
0.134
8.33
9.00
4.91
7.33
8.99
8.46
8.15
0.223
0.232
0.163
0.259
0.181
-
0.251
9.00
9.52
-
6.60
11.0
-
8.01
1.09
1.19
0.128
0.043
1.37
1.40
0.396
9.35
9.97
3.49
6.02
11.5
11.0
6.29
0.100
0.104
0.080
0.140
0.079
-
0.156
5.31
5.57
-
5.29
5.20
-
6.29
0.047
0.062
0.013
0.017
0.092
0.080
0.025
5.56
5.88
4.16
5.47
5.43
5.09
6.35
1.15
1.18
1.02
1.17
1.08
-
1.18
0.894
0.934
-
0.809
0.987
-
0.759
1.85
1.80
1.55
1.23
1.80
1.86
1.64
0.875
0.916
0.551
0.782
0.957
0.966
0.707
Preschool Children (pmoles/kg/day)
0.856
0.904
0.622
1.13
0.662
-
1.22
36.6
39.2
-
33.1
39.8
-
38.7
1.45
1.70
0.231
0.150
2.10
2.11
0.606
37.7
40.7
22.2
33.2
40.7
38.3
36.9
1.01
1.05
0.738
1.17
0.818
-
1.13
40.7
43.1
-
29.9
49.6
-
36.3
4.93
5.38
0.579
0.195
6.21
6.34
1.79
42.3
45.1
15.8
27.2
52.1
49.6
28.4
0.450
0.471
0.363
0.632
0.356
-
0.705
24.0
25.2
-
24.0
23.5
-
28.5
0.215
0.282
0.058
0.075
0.416
0.360
0.111
25.1
26.6
18.8
24.8
24.6
23.0
28.7
1.15
1.18
1.02
1.17
1.08
-
1.18
0.894
0.934
-
0.809
0.987
-
0.759
1.85
1.80
1.55
1.23
1.80
1.86
1.64
0.875
0.916
0.551
0.782
0.957
0.966
0.707
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                     L-74

-------
Table L-18d.    2.4-D (2.4-dichlorophenoxyacetic acid) (94-75-7):  Range of Potential Absorbed
                 Dose in NC Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Potential Absorbed
Dose - Aggregated
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
122
101
21
54
64
65
57
124
106
18
58
62
65
59
116
96
20
50
62
65
51
105
88
17
45
56
63
42

-------
Table L-19a.    Heptachlor (76-44-8):  Estimates of Potential Exposure in NC Preschool Children.
                 Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
125
104
21
57
64
65
60
119
98
21
51
64
65
54
97.6
99.0
90.5
98.2
96.9
95.4
100.0
18.4
19.2
14.3
19.3
17.2
20.0
16.7
54.6
54.1
57.1
51.0
54.7
43.1
68.5
205
182
317
215
169
195
216
-
-
-
-
-
-
-
5.32
5.18
5.96
5.38
5.15
-
5.29
400
399
394
355
345
453
337
-
-
-
-
-
-
-
13.7
14.6
8.43
9.67
16.5
-
8.73
76.4
71.7
104
87.8
66.3
57.5
104
-
-
-
-
-
-
-
0.764
0.717
1.03
0.740
0.702
-
1.10
1.39
1.25
1.92
1.43
1.31
1.53
1.14
-
-
-
-
-
-
-
2.24
2.21
2.39
2.41
2.13
-
2.22
Potential Exposure in NC Preschool Children (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
125
104
21
57
64
65
60
119
98
21
51
64
65
54
97.6
99.0
90.5
98.2
96.9
95.4
100.0
18.4
19.2
14.3
19.3
17.2
20.0
16.7
54.6
54.1
57.1
51.0
54.7
43.1
68.5
549
488
849
577
453
523
578
-
-
-
-
-
-
-
14.2
13.9
16.0
14.4
13.8
-
14.2
1,070
1,070
1,060
951
925
1,210
901
-
-
-
-
-
-
-
36.6
39.0
22.6
25.9
44.2
-
23.4
205
192
279
235
178
154
280
-
-
-
-
-
-
-
2.05
1.92
2.76
1.98
1.88
-
2.96
1.39
1.25
1.92
1.43
1.31
1.53
1.14
-
-
-
-
-
-
-
2.24
2.21
2.39
2.41
2.13
-
2.22
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                    L-76

-------
Table L-19b.   Heptachlor (76-44-8): Range of Potential Exposure in NC Preschool Children.
                Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
125
104
21
57
64
65
60
119
98
21
51
64
65
54

-------
Table L-19c.   Heptachlor (76-44-8):  Estimates of Potential Absorbed Dose in NC Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
125
104
21
57
64
65
60
119
98
21
51
64
65
54
97.6
99.0
90.5
98.2
96.9
95.4
100.0
18.4
19.2
14.3
19.3
17.2
20.0
16.7
54.6
54.1
57.1
51.0
54.7
43.1
68.5
6.37
5.91
8.64
6.39
5.98
6.55
6.18
-
-
-
-
-
-
-
0.177
0.178
0.170
0.144
0.204
-
0.143
13.8
14.4
10.7
11.0
15.5
16.5
10.2
-
-
-
-
-
-
-
0.591
0.643
0.241
0.234
0.780
-
0.211
2.28
2.17
2.93
2.51
2.07
1.83
2.91
-
-
-
-
-
-
-
0.023
0.022
0.029
0.021
0.022
-
0.031
1.39
1.27
1.90
1.44
1.33
1.54
1.17
-
-
-
-
-
-
-
2.26
2.24
2.41
2.40
2.19
-
2.21
Potential Absorbed Dose in NC Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
125
104
21
57
64
65
60
119
98
21
51
64
65
54
97.6
99.0
90.5
98.2
96.9
95.4
100.0
18.4
19.2
14.3
19.3
17.2
20.0
16.7
54.6
54.1
57.1
51.0
54.7
43.1
68.5
17.1
15.8
23.1
17.1
16.0
17.6
16.5
-
-
-
-
-
-
-
0.473
0.477
0.455
0.386
0.545
-
0.382
37.0
38.5
28.6
29.4
41.5
44.3
27.3
-
-
-
-
-
-
-
1.58
1.72
0.645
0.627
2.09
-
0.564
6.11
5.80
7.84
6.74
5.54
4.89
7.80
-
-
-
-
-
-
-
0.061
0.058
0.077
0.056
0.059
-
0.082
1.39
1.27
1.90
1.44
1.33
1.54
1.17
-
-
-
-
-
-
-
2.26
2.24
2.41
2.40
2.19
-
2.21
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      L-78

-------
Table L-19d.   Heptachlor (76-44-8): Range of Potential Absorbed Dose in NC Preschool Children.
                 Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
125
104
21
57
64
65
60
119
98
21
51
64
65
54

-------
Table L-20a.    lndenori.2.3-cc/|pvrene (193-39-5): Estimates of Potential Exposure in NC
                 Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54
75.0
75.7
71.4
87.3
64.6
64.6
86.4
0.8
0.9
0.0
1.7
0.0
0.0
1.6
100.0
100.0
100.0
100.0
100.0
100.0
100.0
1.41
1.44
1.28
1.77
1.12
1.43
1.40
-
-
-
-
-
-
-
24.6
20.8
41.7
16.8
32.4
16.1
34.3
1.49
1.51
1.40
1.61
1.35
1.71
1.21
-
-
-
-
-
-
-
65.9
39.8
131
28.0
87.5
27.3
91.6
1.000
1.01
0.928
1.30
0.795
0.949
1.06
-
-
-
-
-
-
-
9.26
9.54
8.10
8.18
10.7
8.02
10.9
0.768
0.778
0.735
0.766
0.712
0.805
0.728
-
-
-
-
-
-
-
1.20
1.14
1.45
1.17
1.23
1.11
1.29
Potential Exposure in NC Preschool Children (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54
75.0
75.7
71.4
87.3
64.6
64.6
86.4
0.8
0.9
0.0
1.7
0.0
0.0
1.6
100.0
100.0
100.0
100.0
100.0
100.0
100.0
5.12
5.22
4.62
6.41
4.04
5.17
5.06
-
-
-
-
-
-
-
88.9
75.2
151
60.9
117
58.2
124
5.38
5.46
5.08
5.84
4.89
6.20
4.37
-
-
-
-
-
-
-
239
144
474
101
317
98.8
332
3.62
3.67
3.36
4.69
2.88
3.43
3.83
-
-
-
-
-
-
-
33.5
34.5
29.3
29.6
38.8
29.0
39.5
0.768
0.778
0.735
0.766
0.712
0.805
0.728
-
-
-
-
-
-
-
1.20
1.14
1.45
1.17
1.23
1.11
1.29
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                   L-80

-------
Table L-20b.   lndenori.2.3-cc/|pvrene (193-39-5):  Range of Potential Exposure in NC Preschool
                Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54

-------
Table L-20c.   lndenori.2.3-cc/|pvrene (193-39-5):  Estimates of Potential Absorbed Dose in NC
                 Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54
75.0
75.7
71.4
87.3
64.6
64.6
86.4
0.8
0.9
0.0
1.7
0.0
0.0
1.6
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.045
0.047
0.035
0.055
0.037
0.050
0.039
-
-
-
-
-
-
-
0.765
0.636
1.35
0.500
1.03
0.558
1.00
0.059
0.063
0.036
0.072
0.047
0.076
0.033
-
-
-
-
-
-
-
2.07
1.20
4.17
0.850
2.75
1.00
2.83
0.030
0.031
0.026
0.037
0.025
0.030
0.030
-
-
-
-
-
-
-
0.274
0.286
0.227
0.231
0.333
0.252
0.302
0.807
0.826
0.711
0.818
0.775
0.857
0.756
-
-
-
-
-
-
-
1.25
1.18
1.57
1.22
1.27
1.19
1.32
Potential Absorbed Dose in NC Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54
75.0
75.7
71.4
87.3
64.6
64.6
86.4
0.8
0.9
0.0
1.7
0.0
0.0
1.6
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.162
0.169
0.127
0.200
0.133
0.180
0.143
-
-
-
-
-
-
-
2.77
2.30
4.88
1.81
3.73
2.02
3.63
0.215
0.228
0.130
0.261
0.169
0.273
0.120
-
-
-
-
-
-
-
7.48
4.34
15.1
3.07
9.94
3.62
10.2
0.108
0.111
0.094
0.134
0.090
0.109
0.107
-
-
-
-
-
-
-
0.992
1.03
0.823
0.835
1.21
0.911
1.09
0.807
0.826
0.711
0.818
0.775
0.857
0.756
-
-
-
-
-
-
-
1.25
1.18
1.57
1.22
1.27
1.19
1.32
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected.  Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      L-82

-------
Table L-20d.    lndenori.2.3-cc/|pvrene (193-39-5): Range of Potential Absorbed Dose in NC
                 Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
128
107
21
58
66
66
62
116
95
21
52
60
62
54

-------
Table L-21a.    Pentachlorophenol (87-86-5): Estimates of Potential Exposure in NC Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
122
101
21
54
64
65
57
124
106
18
58
62
65
59
117
96
21
50
63
65
52
99.2
99.0
100.0
100.0
98.4
98.5
100.0
15.3
17.0
5.6
15.5
16.1
9.2
22.0
96.6
96.9
95.2
100.0
93.7
93.8
100.0
26.1
21.1
50.2
26.6
26.6
22.9
29.8
-
-
-
-
-
-
-
7.42
7.48
7.17
7.77
7.46
8.02
6.68
41.5
28.1
75.8
32.7
48.9
40.3
42.9
-
-
-
-
-
-
-
12.1
12.4
11.2
12.6
12.2
13.0
11.0
13.9
12.8
20.9
17.9
11.5
10.8
18.6
-
-
-
-
-
-
-
3.31
3.26
3.54
3.42
3.30
3.54
3.03
1.03
0.956
1.29
0.846
1.16
1.10
0.871
-
-
-
-
-
-
-
1.29
1.32
1.12
1.33
1.29
1.28
1.30
Potential Exposure in NC Preschool Children (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
122
101
21
54
64
65
57
124
106
18
58
62
65
59
117
96
21
50
63
65
52
99.2
99.0
100.0
100.0
98.4
98.5
100.0
15.3
17.0
5.6
15.5
16.1
9.2
22.0
96.6
96.9
95.2
100.0
93.7
93.8
100.0
98.0
79.2
188
99.8
00.0
85.9
112
-
-
-
-
-
-
-
27.9
28.1
26.9
29.2
28.0
30.1
25.1
156
105
284
123
184
151
161
-
-
-
-
-
-
-
45.5
46.4
42.0
47.2
45.7
48.7
41.5
52.3
48.0
78.6
67.2
43.1
40.6
69.7
-
-
-
-
-
-
-
12.4
12.2
13.3
12.8
12.4
13.3
11.4
1.03
0.956
1.29
0.846
1.16
1.10
0.871
-
-
-
-
-
-
-
1.29
1.32
1.12
1.33
1.29
1.28
1.30
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                   L-84

-------
Table L-21b.   Pentachlorophenol (87-86-5): Range of Potential Exposure in NC Preschool
                Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
122
101
21
54
64
65
57
124
106
18
58
62
65
59
117
96
21
50
63
65
52

-------
Table L-21c.   Pentachlorophenol (87-86-5):  Estimates of Potential Absorbed Dose in NC
                 Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
122
101
21
54
64
65
57
124
106
18
58
62
65
59
117
96
21
50
63
65
52
99.2
99.0
100.0
100.0
98.4
98.5
100.0
15.3
17.0
5.6
15.5
16.1
9.2
22.0
96.6
96.9
95.2
100.0
93.7
93.8
100.0
0.799
0.675
1.40
0.816
0.816
0.746
0.860
-
-
-
-
-
-
-
0.221
0.222
0.217
0.222
0.230
0.250
0.185
1.26
0.980
2.10
1.08
1.44
1.29
1.24
-
-
-
-
-
-
-
0.332
0.331
0.346
0.349
0.329
0.369
0.279
0.416
0.387
0.588
0.509
0.359
0.344
0.516
-
-
-
-
-
-
-
0.099
0.099
0.099
0.097
0.104
0.112
0.085
1.04
0.974
1.26
0.908
1.13
1.11
0.909
-
-
-
-
-
-
-
1.32
1.35
1.19
1.35
1.32
1.30
1.33
Potential Absorbed Dose in NC Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
122
101
21
54
64
65
57
124
106
18
58
62
65
59
117
96
21
50
63
65
52
99.2
99.0
100.0
100.0
98.4
98.5
100.0
15.3
17.0
5.6
15.5
16.1
9.2
22.0
96.6
96.9
95.2
100.0
93.7
93.8
100.0
3.00
2.53
5.25
3.06
3.07
2.80
3.23
-
-
-
-
-
-
-
0.831
0.834
0.815
0.832
0.865
0.939
0.695
4.74
3.68
7.87
4.04
5.40
4.84
4.65
-
-
-
-
-
-
-
1.25
1.24
1.30
1.31
1.24
1.39
1.05
1.56
1.45
2.21
1.91
1.35
1.29
1.94
-
-
-
-
-
-
-
0.372
0.371
0.373
0.365
0.390
0.422
0.317
1.04
0.974
1.26
0.908
1.13
1.11
0.909
-
-
-
-
-
-
-
1.32
1.35
1.19
1.35
1.32
1.30
1.33
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      L-86

-------
Table L-21d.    Pentachlorophenol (87-86-5): Range of Potential Absorbed Dose in NC Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
122
101
21
54
64
65
57
124
106
18
58
62
65
59
117
96
21
50
63
65
52

-------
Table L-22a.    c/s-Permethrin (61949-76-6):  Estimates of Potential Exposure in NC Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Potential Exposure
-Aggregated
(ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
122
102
20
56
62
63
59
120
99
21
52
64
66
54
109
89
20
45
60
62
47
75.8
72.8
90.5
92.7
61.5
61.5
91.5
60.7
63.7
45.0
64.3
56.5
50.8
71.2
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
Potential Exposure in NC
Potential Exposure
via Inhalation
(p moles/day)
Potential Exposure
via Dietary
Ingestion
(p moles/day)
Potential Exposure
via Indirect
Ingestion
(p moles/day)
Potential Exposure
-Aggregated
(p moles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
122
102
20
56
62
63
59
120
99
21
52
64
66
54
109
89
20
45
60
62
47
75.8
72.8
90.5
92.7
61.5
61.5
91.5
60.7
63.7
45.0
64.3
56.5
50.8
71.2
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
13.2
13.0
13.9
22.4
5.88
9.35
17.3
2,870
3,360
-
5,430
677
621
5,270
220
209
271
118
314
233
203
3,290
3,880
656
6,510
1,030
867
6,490
Preschool Children
33.6
33.2
35.5
57.2
15.0
23.9
44.3
7,330
8,590
-
13,900
1,730
1,590
13,500
561
534
692
301
803
596
519
8,410
9,930
1,680
16,600
2,630
2,220
16,600
28.5
29.4
24.8
39.9
9.38
17.5
36.8
14,200
15,500
-
20,700
1,570
1,560
20,100
670
601
946
181
895
721
608
15,000
16,500
1,240
22,900
1,760
1,690
22,400
4.17
3.88
5.86
8.11
2.43
3.13
5.71
132
142
-
151
114
88.8
200
48.4
47.4
53.3
58.1
43.6
44.1
54.3
306
329
218
322
298
224
460
1.46
1.49
1.26
1.43
1.27
1.45
1.42
1.97
2.03
-
2.13
1.83
1.83
2.04
1.57
1.62
1.36
1.19
1.85
1.62
1.52
1.71
1.77
1.41
1.85
1.62
1.57
1.82
pmoles/day)
72.9
75.0
63.3
102
24.0
44.8
94.1
36,200
39,500
-
52,800
4,030
3,990
51,500
1,710
1,540
2,420
464
2,290
1,840
1,550
38,200
42,200
3,180
58,600
4,510
4,330
57,300
10.6
9.93
15.0
20.7
6.20
8.00
14.6
336
364
-
387
290
227
512
124
121
136
149
111
113
139
781
842
558
824
761
573
1,180
1.46
1.49
1.26
1.43
1.27
1.45
1.42
1.97
2.03
-
2.13
1.83
1.83
2.04
1.57
1.62
1.36
1.19
1.85
1.62
1.52
1.71
1.77
1.41
1.85
1.62
1.57
1.82
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected.  Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                    L-8

-------
Table L-22b.   c/s-Permethrin (61949-76-6):  Range of Potential Exposure in NC Preschool
                Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Potential Exposure
- Aggregated
(ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
122
102
20
56
62
63
59
120
99
21
52
64
66
54
109
89
20
45
60
62
47
Potential E
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Potential Exposure
-Aggregated
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
122
102
20
56
62
63
59
120
99
21
52
64
66
54
109
89
20
45
60
62
47

-------
Table L-22c.   c/s-Permethrin (61949-76-6):  Estimates of Potential Absorbed Dose in NC
                 Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Potential Absorbed
Dose - Aggregated
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
122
102
20
56
62
63
59
120
99
21
52
64
66
54
109
89
20
45
60
62
47
Potential Absor
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose - Aggregated
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
122
102
20
56
62
63
59
120
99
21
52
64
66
54
109
89
20
45
60
62
47
75.8
72.8
90.5
92.7
61.5
61.5
91.5
60.7
63.7
45.0
64.3
56.5
50.8
71.2
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
bed Dose in NC
75.8
72.8
90.5
92.7
61.5
61.5
91.5
60.7
63.7
45.0
64.3
56.5
50.8
71.2
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.400
0.407
0.364
0.676
0.184
0.313
0.495
80.9
94.7
-
148
23.5
20.1
146
6.90
6.76
7.56
3.47
10.1
7.70
5.92
92.5
109
18.6
175
34.8
28.3
177
0.907
0.957
0.623
1.28
0.296
0.671
1.11
391
427
-
570
58.0
51.9
555
20.9
19.8
26.1
5.25
27.9
23.7
16.9
412
454
34.8
631
63.3
56.6
617
0.124
0.117
0.165
0.232
0.076
0.099
0.159
3.92
4.29
-
4.31
3.55
2.81
5.60
1.44
1.43
1.50
1.64
1.37
1.40
1.50
9.08
9.91
6.17
9.06
9.31
7.11
12.5
1.45
1.49
1.21
1.44
1.28
1.43
1.44
1.96
2.02
-
2.09
1.85
1.85
2.02
1.62
1.67
1.37
1.22
1.90
1.65
1.59
1.71
1.77
1.41
1.80
1.66
1.60
1.82
Preschool Children (pmoles/kg/day)
1.02
1.04
0.930
1.73
0.470
0.799
1.27
207
242
-
379
60.0
51.3
372
17.6
17.3
19.3
8.87
25.7
19.7
15.1
236
279
47.5
448
88.9
72.4
453
2.32
2.45
1.59
3.26
0.755
1.71
2.84
1,000
1,090
-
1,460
148
133
1,420
53.3
50.5
66.6
13.4
71.3
60.6
43.3
1,050
1,160
88.8
1,610
162
145
1,580
0.318
0.300
0.421
0.593
0.193
0.254
0.406
10.0
11.0
-
11.0
9.08
7.18
14.3
3.69
3.66
3.82
4.19
3.50
3.57
3.84
23.2
25.3
15.8
23.1
23.8
18.2
32.0
1.45
1.49
1.21
1.44
1.28
1.43
1.44
1.96
2.02
-
2.09
1.85
1.85
2.02
1.62
1.67
1.37
1.22
1.90
1.65
1.59
1.71
1.77
1.41
1.80
1.66
1.60
1.82
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      L-90

-------
Table L-22d.    c/s-Permethrin (61949-76-6):  Range of Potential Absorbed Dose in NC Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Potential Absorbed
Dose - Aggregated
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
122
102
20
56
62
63
59
120
99
21
52
64
66
54
109
89
20
45
60
62
47

-------
Table L-23a.    frans-Permethrin (61949-77-7):  Estimates of Potential Exposure in NC Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Potential Exposure
-Aggregated
(ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
119
100
19
53
62
63
56
120
99
21
52
64
66
54
106
87
19
42
60
62
44
75.0
71.8
90.5
92.7
61.5
60.0
91.5
59.7
63.0
42.1
62.3
56.5
50.8
69.6
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
Potential Exposure in NC
Potential Exposure
via Inhalation
(p moles/day)
Potential Exposure
via Dietary
Ingestion
(p moles/day)
Potential Exposure
via Indirect
Ingestion
(p moles/day)
Potential Exposure
-Aggregated
(p moles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
119
100
19
53
62
63
56
120
99
21
52
64
66
54
106
87
19
42
60
62
44
75.0
71.8
90.5
92.7
61.5
60.0
91.5
59.7
63.0
42.1
62.3
56.5
50.8
69.6
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
11.8
11.7
12.2
20.4
5.03
8.35
15.6
1,580
1,830
-
2,930
493
491
2,810
222
211
272
112
323
236
204
1,870
2,160
562
3,440
848
739
3,460
Preschool Children
30.1
29.9
31.3
52.1
12.9
21.3
39.7
4,050
4,690
-
7,480
1,260
1,250
7,190
566
539
695
286
825
603
522
4,780
5,510
1,440
8,800
2,170
1,890
8,850
29.4
30.5
24.1
41.8
8.81
17.1
38.6
8,310
9,050
-
12,300
1,120
1,240
12,000
698
627
983
176
934
755
627
8,720
9,600
1,150
13,700
1,430
1,440
13,400
3.31
3.09
4.58
6.32
1.98
2.47
4.56
111
120
-
125
98.7
81.7
157
42.7
42.2
45.0
47.0
41.2
38.6
48.3
252
274
172
243
262
200
349
1.46
1.49
1.34
1.47
1.26
1.47
1.40
1.80
1.85
-
1.93
1.69
1.73
1.83
1.67
1.72
1.42
1.32
1.93
1.70
1.63
1.60
1.63
1.44
1.70
1.55
1.54
1.65
pmoles/day)
75.2
78.0
61.5
107
22.5
43.7
98.6
21,200
23,100
-
31 ,500
2,860
3,160
30,600
1,780
1,600
2,510
450
2,390
1,930
1,600
22,300
24,500
2,930
35,000
3,650
3,680
34,100
8.45
7.91
11.7
16.2
5.05
6.31
11.7
284
306
-
318
252
209
401
109
108
115
120
105
98.7
123
644
700
440
620
669
511
892
1.46
1.49
1.34
1.47
1.26
1.47
1.40
1.80
1.85
-
1.93
1.69
1.73
1.83
1.67
1.72
1.42
1.32
1.93
1.70
1.63
1.60
1.63
1.44
1.70
1.55
1.54
1.65
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                   L-92

-------
Table L-23b.   frans-Permethrin (61949-77-7):  Range of Potential Exposure in NC Preschool
                Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Potential Exposure
- Aggregated
(ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
119
100
19
53
62
63
56
120
99
21
52
64
66
54
106
87
19
42
60
62
44
Potential E
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Potential Exposure
-Aggregated
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
119
100
19
53
62
63
56
120
99
21
52
64
66
54
106
87
19
42
60
62
44

-------
Table L-23c.   frans-Permethrin (61949-77-7): Estimates of Potential Absorbed Dose in NC
                 Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Potential Absorbed
Dose - Aggregated
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
119
100
19
53
62
63
56
120
99
21
52
64
66
54
106
87
19
42
60
62
44
Potential Absor
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose - Aggregated
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
119
100
19
53
62
63
56
120
99
21
52
64
66
54
106
87
19
42
60
62
44
75.0
71.8
90.5
92.7
61.5
60.0
91.5
59.7
63.0
42.1
62.3
56.5
50.8
69.6
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
bed Dose in NC
75.0
71.8
90.5
92.7
61.5
60.0
91.5
59.7
63.0
42.1
62.3
56.5
50.8
69.6
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.366
0.374
0.322
0.633
0.157
0.285
0.455
44.4
51.5
-
78.1
17.3
15.7
76.8
7.02
6.90
7.58
3.38
10.4
7.88
5.96
52.4
60.4
15.8
89.4
28.7
24.1
92.3
0.978
1.04
0.614
1.40
0.276
0.670
1.23
225
245
-
333
42.3
39.4
324
21.9
20.7
27.1
5.24
29.2
25.0
17.4
235
259
31.8
368
51.0
46.9
359
0.099
0.094
0.129
0.181
0.062
0.078
0.127
3.32
3.61
-
3.56
3.09
2.59
4.40
1.27
1.27
1.26
1.33
1.29
1.22
1.34
7.52
8.27
4.85
6.85
8.19
6.35
9.54
1.46
1.49
1.29
1.49
1.26
1.46
1.42
1.79
1.84
-
1.89
1.72
1.75
1.81
1.72
1.78
1.46
1.38
1.98
1.74
1.70
1.61
1.64
1.45
1.65
1.60
1.57
1.66
Preschool Children (pmoles/kg/day)
0.934
0.957
0.823
1.62
0.402
0.727
1.16
114
131
-
200
44.2
40.1
196
17.9
17.6
19.4
8.63
26.5
20.2
15.2
134
154
40.5
228
73.4
61.5
236
2.50
2.65
1.57
3.57
0.704
1.71
3.15
576
627
-
851
108
101
828
55.8
53.0
69.2
13.4
74.7
63.9
44.6
601
661
81.3
940
130
120
918
0.252
0.239
0.328
0.462
0.158
0.200
0.325
8.49
9.24
-
9.11
7.89
6.61
11.2
3.25
3.26
3.23
3.39
3.31
3.13
3.41
19.2
21.1
12.4
17.5
20.9
16.2
24.4
1.46
1.49
1.29
1.49
1.26
1.46
1.42
1.79
1.84
-
1.89
1.72
1.75
1.81
1.72
1.78
1.46
1.38
1.98
1.74
1.70
1.61
1.64
1.45
1.65
1.60
1.57
1.66
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      L-94

-------
Table L-23d.    frans-Permethrin (61949-77-7):  Range of Potential Absorbed Dose in NC Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Potential Absorbed
Dose - Aggregated
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
119
100
19
53
62
63
56
120
99
21
52
64
66
54
106
87
19
42
60
62
44

-------
Table L-24a.    PCB 52 (35693-99-3):  Estimates of Potential Exposure in NC Preschool Children.
                 Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
120
99
21
52
64
65
55
120
99
21
52
64
66
54
97.6
97.1
100.0
100.0
98.5
95.4
100.0
10.8
10.1
14.3
17.3
4.7
4.6
18.2
45.8
47.5
38.1
46.2
46.9
27.3
68.5
6.28
6.28
6.27
7.67
5.36
4.66
8.06
-
-
-
-
-
-
-
-
-
-
-
-
-
0.491
9.18
9.60
6.95
13.0
3.82
4.30
12.3
-
-
-
-
-
-
-
-
-
-
-
-
-
0.691
4.33
4.27
4.63
4.56
4.40
3.76
5.05
-
-
-
-
-
-
-
-
-
-
-
-
-
0.249
0.795
0.816
0.699
0.929
0.627
0.636
0.921
-
-
-
-
-
-
-
-
-
-
-
-
-
1.19
Potential Exposure in NC Preschool Children (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
120
99
21
52
64
65
55
120
99
21
52
64
66
54
97.6
97.1
100.0
100.0
98.5
95.4
100.0
10.8
10.1
14.3
17.3
4.7
4.6
18.2
45.8
47.5
38.1
46.2
46.9
27.3
68.5
21.5
21.5
21.5
26.3
18.4
16.0
27.6
-
-
-
-
-
-
-
-
-
-
-
-
-
1.68
31.4
32.9
23.8
44.7
13.1
14.7
42.3
-
-
-
-
-
-
-
-
-
-
-
-
-
2.37
14.8
14.6
15.8
15.6
15.1
12.9
17.3
-
-
-
-
-
-
-
-
-
-
-
-
-
0.854
0.795
0.816
0.699
0.929
0.627
0.636
0.921
-
-
-
-
-
-
-
-
-
-
-
-
-
1.19
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                    L-96

-------
Table L-24b.   PCB 52 (35693-99-3):  Range of Potential Exposure in NC Preschool Children.
                Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
120
99
21
52
64
65
55
120
99
21
52
64
66
54

-------
Table L-24c.   PCB 52 (35693-99-3):  Estimates of Potential Absorbed Dose in NC Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
120
99
21
52
64
65
55
120
99
21
52
64
66
54
97.6
97.1
100.0
100.0
98.5
95.4
100.0
10.8
10.1
14.3
17.3
4.7
4.6
18.2
45.8
47.5
38.1
46.2
46.9
27.3
68.5
0.195
0.200
0.171
0.240
0.166
0.147
0.247
-
-
-
-
-
-
-
-
-
-
-
-
-
0.015
0.340
0.366
0.163
0.493
0.115
0.108
0.476
-
-
-
-
-
-
-
-
-
-
-
-
-
0.025
0.129
0.129
0.130
0.130
0.137
0.119
0.141
-
-
-
-
-
-
-
-
-
-
-
-
-
0.007
0.827
0.855
0.693
0.986
0.622
0.676
0.965
-
-
-
-
-
-
-
-
-
-
-
-
-
1.24
Potential Absorbed Dose in NC Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
120
99
21
52
64
65
55
120
99
21
52
64
66
54
97.6
97.1
100.0
100.0
98.5
95.4
100.0
10.8
10.1
14.3
17.3
4.7
4.6
18.2
45.8
47.5
38.1
46.2
46.9
27.3
68.5
0.668
0.685
0.586
0.821
0.570
0.505
0.847
-
-
-
-
-
-
-
-
-
-
-
-
-
0.051
1.16
1.25
0.557
1.69
0.394
0.369
1.63
-
-
-
-
-
-
-
-
-
-
-
-
-
0.085
0.442
0.442
0.445
0.447
0.470
0.409
0.482
-
-
-
-
-
-
-
-
-
-
-
-
-
0.024
0.827
0.855
0.693
0.986
0.622
0.676
0.965
-
-
-
-
-
-
-
-
-
-
-
-
-
1.24
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      L-98

-------
Table L-24d.    PCB 52 (35693-99-3):  Range of Potential Absorbed Dose in NC Preschool Children.
                 Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
120
99
21
52
64
65
55
120
99
21
52
64
66
54

-------
Table L-25a.    PCB 95 (38379-99-6):  Estimates of Potential Exposure in NC Preschool Children.
                 Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
120
99
21
52
64
65
55
120
99
21
52
64
66
54
87.1
88.3
81.0
90.9
89.2
76.9
98.3
3.3
2.0
9.5
3.8
3.1
4.6
1.8
48.3
47.5
52.4
51.9
45.3
36.4
63.0
1.30
1.22
1.74
1.76
0.981
1.06
1.58
-
-
-
-
-
-
-
-
-
0.573
0.269
-
-
0.325
2.89
2.73
3.63
4.16
1.06
2.07
3.58
-
-
-
-
-
-
-
-
-
1.51
0.402
-
-
0.594
0.778
0.777
0.784
0.878
0.742
0.698
0.877
-
-
-
-
-
-
-
-
-
0.178
0.138
-
-
0.158
0.811
0.759
1.05
0.934
0.678
0.740
0.873
-
-
-
-
-
-
-
-
-
1.26
1.08
-
-
1.08
Potential Exposure in NC Preschool Children (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
120
99
21
52
64
65
55
120
99
21
52
64
66
54
87.1
88.3
81.0
90.9
89.2
76.9
98.3
3.3
2.0
9.5
3.8
3.1
4.6
1.8
48.3
47.5
52.4
51.9
45.3
36.4
63.0
3.99
3.72
5.32
5.38
3.00
3.23
4.83
-
-
-
-
-
-
-
-
-
1.76
0.824
-
-
0.995
8.85
8.35
11.1
12.7
3.25
6.35
11.0
-
-
-
-
-
-
-
-
-
4.62
1.23
-
-
1.82
2.38
2.38
2.40
2.69
2.27
2.14
2.69
-
-
-
-
-
-
-
-
-
0.544
0.423
-
-
0.483
0.811
0.759
1.05
0.934
0.678
0.740
0.873
-
-
-
-
-
-
-
-
-
1.26
1.08
-
-
1.08
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected.  Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                   L-100

-------
Table L-25b.   PCB 95 (38379-99-6):  Range of Potential Exposure in NC Preschool Children.
                Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
120
99
21
52
64
65
55
120
99
21
52
64
66
54

-------
Table L-25c.   PCB 95 (38379-99-6):  Estimates of Potential Absorbed Dose in NC Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
120
99
21
52
64
65
55
120
99
21
52
64
66
54
87.1
88.3
81.0
90.9
89.2
76.9
98.3
3.3
2.0
9.5
3.8
3.1
4.6
1.8
48.3
47.5
52.4
51.9
45.3
36.4
63.0
0.040
0.040
0.044
0.054
0.031
0.032
0.050
-
-
-
-
-
-
-
-
-
0.020
0.008
-
-
0.010
0.101
0.106
0.076
0.147
0.033
0.044
0.139
-
-
-
-
-
-
-
-
-
0.061
0.013
-
-
0.018
0.023
0.023
0.022
0.025
0.023
0.022
0.024
-
-
-
-
-
-
-
-
-
0.005
0.004
-
-
0.004
0.852
0.812
1.05
0.977
0.714
0.770
0.938
-
-
-
-
-
-
-
-
-
1.33
1.16
-
-
1.12
Potential Absorbed Dose in NC Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
120
99
21
52
64
65
55
120
99
21
52
64
66
54
87.1
88.3
81.0
90.9
89.2
76.9
98.3
3.3
2.0
9.5
3.8
3.1
4.6
1.8
48.3
47.5
52.4
51.9
45.3
36.4
63.0
0.124
0.122
0.135
0.165
0.095
0.097
0.154
-
-
-
-
-
-
-
-
-
0.061
0.025
-
-
0.029
0.310
0.324
0.234
0.451
0.100
0.134
0.427
-
-
-
-
-
-
-
-
-
0.188
0.041
-
-
0.056
0.071
0.072
0.067
0.077
0.071
0.068
0.075
-
-
-
-
-
-
-
-
-
0.015
0.012
-
-
0.013
0.852
0.812
1.05
0.977
0.714
0.770
0.938
-
-
-
-
-
-
-
-
-
1.33
1.16
-
-
1.12
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                     L-102

-------
Table L-25d.    PCB 95 (38379-99-6):  Range of Potential Absorbed Dose in NC Preschool Children.
                 Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
120
99
21
52
64
65
55
120
99
21
52
64
66
54

-------
Table L-26a.    PCB 101  (37680-73-2):  Estimates of Potential Exposure in NC Preschool Children.
                 Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
120
99
21
52
64
65
55
120
99
21
52
64
66
54
73.4
73.8
71.4
80.0
72.3
61.5
86.4
0.0
0.0
0.0
0.0
0.0
0.0
0.0
49.2
48.5
52.4
50.0
48.4
36.4
64.8
1.12
1.00
1.71
1.50
0.851
0.972
1.29
-
-
-
-
-
-
-
-
-
0.614
0.306
-
-
0.407
2.53
2.16
3.89
3.60
1.06
2.24
2.82
-
-
-
-
-
-
-
-
-
1.51
0.468
-
-
0.813
0.617
0.605
0.684
0.684
0.593
0.570
0.674
-
-
-
-
-
-
-
-
-
0.199
0.150
-
-
0.174
0.886
0.832
1.13
1.01
0.774
0.832
0.941
-
-
-
-
-
-
-
-
-
1.30
1.14
-
-
1.18
Potential Exposure in NC Preschool Children (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
120
99
21
52
64
65
55
120
99
21
52
64
66
54
73.4
73.8
71.4
80.0
72.3
61.5
86.4
0.0
0.0
0.0
0.0
0.0
0.0
0.0
49.2
48.5
52.4
50.0
48.4
36.4
64.8
3.43
3.07
5.24
4.60
2.61
2.98
3.94
-
-
-
-
-
-
-
-
-
1.88
0.938
-
-
1.25
7.75
6.61
11.9
11.0
3.26
6.86
8.65
-
-
-
-
-
-
-
-
-
4.63
1.43
-
-
2.49
1.89
1.85
2.09
2.10
1.82
1.75
2.07
-
-
-
-
-
-
-
-
-
0.610
0.459
-
-
0.534
0.886
0.832
1.13
1.01
0.774
0.832
0.941
-
-
-
-
-
-
-
-
-
1.30
1.14
-
-
1.18
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected.  Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                   L-104

-------
Table L-26b.   PCB 101 (37680-73-2): Range of Potential Exposure in NC Preschool Children.
                Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
120
99
21
52
64
65
55
120
99
21
52
64
66
54

-------
Table L-26c.   PCB 101 (37680-73-2):  Estimates of Potential Absorbed Dose in NC Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
120
99
21
52
64
65
55
120
99
21
52
64
66
54
73.4
73.8
71.4
80.0
72.3
61.5
86.4
0.0
0.0
0.0
0.0
0.0
0.0
0.0
49.2
48.5
52.4
50.0
48.4
36.4
64.8
0.034
0.032
0.043
0.045
0.027
0.028
0.041
-
-
-
-
-
-
-
-
-
0.021
0.009
-
-
0.012
0.082
0.083
0.081
0.118
0.033
0.047
0.109
-
-
-
-
-
-
-
-
-
0.061
0.015
-
-
0.024
0.018
0.018
0.019
0.020
0.018
0.018
0.019
-
-
-
-
-
-
-
-
-
0.006
0.004
-
-
0.005
0.911
0.865
1.13
1.05
0.783
0.829
1.000
-
-
-
-
-
-
-
-
-
1.37
1.22
-
-
1.21
Potential Absorbed Dose in NC Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
120
99
21
52
64
65
55
120
99
21
52
64
66
54
73.4
73.8
71.4
80.0
72.3
61.5
86.4
0.0
0.0
0.0
0.0
0.0
0.0
0.0
49.2
48.5
52.4
50.0
48.4
36.4
64.8
0.105
0.100
0.131
0.138
0.082
0.087
0.125
-
-
-
-
-
-
-
-
-
0.065
0.029
-
-
0.036
0.252
0.254
0.247
0.361
0.100
0.145
0.332
-
-
-
-
-
-
-
-
-
0.188
0.047
-
-
0.075
0.056
0.056
0.059
0.060
0.057
0.055
0.058
-
-
-
-
-
-
-
-
-
0.017
0.013
-
-
0.015
0.911
0.865
1.13
1.05
0.783
0.829
1.000
-
-
-
-
-
-
-
-
-
1.37
1.22
-
-
1.21
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                     L-106

-------
Table L-26d.    PCB 101 (37680-73-2):  Range of Potential Absorbed Dose in NC Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
103
21
55
65
65
59
120
99
21
52
64
65
55
120
99
21
52
64
66
54

-------
Table L-27a.    3.5.6-TCP (3.5.6-trichloro-2-pyridinol) (6515-38-4):  Estimates of Potential Exposure
                 in NC Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Potential Exposure
-Aggregated
(ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
123
102
21
55
64
65
58
128
107
21
58
66
66
62
120
99
21
52
64
66
54
113
92
21
47
62
65
48
100.0
100.0
100.0
100.0
100.0
100.0
100.0
99.2
99.1
100.0
100.0
98.5
98.5
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
Potential Exposure in NC
Potential Exposure
via Inhalation
(p moles/day)
Potential Exposure
via Dietary
Ingestion
(p moles/day)
Potential Exposure
via Indirect
Ingestion
(p moles/day)
Potential Exposure
-Aggregated
(p moles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
123
102
21
55
64
65
58
128
107
21
58
66
66
62
120
99
21
52
64
66
54
113
92
21
47
62
65
48
100.0
100.0
100.0
100.0
100.0
100.0
100.0
99.2
99.1
100.0
100.0
98.5
98.5
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
32.1
33.1
27.5
36.1
29.6
27.6
37.2
1,440
1,480
1,240
1,110
1,710
1,290
1,600
13.1
10.6
25.1
14.1
11.5
14.8
11.1
1,480
1,530
1,300
1,160
1,720
1,340
1,670
Preschool Children
162
167
139
182
149
139
187
7,260
7,450
6,260
5,600
8,630
6,490
8,070
66.2
53.4
127
71.0
58.2
74.8
55.8
7,480
7,700
6,530
5,830
8,640
6,780
8,440
67.6
72.4
37.0
80.7
56.9
56.9
78.1
994
1,050
580
648
1,160
1,120
814
28.4
23.6
43.4
28.8
27.5
33.9
19.7
1,010
1,090
562
680
1,160
1,130
803
15.3
15.2
15.5
16.6
14.2
13.0
18.3
1,060
1,050
1,090
832
1,280
857
1,320
4.46
4.07
6.92
4.93
3.86
4.73
4.15
1,110
1,100
1,160
869
1,310
933
1,400
1.11
1.11
1.12
1.11
1.14
1.13
1.06
0.935
0.994
0.559
0.935
0.904
1.05
0.736
1.43
1.35
1.71
1.44
1.41
1.47
1.39
0.887
0.955
0.506
0.921
0.836
0.970
0.705
pmoles/day)
341
365
186
406
287
287
394
5,010
5,310
2,920
3,270
5,840
5,660
4,100
143
119
219
145
139
171
99.2
5,110
5,480
2,830
3,420
5,870
5,700
4,050
77.0
76.7
78.2
83.5
71.4
65.4
92.4
5,330
5,290
5,510
4,190
6,450
4,320
6,660
22.5
20.5
34.9
24.9
19.5
23.8
20.9
5,600
5,540
5,860
4,380
6,600
4,700
7,080
1.11
1.11
1.12
1.11
1.14
1.13
1.06
0.935
0.994
0.559
0.935
0.904
1.05
0.736
1.43
1.35
1.71
1.44
1.41
1.47
1.39
0.887
0.955
0.506
0.921
0.836
0.970
0.705
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected.  Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                   L-108

-------
Table L-27b.   3.5.6-TCP (3.5.6-trichloro-2-pyridinol) (6515-38-4):  Range of Potential Exposure in
                NC Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Potential Exposure
- Aggregated
(ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
123
102
21
55
64
65
58
128
107
21
58
66
66
62
120
99
21
52
64
66
54
113
92
21
47
62
65
48
Potential E
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Potential Exposure
-Aggregated
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
123
102
21
55
64
65
58
128
107
21
58
66
66
62
120
99
21
52
64
66
54
113
92
21
47
62
65
48
1.29
1.29
2.00
2.16
1.29
1.29
2.00

-------
Table L-27c.   3.5.6-TCP (3.5.6-trichloro-2-pyridinol) (6515-38-4):  Estimates of Potential Absorbed
                 Dose in NC Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Potential Absorbed
Dose - Aggregated
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
123
102
21
55
64
65
58
128
107
21
58
66
66
62
120
99
21
52
64
66
54
113
92
21
47
62
65
48
100.0
100.0
100.0
100.0
100.0
100.0
100.0
99.2
99.1
100.0
100.0
98.5
98.5
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
Potential Absorbed Dose in NC
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose - Aggregated
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
123
102
21
55
64
65
58
128
107
21
58
66
66
62
120
99
21
52
64
66
54
113
92
21
47
62
65
48
100.0
100.0
100.0
100.0
100.0
100.0
100.0
99.2
99.1
100.0
100.0
98.5
98.5
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.971
1.02
0.730
1.08
0.911
0.837
1.12
42.4
43.9
34.8
31.7
51.8
40.5
44.4
0.398
0.325
0.742
0.399
0.376
0.466
0.314
43.8
45.6
36.2
32.5
52.4
42.3
45.9
2.10
2.26
0.943
2.57
1.68
1.64
2.52
29.9
31.6
16.9
18.9
34.9
36.5
20.8
0.865
0.729
1.30
0.840
0.879
1.06
0.542
30.9
33.2
16.3
19.5
35.7
36.7
21.0
0.457
0.461
0.436
0.474
0.444
0.412
0.513
31.7
31.8
30.7
23.9
40.1
27.2
37.3
0.133
0.123
0.194
0.139
0.122
0.150
0.115
33.3
33.4
32.7
24.7
41.2
29.7
38.9
1.11
1.12
1.06
1.13
1.13
1.10
1.12
0.900
0.957
0.529
0.902
0.845
1.03
0.704
1.44
1.37
1.73
1.44
1.46
1.46
1.43
0.851
0.916
0.479
0.881
0.778
0.945
0.681
Preschool Children (pmoles/kg/day)
4.89
5.14
3.68
5.42
4.59
4.22
5.65
214
221
175
160
261
204
224
2.00
1.64
3.74
2.01
1.89
2.35
1.58
221
230
183
164
264
213
231
10.6
11.4
4.75
13.0
8.48
8.27
12.7
151
159
85.2
95.2
176
184
105
4.36
3.67
6.57
4.23
4.43
5.33
2.73
156
167
82.1
98.5
180
185
106
2.30
2.32
2.20
2.39
2.24
2.08
2.58
160
160
155
121
202
137
188
0.670
0.619
0.979
0.701
0.612
0.756
0.579
168
168
165
125
208
149
196
1.11
1.12
1.06
1.13
1.13
1.10
1.12
0.900
0.957
0.529
0.902
0.845
1.03
0.704
1.44
1.37
1.73
1.44
1.46
1.46
1.43
0.851
0.916
0.479
0.881
0.778
0.945
0.681
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                     L-110

-------
Table L-27d.    3.5.6-TCP (3.5.6-trichloro-2-pyridinol) (6515-38-4):  Range of Potential Absorbed
                 Dose in NC Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in NC Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Potential Absorbed
Dose - Aggregated
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
123
102
21
55
64
65
58
128
107
21
58
66
66
62
120
99
21
52
64
66
54
113
92
21
47
62
65
48
0.040
0.040
0.054
0.054
0.040
0.040
0.062

-------

-------
                                   Appendix M
Descriptive Statistics of Potential Exposure Level and Potential Absorbed Dose Estimates
                 for Target Pollutants in Participating OH Children
                                       M-l

-------
M-2

-------
This appendix contains tables of descriptive statistics of potential exposure and potential absorbed dose
estimates (expressed in both ng and pmole units) in OH children for the following pollutants and
metabolites:
Pollutant/Metabolite
Benz[a]anthracene
Benzo[£>]fluoranthene
Benzo[/(]fluoranthene
Benzo[g/?/]perylene
Benzo[a]pyrene
Benzo[e]pyrene
Benzylbutylphthalate
Bisphenol-A
a/p/?a-Chlordane
gamma-Chlordane
Chlorpyrifos
Chrysene
Cyfluthrin
Diazinon
Dibenzo[a,/?]anthracene
Di-n-butylphthalate
p,p'-DDE
2,4-D (2,4-dichlorophenoxyacetic acid)
lndeno[1 ,2,3-cd]pyrene
Pentachlorophenol
c/s-Permethrin
frans-Permethrin
PCS 52
PCB95
PCS 101
3,5,6-TCP (3,5,6-trichloro-2-Dvridinol)
Table Numbers for
Potential Exposure
Summaries
Tables M-1 a, M-1b
Tables M-2a, M-2b
Tables M-3a, M-3b
Tables M-4a, M-4b
Tables M-5a, M-5b
Tables M-6a, M-6b
Tables M-7a, M-7b
Tables M-8a, M-8b
Tables M-9a, M-9b
Tables M-1 Oa, M-1 Ob
Tables M-1 1 a, M-11b
Tables M-12a, M-12b
Tables M-1 3a, M-13b
Tables M-14a, M-14b
Tables M-1 5a, M-15b
Tables M-16a, M-16b
Tables M-1 7a, M-17b
Tables M-1 8a, M-18b
Tables M-1 9a, M-19b
Tables M-20a, M-20b
Tables M-21 a, M-21b
Tables M-22a, M-22b
Tables M-23a, M-23b
Tables M-24a, M-24b
Tables M-25a, M-25b
Tables M-26a, M-26b
Table Numbers for
Potential Absorbed
Dose Summaries
Tables M-1c, M-1d
Tables M-2c, M-2d
Tables M-3c, M-3d
Tables M-4c, M-4d
Tables M-5c, M-5d
Tables M-6c, M-6d
Tables M-7c, M-7d
Tables M-8c, M-8d
Tables M-9c, M-9d
Tables M-1 Oc, M-10d
Tables M-1 1c, M-11d
Tables M-12c, M-12d
Tables M-1 3c, M-1 3d
Tables M-14c, M-14d
Tables M-1 5c, M-15d
Tables M-16c, M-16d
Tables M-1 7c, M-17d
Tables M-1 8c, M-18d
Tables M-1 9c, M-19d
Tables M-20c, M-20d
Tables M-21 c, M-21d
Tables M-22c, M-22d
Tables M-23c, M-23d
Tables M-24c, M-24d
Tables M-25c, M-25d
Tables M-26c, M-26d
Descriptive statistics are presented separately for the following groups of OH child participants:
        All participants
        Participants from urban areas
        Participants from rural areas
        Participants from low-income areas
        Participants from middle/upper-income areas
        Stay-at-home children
        Day care children
                                                  M-3

-------
Table M-1a.     Benzralanthracene (56-55-3): Estimates of Potential Exposure in OH Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
106
90
16
33
63
60
46
127
110
17
41
73
69
58
115
98
17
35
67
62
53
41.5
47.8
6.3
54.5
38.1
36.7
47.8
37.0
36.4
41.2
51.2
31.5
33.3
41.4
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
1.26
-
-
-
-
-
-
46.8
-
-
-
59.8
66.3
22.2
30.2
82.3
41.2
81.5
-
-
-
1.60
-
-
-
-
-
-
74.6
-
-
-
138
149
29.9
32.1
177
93.7
176
-
-
-
0.839
-
-
-
-
-
-
33.4
-
-
-
24.2
28.2
10.0
19.4
29.2
16.0
39.1
-
-
-
0.787
-
-
-
-
-
-
0.640
-
-
-
1.24
1.18
1.30
0.981
1.40
1.24
1.07
Potential Exposure in OH Preschool Children (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
106
90
16
33
63
60
46
127
110
17
41
73
69
58
115
98
17
35
67
62
53
41.5
47.8
6.3
54.5
38.1
36.7
47.8
37.0
36.4
41.2
51.2
31.5
33.3
41.4
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
5.51
-
-
-
-
-
-
205
-
-
-
262
290
97.1
132
360
180
357
-
-
-
6.99
-
-
-
-
-
-
327
-
-
-
607
651
131
140
775
411
769
-
-
-
3.68
-
-
-
-
-
-
146
-
-
-
106
123
43.9
85.1
128
70.3
171
-
-
-
0.787
-
-
-
-
-
-
0.640
-
-
-
1.24
1.18
1.30
0.981
1.40
1.24
1.07
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                    M-4

-------
Table M-1 b.    Benzralanthracene (56-55-3): Range of Potential Exposure in OH Preschool
                Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
106
90
16
33
63
60
46
127
110
17
41
73
69
58
115
98
17
35
67
62
53

-------
Table M-1c.    Benzralanthracene (56-55-3):  Estimates of Potential Absorbed Dose in OH
                 Preschool Children.  Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
106
90
16
33
63
60
46
127
110
17
41
73
69
58
115
98
17
35
67
62
53
41.5
47.8
6.3
54.5
38.1
36.7
47.8
37.0
36.4
41.2
51.2
31.5
33.3
41.4
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
0.035
-
-
-
-
-
-
1.42
-
-
-
1.76
1.96
0.616
0.921
2.41
1.38
2.21
-
-
-
0.043
-
-
-
-
-
-
2.57
-
-
-
3.88
4.16
0.806
1.13
4.92
3.78
3.98
-
-
-
0.023
-
-
-
-
-
-
0.942
-
-
-
0.697
0.813
0.289
0.556
0.842
0.480
1.08
-
-
-
0.808
-
-
-
-
-
-
0.710
-
-
-
1.26
1.19
1.27
1.02
1.40
1.27
1.10
Potential Absorbed Dose in OH Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
106
90
16
33
63
60
46
127
110
17
41
73
69
58
115
98
17
35
67
62
53
41.5
47.8
6.3
54.5
38.1
36.7
47.8
37.0
36.4
41.2
51.2
31.5
33.3
41.4
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
0.153
-
-
-
-
-
-
6.24
-
-
-
7.71
8.58
2.70
4.04
10.6
6.04
9.67
-
-
-
0.190
-
-
-
-
-
-
11.2
-
-
-
17.0
18.2
3.53
4.93
21.6
16.6
17.4
-
-
-
0.102
-
-
-
-
-
-
4.13
-
-
-
3.05
3.56
1.27
2.43
3.69
2.10
4.73
-
-
-
0.808
-
-
-
-
-
-
0.710
-
-
-
1.26
1.19
1.27
1.02
1.40
1.27
1.10
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected.  Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      M-6

-------
Table M-1d.    Benzralanthracene (56-55-3): Range of Potential Absorbed Dose in OH Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
106
90
16
33
63
60
46
127
110
17
41
73
69
58
115
98
17
35
67
62
53

-------
Table M-2a.     Benzorfrlfluoranthene (205-99-2):  Estimates of Potential Exposure in OH Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
127
110
17
41
73
69
58
115
98
17
35
67
62
53
48.8
51.9
29.4
59.0
46.6
37.7
62.5
52.8
51.8
58.8
65.9
47.9
40.6
67.2
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
1.14
-
1.67
-
-
1.34
60.8
63.5
43.2
59.6
-
-
66.2
140
155
53.8
74.9
190
92.3
197
-
1.91
-
2.99
-
-
2.37
146
156
25.4
94.5
-
-
110
306
328
66.6
82.8
389
177
403
-
0.778
-
0.919
-
-
0.853
36.4
36.1
38.0
41.2
-
-
41.5
61.6
71.4
26.3
48.0
74.2
41.9
96.7
-
0.695
-
0.904
-
-
0.772
0.747
0.780
0.503
0.717
-
-
0.780
1.19
1.13
1.24
0.971
1.33
1.17
1.07
Potential Exposure in OH Preschool Children (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
127
110
17
41
73
69
58
115
98
17
35
67
62
53
48.8
51.9
29.4
59.0
46.6
37.7
62.5
52.8
51.8
58.8
65.9
47.9
40.6
67.2
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
4.54
-
6.61
-
-
5.31
241
252
171
236
-
-
262
556
616
213
297
751
366
779
-
7.58
-
11.9
-
-
9.39
578
619
101
375
-
-
437
1,210
1,300
264
328
1,540
700
1,600
-
3.09
-
3.64
-
-
3.38
144
143
150
163
-
-
164
244
283
104
190
294
166
383
-
0.695
-
0.904
-
-
0.772
0.747
0.780
0.503
0.717
-
-
0.780
1.19
1.13
1.24
0.971
1.33
1.17
1.07
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                   M-8

-------
Table M-2b.    BenzoTfolfluoranthene (205-99-2): Range of Potential Exposure in OH Preschool
                Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
127
110
17
41
73
69
58
115
98
17
35
67
62
53

-------
Table M-2c.    Benzorfrlfluoranthene (205-99-2):  Estimates of Potential Absorbed Dose in OH
                 Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
127
110
17
41
73
69
58
115
98
17
35
67
62
53
48.8
51.9
29.4
59.0
46.6
37.7
62.5
52.8
51.8
58.8
65.9
47.9
40.6
67.2
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
0.033
-
0.048
-
-
0.037
1.74
1.80
1.30
1.81
-
-
1.91
4.12
4.57
1.52
2.31
5.52
3.04
5.39
-
0.055
-
0.086
-
-
0.064
3.87
4.14
0.910
3.26
-
-
3.48
8.18
8.76
1.90
2.95
10.3
6.98
9.31
-
0.022
-
0.026
-
-
0.023
1.04
1.03
1.09
1.16
-
-
1.14
1.78
2.06
0.758
1.37
2.14
1.25
2.67
-
0.724
-
0.935
-
-
0.819
0.765
0.791
0.581
0.777
-
-
0.807
1.21
1.15
1.22
1.02
1.34
1.20
1.10
Potential Absorbed Dose in OH Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
127
110
17
41
73
69
58
115
98
17
35
67
62
53
48.8
51.9
29.4
59.0
46.6
37.7
62.5
52.8
51.8
58.8
65.9
47.9
40.6
67.2
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
0.132
-
0.191
-
-
0.148
6.88
7.14
5.17
7.17
-
-
7.59
16.3
18.1
6.01
9.17
21.9
12.1
21.3
-
0.218
-
0.341
-
-
0.255
15.3
16.4
3.61
12.9
-
-
13.8
32.4
34.7
7.51
11.7
40.8
27.7
36.9
-
0.088
-
0.102
-
-
0.093
4.13
4.10
4.33
4.61
-
-
4.53
7.04
8.16
3.00
5.44
8.49
4.96
10.6
-
0.724
-
0.935
-
-
0.819
0.765
0.791
0.581
0.777
-
-
0.807
1.21
1.15
1.22
1.02
1.34
1.20
1.10
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                     M-10

-------
Table M-2d.    BenzoTfolfluoranthene (205-99-2):  Range of Potential Absorbed Dose in OH
                 Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
127
110
17
41
73
69
58
115
98
17
35
67
62
53

-------
Table M-3a.     Benzorftlfluoranthene (207-08-9):  Estimates of Potential Exposure in OH Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
127
110
17
41
73
69
58
115
98
17
35
67
62
53
40.8
42.6
29.4
48.7
38.4
30.4
53.6
25.2
24.5
29.4
31.7
24.7
17.4
34.5
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
-
-
-
0.646
-
-
-
-
-
-
-
50.1
55.2
20.7
26.4
67.8
34.6
68.3
-
-
-
-
-
-
0.409
-
-
-
-
-
-
-
109
117
23.2
28.3
139
73.1
138
-
-
-
-
-
-
0.591
-
-
-
-
-
-
-
22.1
25.2
10.4
17.1
26.5
15.1
34.6
-
-
-
-
-
-
0.363
-
-
-
-
-
-
-
1.19
1.13
1.27
0.984
1.32
1.18
1.04
Potential Exposure in OH Preschool Children (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
127
110
17
41
73
69
58
115
98
17
35
67
62
53
40.8
42.6
29.4
48.7
38.4
30.4
53.6
25.2
24.5
29.4
31.7
24.7
17.4
34.5
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
-
-
-
2.56
-
-
-
-
-
-
-
199
219
82.1
105
269
137
271
-
-
-
-
-
-
1.62
-
-
-
-
-
-
-
432
464
92.1
112
550
290
548
-
-
-
-
-
-
2.34
-
-
-
-
-
-
-
87.8
100
41.4
67.7
105
59.9
137
-
-
-
-
-
-
0.363
-
-
-
-
-
-
-
1.19
1.13
1.27
0.984
1.32
1.18
1.04
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                   M-12

-------
Table M-3b.    BenzoT/clfluoranthene (207-08-9): Range of Potential Exposure in OH Preschool
                Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
127
110
17
41
73
69
58
115
98
17
35
67
62
53

-------
Table M-3c.    Benzorftlfluoranthene (207-08-9):  Estimates of Potential Absorbed Dose in OH
                 Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
127
110
17
41
73
69
58
115
98
17
35
67
62
53
40.8
42.6
29.4
48.7
38.4
30.4
53.6
25.2
24.5
29.4
31.7
24.7
17.4
34.5
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
-
-
-
0.018
-
-
-
-
-
-
-
1.48
1.64
0.574
0.820
1.99
1.16
1.86
-
-
-
-
-
-
0.011
-
-
-
-
-
-
-
3.05
3.27
0.641
1.01
3.86
2.94
3.16
-
-
-
-
-
-
0.016
-
-
-
-
-
-
-
0.638
0.728
0.301
0.488
0.766
0.452
0.957
-
-
-
-
-
-
0.428
-
-
-
-
-
-
-
1.21
1.16
1.24
1.05
1.33
1.22
1.07
Potential Absorbed Dose in OH Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
127
110
17
41
73
69
58
115
98
17
35
67
62
53
40.8
42.6
29.4
48.7
38.4
30.4
53.6
25.2
24.5
29.4
31.7
24.7
17.4
34.5
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
-
-
-
0.071
-
-
-
-
-
-
-
5.88
6.50
2.28
3.25
7.90
4.59
7.39
-
-
-
-
-
-
0.045
-
-
-
-
-
-
-
12.1
13.0
2.54
4.00
15.3
11.7
12.5
-
-
-
-
-
-
0.064
-
-
-
-
-
-
-
2.53
2.88
1.19
1.93
3.04
1.79
3.79
-
-
-
-
-
-
0.428
-
-
-
-
-
-
-
1.21
1.16
1.24
1.05
1.33
1.22
1.07
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                     M-14

-------
Table M-3d.    BenzoT/clfluoranthene (207-08-9):  Range of Potential Absorbed Dose in OH
                 Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
127
110
17
41
73
69
58
115
98
17
35
67
62
53

-------
Table M-4a.     Benzorq/i/lperylene (191-24-2): Estimates of Potential Exposure in OH Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
127
110
17
41
73
69
58
115
98
17
35
67
62
53
44.0
50.0
5.9
69.2
34.2
30.4
60.7
4.7
4.5
5.9
4.9
5.5
2.9
6.9
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
1.04
-
1.60
-
-
1.29
-
-
-
-
-
-
-
72.8
80.1
31.0
39.5
98.0
50.5
98.9
-
1.74
-
2.81
-
-
2.35
-
-
-
-
-
-
-
152
163
37.8
41.2
193
111
186
-
0.765
-
0.962
-
-
0.841
-
-
-
-
-
-
-
32.9
37.6
15.4
25.6
39.5
22.4
51.7
-
0.580
-
0.808
-
-
0.704
-
-
-
-
-
-
-
1.18
1.12
1.24
0.968
1.31
1.16
1.03
Potential Exposure in OH Preschool Children (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
127
110
17
41
73
69
58
115
98
17
35
67
62
53
44.0
50.0
5.9
69.2
34.2
30.4
60.7
4.7
4.5
5.9
4.9
5.5
2.9
6.9
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
3.75
-
5.79
-
-
4.65
-
-
-
-
-
-
-
264
290
112
143
354
183
358
-
6.31
-
10.2
-
-
8.49
-
-
-
-
-
-
-
550
589
137
149
699
403
674
-
2.77
-
3.48
-
-
3.04
-
-
-
-
-
-
-
119
136
55.6
92.8
143
81.0
187
-
0.580
-
0.808
-
-
0.704
-
-
-
-
-
-
-
1.18
1.12
1.24
0.968
1.31
1.16
1.03
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected.  Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                   M-16

-------
Table M-4b.    Benzorq/i/lperylene (191-24-2): Range of Potential Exposure in OH Preschool
                Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
127
110
17
41
73
69
58
115
98
17
35
67
62
53

-------
Table M-4c.    Benzorq/i/lperylene (191-24-2):  Estimates of Potential Absorbed Dose in OH
                 Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
127
110
17
41
73
69
58
115
98
17
35
67
62
53
44.0
50.0
5.9
69.2
34.2
30.4
60.7
4.7
4.5
5.9
4.9
5.5
2.9
6.9
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
0.030
-
0.047
-
-
0.037
-
-
-
-
-
-
-
2.18
2.40
0.869
1.22
2.91
1.70
2.74
-
0.052
-
0.084
-
-
0.070
-
-
-
-
-
-
-
4.50
4.82
1.05
1.49
5.69
4.56
4.40
-
0.022
-
0.027
-
-
0.023
-
-
-
-
-
-
-
0.949
1.08
0.442
0.733
1.14
0.669
1.43
-
0.619
-
0.852
-
-
0.755
-
-
-
-
-
-
-
1.20
1.15
1.22
1.03
1.32
1.19
1.07
Potential Absorbed Dose in OH Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
127
110
17
41
73
69
58
115
98
17
35
67
62
53
44.0
50.0
5.9
69.2
34.2
30.4
60.7
4.7
4.5
5.9
4.9
5.5
2.9
6.9
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
0.110
-
0.169
-
-
0.133
-
-
-
-
-
-
-
7.87
8.70
3.15
4.43
10.5
6.14
9.90
-
0.190
-
0.305
-
-
0.253
-
-
-
-
-
-
-
16.3
17.4
3.79
5.39
20.6
16.5
15.9
-
0.079
-
0.098
-
-
0.083
-
-
-
-
-
-
-
3.43
3.92
1.60
2.65
4.13
2.42
5.17
-
0.619
-
0.852
-
-
0.755
-
-
-
-
-
-
-
1.20
1.15
1.22
1.03
1.32
1.19
1.07
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected.  Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                     M-18

-------
Table M-4d.    Benzorq/i/lperylene (191-24-2): Range of Potential Absorbed Dose in OH
                 Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
127
110
17
41
73
69
58
115
98
17
35
67
62
53

-------
Table M-5a.     BenzoMpyrene (50-32-8):  Estimates of Potential Exposure in OH Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
127
110
17
41
73
69
58
115
98
17
35
67
62
53
32.8
37.0
5.9
48.7
27.4
23.2
44.6
22.8
20.0
41.2
24.4
24.7
18.8
27.6
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
-
-
-
-
-
-
-
-
-
-
-
79.1
87.2
32.2
39.3
109
55.2
107
-
-
-
-
-
-
-
-
-
-
-
-
-
-
183
196
41.1
42.9
233
123
232
-
-
-
-
-
-
-
-
-
-
-
-
-
-
33.0
37.7
15.3
25.0
40.4
22.7
51.2
-
-
-
-
-
-
-
-
-
-
-
-
-
-
1.21
1.15
1.28
0.986
1.35
1.21
1.07
Potential Exposure in OH Preschool Children (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
127
110
17
41
73
69
58
115
98
17
35
67
62
53
32.8
37.0
5.9
48.7
27.4
23.2
44.6
22.8
20.0
41.2
24.4
24.7
18.8
27.6
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
-
-
-
-
-
-
-
-
-
-
-
313
346
128
156
433
219
424
-
-
-
-
-
-
-
-
-
-
-
-
-
-
724
111
163
170
924
488
920
-
-
-
-
-
-
-
-
-
-
-
-
-
-
131
149
60.7
99.2
160
89.8
203
-
-
-
-
-
-
-
-
-
-
-
-
-
-
1.21
1.15
1.28
0.986
1.35
1.21
1.07
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected.  Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                   M-20

-------
Table M-5b.    Benzolalpyrene (50-32-8):  Range of Potential Exposure in OH Preschool Children.
                Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
127
110
17
41
73
69
58
115
98
17
35
67
62
53

-------
Table M-5c.    BenzoMpyrene (50-32-8):  Estimates of Potential Absorbed Dose in OH Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
127
110
17
41
73
69
58
115
98
17
35
67
62
53
32.8
37.0
5.9
48.7
27.4
23.2
44.6
22.8
20.0
41.2
24.4
24.7
18.8
27.6
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
-
-
-
-
-
-
-
-
-
-
-
2.34
2.59
0.900
1.20
3.21
1.85
2.91
-
-
-
-
-
-
-
-
-
-
-
-
-
-
5.14
5.51
1.13
1.49
6.52
4.96
5.32
-
-
-
-
-
-
-
-
-
-
-
-
-
-
0.952
1.09
0.441
0.715
1.17
0.677
1.42
-
-
-
-
-
-
-
-
-
-
-
-
-
-
1.23
1.18
1.26
1.04
1.36
1.24
1.10
Potential Absorbed Dose in OH Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
127
110
17
41
73
69
58
115
98
17
35
67
62
53
32.8
37.0
5.9
48.7
27.4
23.2
44.6
22.8
20.0
41.2
24.4
24.7
18.8
27.6
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
-
-
-
-
-
-
-
-
-
-
-
9.27
10.3
3.57
4.76
12.7
7.34
11.5
-
-
-
-
-
-
-
-
-
-
-
-
-
-
20.4
21.8
4.46
5.89
25.8
19.7
21.1
-
-
-
-
-
-
-
-
-
-
-
-
-
-
3.77
4.31
1.75
2.84
4.62
2.69
5.61
-
-
-
-
-
-
-
-
-
-
-
-
-
-
1.23
1.18
1.26
1.04
1.36
1.24
1.10
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                     M-22

-------
Table M-5d.    Benzolalpyrene (50-32-8):  Range of Potential Absorbed Dose in OH Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
127
110
17
41
73
69
58
115
98
17
35
67
62
53

-------
Table M-6a.     Benzorelpyrene (192-97-2): Estimates of Potential Exposure in OH Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
127
110
17
41
73
69
58
115
98
17
35
67
62
53
40.0
45.4
5.9
53.8
35.6
30.4
51.8
28.3
25.5
47.1
36.6
27.4
18.8
39.7
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
0.973
-
-
0.828
-
-
-
-
-
-
-
74.8
82.6
29.7
39.7
101
51.7
102
-
-
-
1.02
-
-
0.803
-
-
-
-
-
-
-
159
171
36.0
43.1
203
108
201
-
-
-
0.745
-
-
0.679
-
-
-
-
-
-
-
33.4
38.3
15.3
25.9
40.2
23.1
51.5
-
-
-
0.635
-
-
0.537
-
-
-
-
-
-
-
1.18
1.12
1.20
0.950
1.31
1.16
1.05
Potential Exposure in OH Preschool Children (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
127
110
17
41
73
69
58
115
98
17
35
67
62
53
40.0
45.4
5.9
53.8
35.6
30.4
51.8
28.3
25.5
47.1
36.6
27.4
18.8
39.7
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
3.86
-
-
3.28
-
-
-
-
-
-
-
296
327
118
157
400
205
403
-
-
-
4.02
-
-
3.18
-
-
-
-
-
-
-
631
677
143
171
803
428
798
-
-
-
2.95
-
-
2.69
-
-
-
-
-
-
-
133
152
60.6
103
159
91.6
204
-
-
-
0.635
-
-
0.537
-
-
-
-
-
-
-
1.18
1.12
1.20
0.950
1.31
1.16
1.05
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                   M-24

-------
Table M-6b.    BenzoTelpyrene (192-97-2): Range of Potential Exposure in OH Preschool
                Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
127
110
17
41
73
69
58
115
98
17
35
67
62
53

-------
Table M-6c.    Benzorelpyrene (192-97-2): Estimates of Potential Absorbed Dose in OH  Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
127
110
17
41
73
69
58
115
98
17
35
67
62
53
40.0
45.4
5.9
53.8
35.6
30.4
51.8
28.3
25.5
47.1
36.6
27.4
18.8
39.7
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
0.028
-
-
0.023
-
-
-
-
-
-
-
2.22
2.46
0.837
1.23
2.97
1.73
2.80
-
-
-
0.030
-
-
0.022
-
-
-
-
-
-
-
4.52
4.85
1.00
1.55
5.71
4.36
4.68
-
-
-
0.021
-
-
0.019
-
-
-
-
-
-
-
0.964
1.10
0.440
0.741
1.16
0.691
1.42
-
-
-
0.690
-
-
0.593
-
-
-
-
-
-
-
1.20
1.15
1.19
1.01
1.32
1.20
1.08
Potential Absorbed Dose in OH Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
127
110
17
41
73
69
58
115
98
17
35
67
62
53
40.0
45.4
5.9
53.8
35.6
30.4
51.8
28.3
25.5
47.1
36.6
27.4
18.8
39.7
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
0.112
-
-
0.092
-
-
-
-
-
-
-
8.79
9.74
3.32
4.88
11.8
6.84
11.1
-
-
-
0.119
-
-
0.088
-
-
-
-
-
-
-
17.9
19.2
3.97
6.14
22.6
17.3
18.6
-
-
-
0.083
-
-
0.074
-
-
-
-
-
-
-
3.82
4.38
1.75
2.94
4.59
2.74
5.64
-
-
-
0.690
-
-
0.593
-
-
-
-
-
-
-
1.20
1.15
1.19
1.01
1.32
1.20
1.08
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected.  Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                     M-26

-------
Table M-6d.    BenzoTelpyrene (192-97-2):  Range of Potential Absorbed Dose in OH Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
127
110
17
41
73
69
58
115
98
17
35
67
62
53

-------
Table M-7a.     Benzyl butyl pht ha late (85-68-7):  Estimates of Potential Exposure in OH Preschool
                 Children. Summarized  by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
107
17
38
73
69
55
48
42
6
14
30
34
14
114
98
16
35
67
62
52
45.2
44.9
47.1
65.8
34.2
29.0
65.5
64.6
66.7
50.0
71.4
63.3
52.9
92.9
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
422
-
-
389
17,500
17,500
17,100
22,300
15,300
14,000
25,900
1,350
1,390
1,090
1,140
1,570
736
2,090
-
-
-
310
-
-
306
22,000
22,200
22,800
30,800
16,300
21,300
22,300
2,740
2,930
1,010
1,040
3,480
880
3,830
-
-
-
344
-
-
321
9,040
9,250
7,710
1 1 ,400
8,590
6,670
18,900
664
646
786
794
620
440
1,080
-
-
-
0.617
-
-
0.575
1.18
1.17
1.37
1.18
1.15
1.17
0.856
1.12
1.16
0.821
0.887
1.26
1.03
1.02
Potential Exposure in OH Preschool Children (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
107
17
38
73
69
55
48
42
6
14
30
34
14
114
98
16
35
67
62
52
45.2
44.9
47.1
65.8
34.2
29.0
65.5
64.6
66.7
50.0
71.4
63.3
52.9
92.9
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
1,350
-
-
1,250
55,900
56,000
54,800
71,500
48,900
44,700
83,000
4,330
4,460
3,500
3,640
5,040
2,360
6,680
-
-
-
991
-
-
979
70,600
71,100
73,000
98,700
52,200
68,200
71 ,300
8,770
9,370
3,230
3,310
11,100
2,820
12,300
-
-
-
1,100
-
-
1,030
28,900
29,600
24,700
36,600
27,500
21,400
60,500
2,120
2,070
2,520
2,540
1,980
1,410
3,470
-
-
-
0.617
-
-
0.575
1.18
1.17
1.37
1.18
1.15
1.17
0.856
1.12
1.16
0.821
0.887
1.26
1.03
1.02
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected.  Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                   M-28

-------
Table M-7b.    Benzylbutylphthalate (85-68-7):  Range of Potential Exposure in OH Preschool
                Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
107
17
38
73
69
55
48
42
6
14
30
34
14
114
98
16
35
67
62
52

-------
Table M-7c.    Benzyl butyl pht ha late (85-68-7): Estimates of Potential Absorbed Dose in OH
                 Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
107
17
38
73
69
55
48
42
6
14
30
34
14
114
98
16
35
67
62
52
45.2
44.9
47.1
65.8
34.2
29.0
65.5
64.6
66.7
50.0
71.4
63.3
52.9
92.9
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
12.0
-
-
10.9
480
479
492
557
437
419
628
38.7
39.5
33.8
36.0
43.2
22.8
57.7
-
-
-
8.31
-
-
9.09
573
563
695
695
483
616
438
70.2
74.4
36.4
40.3
86.4
28.4
96.3
-
-
-
9.65
-
-
8.80
258
264
224
328
239
198
491
19.1
18.6
22.2
22.7
17.9
13.1
29.8
-
-
-
0.660
-
-
0.624
1.16
1.15
1.35
1.05
1.19
1.20
0.774
1.13
1.17
0.900
0.970
1.26
1.06
1.06
Potential Absorbed Dose in OH Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
107
17
38
73
69
55
48
42
6
14
30
34
14
114
98
16
35
67
62
52
45.2
44.9
47.1
65.8
34.2
29.0
65.5
64.6
66.7
50.0
71.4
63.3
52.9
92.9
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
38.3
-
-
35.0
1,540
1,530
1,570
1,780
1,400
1,340
2,010
124
126
108
115
138
72.9
185
-
-
-
26.6
-
-
29.1
1,830
1,800
2,220
2,220
1,550
1,970
1,400
225
238
116
129
277
90.9
308
-
-
-
30.9
-
-
28.2
827
844
716
1,050
766
635
1,570
61.1
59.6
71.2
72.7
57.3
42.1
95.2
-
-
-
0.660
-
-
0.624
1.16
1.15
1.35
1.05
1.19
1.20
0.774
1.13
1.17
0.900
0.970
1.26
1.06
1.06
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                     M-30

-------
Table M-7d.    Benzylbutylphthalate (85-68-7):  Range of Potential Absorbed Dose in OH
                 Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
107
17
38
73
69
55
48
42
6
14
30
34
14
114
98
16
35
67
62
52

-------
Table M-8a.     Bisphenol-A (80-05-7): Estimates of Potential Exposure in OH Preschool Children.
                 Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Potential Exposure
-Aggregated
(ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
101
85
16
32
59
59
42
107
93
14
35
60
58
49
104
88
16
28
64
60
44
67
55
12
19
40
41
26
79.2
77.6
87.5
84.4
72.9
71.2
90.5
100.0
100.0
100.0
100.0
100.0
100.0
100.0
67.3
65.9
75.0
82.1
62.5
55.0
84.1
100.0
100.0
100.0
100.0
100.0
100.0
100.0
Potential Exposure in OH
Potential Exposure
via Inhalation
(p moles/day)
Potential Exposure
via Dietary
Ingestion
(p moles/day)
Potential Exposure
via Indirect
Ingestion
(p moles/day)
Potential Exposure
-Aggregated
(p moles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
101
85
16
32
59
59
42
107
93
14
35
60
58
49
104
88
16
28
64
60
44
67
55
12
19
40
41
26
79.2
77.6
87.5
84.4
72.9
71.2
90.5
100.0
100.0
100.0
100.0
100.0
100.0
100.0
67.3
65.9
75.0
82.1
62.5
55.0
84.1
100.0
100.0
100.0
100.0
100.0
100.0
100.0
13.0
13.2
12.0
20.4
9.92
10.1
17.2
3,080
2,740
5,320
3,120
2,400
2,310
3,980
1.74
1.78
1.55
1.14
1.90
1.95
1.46
3,620
3,170
5,670
3,850
2,570
2,500
5,390
Preschool Children
57.1
57.9
52.6
89.2
43.4
44.2
75.3
13,500
12,000
23,300
13,700
10,500
10,100
17,400
7.64
7.80
6.78
5.00
8.32
8.56
6.40
15,900
13,900
24,800
16,900
11,200
10,900
23,600
16.2
15.9
18.1
25.7
7.29
11.2
20.7
5,180
2,810
12,500
3,060
2,470
2,370
7,140
2.08
2.18
1.43
1.17
2.15
2.43
1.44
6,310
3,190
13,500
3,770
2,520
2,410
9,520
9.36
9.55
8.41
12.2
8.38
8.00
11.7
1,910
1,880
2,150
2,240
1,650
1,620
2,340
1.16
1.17
1.14
0.852
1.27
1.22
1.09
2,150
2,170
2,070
2,740
1,810
1,810
2,820
0.690
0.698
0.657
0.925
0.540
0.569
0.787
0.871
0.842
1.07
0.803
0.838
0.820
0.894
0.827
0.837
0.795
0.702
0.841
0.901
0.719
0.907
0.863
1.13
0.817
0.830
0.796
1.02
pmoles/day)
70.8
69.6
79.1
112
31.9
49.3
90.6
22,700
12,300
54,800
13,400
10,800
10,400
31 ,300
9.10
9.54
6.26
5.13
9.43
10.7
6.30
27,600
14,000
59,300
16,500
1 1 ,000
10,600
41 ,700
41.0
41.8
36.9
53.6
36.7
35.1
51.1
8,380
8,240
9,410
9,830
7,220
7,080
10,200
5.09
5.11
4.99
3.73
5.55
5.34
4.77
9,410
9,500
9,050
12,000
7,930
7,920
12,400
0.690
0.698
0.657
0.925
0.540
0.569
0.787
0.871
0.842
1.07
0.803
0.838
0.820
0.894
0.827
0.837
0.795
0.702
0.841
0.901
0.719
0.907
0.863
1.13
0.817
0.830
0.796
1.02
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                   M-32

-------
Table M-8b.    Bisphenol-A (80-05-7):  Range of Potential Exposure in OH Preschool Children.
                Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Potential Exposure
- Aggregated
(ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
101
85
16
32
59
59
42
107
93
14
35
60
58
49
104
88
16
28
64
60
44
67
55
12
19
40
41
26
Potential E
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Potential Exposure
-Aggregated
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
101
85
16
32
59
59
42
107
93
14
35
60
58
49
104
88
16
28
64
60
44
67
55
12
19
40
41
26

-------
Table M-8c.    Bisphenol-A (80-05-7): Estimates of Potential Absorbed Dose in OH Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Potential Absorbed
Dose - Aggregated
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
101
85
16
32
59
59
42
107
93
14
35
60
58
49
104
88
16
28
64
60
44
67
55
12
19
40
41
26
79.2
77.6
87.5
84.4
72.9
71.2
90.5
100.0
100.0
100.0
100.0
100.0
100.0
100.0
67.3
65.9
75.0
82.1
62.5
55.0
84.1
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.367
0.375
0.323
0.545
0.291
0.294
0.469
85.1
81.1
111
90.2
72.6
68.5
105
0.054
0.055
0.047
0.036
0.059
0.064
0.041
101
98.7
112
115
82.1
76.7
140
0.426
0.430
0.416
0.670
0.213
0.280
0.560
109
90.2
194
89.2
87.3
66.0
142
0.073
0.077
0.042
0.043
0.078
0.090
0.037
130
107
210
110
99.0
70.6
184
0.270
0.276
0.241
0.340
0.245
0.240
0.319
55.1
54.2
61.1
63.4
48.1
48.1
64.6
0.034
0.034
0.032
0.025
0.037
0.036
0.030
63.8
65.4
56.8
81.1
54.4
55.6
79.1
0.688
0.700
0.627
0.910
0.557
0.566
0.808
0.877
0.868
0.962
0.845
0.864
0.836
0.906
0.898
0.899
0.918
0.802
0.899
0.978
0.773
0.906
0.892
1.00
0.861
0.871
0.811
1.02
Potential Absorbed Dose in OH Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose - Aggregated
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
101
85
16
32
59
59
42
107
93
14
35
60
58
49
104
88
16
28
64
60
44
67
55
12
19
40
41
26
79.2
77.6
87.5
84.4
72.9
71.2
90.5
100.0
100.0
100.0
100.0
100.0
100.0
100.0
67.3
65.9
75.0
82.1
62.5
55.0
84.1
100.0
100.0
100.0
100.0
100.0
100.0
100.0
1.61
1.64
1.42
2.39
1.28
1.29
2.05
373
355
488
395
318
300
459
0.237
0.243
0.204
0.160
0.256
0.279
0.180
443
432
492
506
359
336
612
1.87
1.88
1.82
2.94
0.935
1.23
2.45
476
395
852
391
382
289
622
0.319
0.338
0.185
0.188
0.342
0.392
0.162
569
471
922
483
434
309
808
1.18
1.21
1.06
1.49
1.07
1.05
1.40
241
238
267
278
211
211
283
0.148
0.149
0.141
0.109
0.160
0.160
0.132
279
286
249
355
238
244
347
0.688
0.700
0.627
0.910
0.557
0.566
0.808
0.877
0.868
0.962
0.845
0.864
0.836
0.906
0.898
0.899
0.918
0.802
0.899
0.978
0.773
0.906
0.892
1.00
0.861
0.871
0.811
1.02
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      M-34

-------
Table M-8d.    Bisphenol-A (80-05-7): Range of Potential Absorbed Dose in OH Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Potential Absorbed
Dose - Aggregated
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
101
85
16
32
59
59
42
107
93
14
35
60
58
49
104
88
16
28
64
60
44
67
55
12
19
40
41
26

-------
Table M-9a.     a/p/ia-Chlordane (5103-71-9):  Estimates of Potential Exposure in OH Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
125
108
17
40
72
69
56
116
99
17
35
68
63
53
97.6
97.2
100.0
100.0
95.9
95.7
100.0
9.6
10.2
5.9
15.0
4.2
11.6
7.1
94.0
93.9
94.1
100.0
89.7
88.9
100.0
7.40
7.72
5.36
7.80
6.36
9.93
4.27
-
-
-
-
-
-
-
1.59
1.73
0.778
1.41
1.66
2.17
0.896
17.7
18.8
8.20
17.4
16.9
22.7
7.29
-
-
-
-
-
-
-
4.37
4.70
1.07
3.34
4.88
5.80
1.14
2.80
2.85
2.48
3.12
2.55
3.09
2.48
-
-
-
-
-
-
-
0.506
0.541
0.346
0.525
0.521
0.538
0.472
1.14
1.14
1.17
1.13
1.09
1.29
0.922
-
-
-
-
-
-
-
1.34
1.33
1.37
1.26
1.35
1.51
1.13
Potential Exposure in OH Preschool Children (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
125
108
17
40
72
69
56
116
99
17
35
68
63
53
97.6
97.2
100.0
100.0
95.9
95.7
100.0
9.6
10.2
5.9
15.0
4.2
11.6
7.1
94.0
93.9
94.1
100.0
89.7
88.9
100.0
18.1
18.8
13.1
19.0
15.5
24.2
10.4
-
-
-
-
-
-
-
3.87
4.21
1.90
3.43
4.04
5.29
2.19
43.2
45.8
20.0
42.5
41.2
55.3
17.8
-
-
-
-
-
-
-
10.7
11.5
2.60
8.16
11.9
14.2
2.77
6.83
6.96
6.05
7.62
6.22
7.54
6.04
-
-
-
-
-
-
-
1.24
1.32
0.845
1.28
1.27
1.31
1.15
1.14
1.14
1.17
1.13
1.09
1.29
0.922
-
-
-
-
-
-
-
1.34
1.33
1.37
1.26
1.35
1.51
1.13
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                   M-36

-------
Table M-9b.    a/p/ia-Chlordane (5103-71-9):  Range of Potential Exposure in OH Preschool
                Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
125
108
17
40
72
69
56
116
99
17
35
68
63
53

-------
Table M-9c.    a/p/ia-Chlordane (5103-71-9):  Estimates of Potential Absorbed Dose in OH
                 Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
125
108
17
40
72
69
56
116
99
17
35
68
63
53
97.6
97.2
100.0
100.0
95.9
95.7
100.0
9.6
10.2
5.9
15.0
4.2
11.6
7.1
94.0
93.9
94.1
100.0
89.7
88.9
100.0
0.225
0.235
0.156
0.235
0.187
0.303
0.128
-
-
-
-
-
-
-
0.047
0.051
0.024
0.040
0.048
0.064
0.026
0.572
0.608
0.230
0.577
0.521
0.727
0.258
-
-
-
-
-
-
-
0.132
0.142
0.038
0.087
0.148
0.175
0.035
0.080
0.082
0.071
0.088
0.073
0.092
0.068
-
-
-
-
-
-
-
0.015
0.016
0.010
0.015
0.015
0.016
0.013
1.17
1.16
1.21
1.18
1.08
1.30
0.972
-
-
-
-
-
-
-
1.37
1.36
1.42
1.30
1.36
1.52
1.18
Potential Absorbed Dose in OH Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
125
108
17
40
72
69
56
116
99
17
35
68
63
53
97.6
97.2
100.0
100.0
95.9
95.7
100.0
9.6
10.2
5.9
15.0
4.2
11.6
7.1
94.0
93.9
94.1
100.0
89.7
88.9
100.0
0.548
0.575
0.380
0.575
0.455
0.740
0.312
-
-
-
-
-
-
-
0.114
0.124
0.059
0.098
0.117
0.157
0.064
1.40
1.48
0.562
1.41
1.27
1.77
0.629
-
-
-
-
-
-
-
0.321
0.345
0.093
0.213
0.362
0.426
0.085
0.195
0.199
0.174
0.214
0.179
0.224
0.166
-
-
-
-
-
-
-
0.036
0.038
0.024
0.037
0.037
0.039
0.032
1.17
1.16
1.21
1.18
1.08
1.30
0.972
-
-
-
-
-
-
-
1.37
1.36
1.42
1.30
1.36
1.52
1.18
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected.  Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                     M-38

-------
Table M-9d.    a/p/ia-Chlordane (5103-71-9):  Range of Potential Absorbed Dose in OH Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
125
108
17
40
72
69
56
116
99
17
35
68
63
53

-------
Table M-10a.   qa/n/na-Chlordane (5103-74-2): Estimates of Potential Exposure in OH Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
125
108
17
40
72
69
56
116
99
17
35
68
63
53
99.2
99.1
100.0
100.0
98.6
98.6
100.0
8.0
8.3
5.9
10.0
4.2
10.1
5.4
93.1
92.9
94.1
100.0
88.2
87.3
100.0
11.8
12.5
7.05
11.4
11.3
16.5
5.95
-
-
-
-
-
-
-
2.02
2.21
0.947
1.51
2.35
2.88
0.998
37.9
40.5
10.1
27.6
43.7
49.9
9.93
-
-
-
-
-
-
-
7.83
8.45
1.33
3.37
9.81
10.5
1.29
3.84
3.92
3.38
4.28
3.49
4.22
3.42
-
-
-
-
-
-
-
0.544
0.576
0.392
0.583
0.551
0.564
0.522
1.18
1.18
1.16
1.15
1.15
1.35
0.929
-
-
-
-
-
-
-
1.38
1.36
1.44
1.25
1.41
1.56
1.13
Potential Exposure in OH Preschool Children (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
125
108
17
40
72
69
56
116
99
17
35
68
63
53
99.2
99.1
100.0
100.0
98.6
98.6
100.0
8.0
8.3
5.9
10.0
4.2
10.1
5.4
93.1
92.9
94.1
100.0
88.2
87.3
100.0
28.8
30.6
17.2
27.8
27.6
40.4
14.5
-
-
-
-
-
-
-
4.93
5.38
2.31
3.68
5.73
7.03
2.44
92.4
98.9
24.6
67.3
107
122
24.2
-
-
-
-
-
-
-
19.1
20.6
3.26
8.23
23.9
25.7
3.14
9.38
9.57
8.26
10.4
8.52
10.3
8.36
-
-
-
-
-
-
-
1.33
1.41
0.956
1.42
1.35
1.38
1.27
1.18
1.18
1.16
1.15
1.15
1.35
0.929
-
-
-
-
-
-
-
1.38
1.36
1.44
1.25
1.41
1.56
1.13
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                   M-40

-------
Table M-10b.   qa/n/na-Chlordane (5103-74-2): Range of Potential Exposure in OH Preschool
                Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
125
108
17
40
72
69
56
116
99
17
35
68
63
53

-------
Table M-10c.   qa/n/na-Chlordane (5103-74-2):  Estimates of Potential Absorbed Dose in OH
                 Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
125
108
17
40
72
69
56
116
99
17
35
68
63
53
99.2
99.1
100.0
100.0
98.6
98.6
100.0
8.0
8.3
5.9
10.0
4.2
10.1
5.4
93.1
92.9
94.1
100.0
88.2
87.3
100.0
0.362
0.386
0.206
0.352
0.336
0.511
0.178
-
-
-
-
-
-
-
0.060
0.066
0.030
0.043
0.070
0.087
0.029
1.21
1.30
0.292
0.946
1.37
1.59
0.351
-
-
-
-
-
-
-
0.243
0.263
0.048
0.088
0.307
0.327
0.040
0.110
0.112
0.097
0.120
0.101
0.125
0.094
-
-
-
-
-
-
-
0.016
0.017
0.011
0.017
0.016
0.017
0.014
1.20
1.21
1.19
1.22
1.14
1.35
0.981
-
-
-
-
-
-
-
1.40
1.39
1.49
1.30
1.42
1.57
1.18
Potential Absorbed Dose in OH Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
125
108
17
40
72
69
56
116
99
17
35
68
63
53
99.2
99.1
100.0
100.0
98.6
98.6
100.0
8.0
8.3
5.9
10.0
4.2
10.1
5.4
93.1
92.9
94.1
100.0
88.2
87.3
100.0
0.883
0.943
0.502
0.858
0.820
1.25
0.435
-
-
-
-
-
-
-
0.147
0.160
0.072
0.106
0.171
0.211
0.071
2.96
3.17
0.713
2.31
3.34
3.89
0.856
-
-
-
-
-
-
-
0.594
0.641
0.117
0.216
0.748
0.798
0.098
0.268
0.274
0.238
0.293
0.246
0.305
0.229
-
-
-
-
-
-
-
0.038
0.041
0.028
0.041
0.039
0.041
0.035
1.20
1.21
1.19
1.22
1.14
1.35
0.981
-
-
-
-
-
-
-
1.40
1.39
1.49
1.30
1.42
1.57
1.18
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                     M-42

-------
Table M-10d.   qa/n/na-Chlordane (5103-74-2): Range of Potential Absorbed Dose in OH  Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
125
108
17
40
72
69
56
116
99
17
35
68
63
53

-------
Table M-11a.   Chlorpyrifos (2921-88-2): Estimates of Potential Exposure in OH Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Potential Exposure
-Aggregated
(ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
107
90
17
33
64
60
47
125
108
17
40
72
69
56
116
99
17
35
68
63
53
96
79
17
28
58
55
41
100.0
100.0
100.0
100.0
100.0
100.0
100.0
79.2
78.7
82.4
95.0
73.6
71.0
89.3
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
Potential Exposure in OH
Potential Exposure
via Inhalation
(p moles/day)
Potential Exposure
via Dietary
Ingestion
(p moles/day)
Potential Exposure
via Indirect
Ingestion
(p moles/day)
Potential Exposure
-Aggregated
(p moles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
107
90
17
33
64
60
47
125
108
17
40
72
69
56
116
99
17
35
68
63
53
96
79
17
28
58
55
41
100.0
100.0
100.0
100.0
100.0
100.0
100.0
79.2
78.7
82.4
95.0
73.6
71.0
89.3
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
33.4
37.1
13.5
42.3
22.6
34.1
32.5
131
137
96.0
178
110
121
144
27.8
32.1
2.94
58.4
5.03
17.1
40.6
178
192
112
211
143
164
196
Preschool Children
95.2
106
38.5
121
64.4
97.2
92.7
375
391
274
509
314
346
411
79.3
91.5
8.38
167
14.4
48.7
116
507
547
321
602
409
467
560
60.5
65.2
11.9
55.8
27.0
75.8
32.8
180
191
83.1
180
188
157
206
164
177
4.22
264
7.46
103
215
234
254
80.6
168
209
234
236
17.1
18.8
10.3
23.8
13.7
14.4
21.3
78.9
80.3
70.8
125
62.1
72.0
88.3
2.97
3.26
1.74
5.07
2.40
2.02
4.69
117
123
90.7
169
92.8
102
139
1.08
1.11
0.719
1.10
0.978
1.14
0.957
0.970
0.996
0.802
0.831
0.970
1.01
0.916
1.54
1.60
1.00
1.79
1.24
1.51
1.46
0.851
0.879
0.674
0.661
0.839
0.904
0.749
pmoles/day)
173
186
34.0
159
77.1
216
93.5
514
544
237
514
538
449
587
467
505
12.0
753
21.3
294
614
668
723
230
478
595
667
674
48.7
53.6
29.5
67.9
39.1
41.0
60.8
225
229
202
358
177
205
252
8.47
9.29
4.96
14.4
6.84
5.77
13.4
333
352
259
481
265
292
398
1.08
1.11
0.719
1.10
0.978
1.14
0.957
0.970
0.996
0.802
0.831
0.970
1.01
0.916
1.54
1.60
1.00
1.79
1.24
1.51
1.46
0.851
0.879
0.674
0.661
0.839
0.904
0.749
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                   M-44

-------
Table M-11b.   Chlorpyrifos (2921-88-2): Range of Potential Exposure in OH Preschool Children.
                Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Potential Exposure
- Aggregated
(ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
107
90
17
33
64
60
47
125
108
17
40
72
69
56
116
99
17
35
68
63
53
96
79
17
28
58
55
41
Potential E
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Potential Exposure
-Aggregated
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
107
90
17
33
64
60
47
125
108
17
40
72
69
56
116
99
17
35
68
63
53
96
79
17
28
58
55
41
1.14
1.14
3.03
2.16
1.14
1.14
2.16

-------
Table M-11c.   Chlorpyrifos (2921-88-2):  Estimates of Potential Absorbed Dose in OH  Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Potential Absorbed
Dose - Aggregated
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
107
90
17
33
64
60
47
125
108
17
40
72
69
56
116
99
17
35
68
63
53
96
79
17
28
58
55
41
100.0
100.0
100.0
100.0
100.0
100.0
100.0
79.2
78.7
82.4
95.0
73.6
71.0
89.3
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
1.06
1.18
0.408
1.31
0.654
1.14
0.958
3.89
4.09
2.64
5.47
3.17
3.71
4.11
0.962
1.11
0.087
1.94
0.140
0.654
1.33
5.39
5.87
3.13
6.38
4.12
5.21
5.63
2.33
2.51
0.409
1.99
0.788
2.97
1.07
5.60
5.95
2.06
6.53
5.28
5.19
6.10
5.74
6.21
0.119
8.82
0.195
4.20
7.18
8.25
8.99
2.00
6.62
5.81
9.02
7.21
0.490
0.539
0.298
0.654
0.399
0.423
0.593
2.26
2.30
2.04
3.56
1.78
2.13
2.43
0.086
0.094
0.050
0.145
0.069
0.060
0.130
3.37
3.56
2.61
4.73
2.70
3.05
3.87
1.11
1.14
0.772
1.18
0.969
1.18
0.996
0.985
1.02
0.735
0.882
0.974
1.02
0.937
1.58
1.64
1.08
1.86
1.24
1.56
1.51
0.861
0.897
0.624
0.728
0.823
0.920
0.764
Potential Absorbed Dose in OH Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose - Aggregated
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
107
90
17
33
64
60
47
125
108
17
40
72
69
56
116
99
17
35
68
63
53
96
79
17
28
58
55
41
100.0
100.0
100.0
100.0
100.0
100.0
100.0
79.2
78.7
82.4
95.0
73.6
71.0
89.3
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
3.02
3.37
1.16
3.73
1.87
3.24
2.73
11.1
11.7
7.52
15.6
9.04
10.6
11.7
2.74
3.17
0.248
5.54
0.401
1.87
3.79
15.4
16.7
8.93
18.2
11.7
14.9
16.0
6.63
7.17
1.17
5.67
2.25
8.47
3.05
16.0
17.0
5.88
18.6
15.1
14.8
17.4
16.4
17.7
0.339
25.2
0.557
12.0
20.5
23.5
25.6
5.71
18.9
16.6
25.7
20.6
1.40
1.54
0.850
1.87
1.14
1.21
1.69
6.45
6.56
5.81
10.2
5.08
6.09
6.93
0.244
0.268
0.143
0.413
0.198
0.172
0.370
9.62
10.2
7.45
13.5
7.70
8.69
11.0
1.11
1.14
0.772
1.18
0.969
1.18
0.996
0.985
1.02
0.735
0.882
0.974
1.02
0.937
1.58
1.64
1.08
1.86
1.24
1.56
1.51
0.861
0.897
0.624
0.728
0.823
0.920
0.764
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      M-46

-------
Table M-11d.   Chlorpyrifos (2921-88-2):  Range of Potential Absorbed Dose in OH Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Potential Absorbed
Dose - Aggregated
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
107
90
17
33
64
60
47
125
108
17
40
72
69
56
116
99
17
35
68
63
53
96
79
17
28
58
55
41
0.039
0.039
0.099
0.055
0.039
0.039
0.055

-------
Table M-12a.   Chrysene (218-01-9):  Estimates of Potential Exposure in OH Preschool Children.
                 Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
105
89
16
34
61
58
47
127
110
17
41
73
69
58
115
98
17
35
67
62
53
64.8
70.8
31.3
82.4
54.1
53.4
78.7
48.8
48.2
52.9
58.5
45.2
42.0
56.9
100.0
100.0
100.0
100.0
100.0
100.0
100.0
1.06
1.15
-
1.64
0.816
0.772
1.41
-
-
41.5
44.2
-
-
47.2
82.3
91.5
29.3
42.0
113
54.5
115
1.49
1.60
-
2.38
0.655
0.703
2.04
-
-
28.0
46.7
-
-
63.1
202
217
36.2
47.7
259
115
269
0.757
0.804
-
0.979
0.690
0.651
0.912
-
-
35.6
34.3
-
-
33.8
34.0
39.5
14.3
26.6
41.1
23.0
53.7
0.663
0.699
-
0.892
0.504
0.480
0.802
-
-
0.538
0.616
-
-
0.667
1.21
1.15
1.25
0.984
1.35
1.20
1.07
Potential Exposure in OH Preschool Children (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
105
89
16
34
61
58
47
127
110
17
41
73
69
58
115
98
17
35
67
62
53
64.8
70.8
31.3
82.4
54.1
53.4
78.7
48.8
48.2
52.9
58.5
45.2
42.0
56.9
100.0
100.0
100.0
100.0
100.0
100.0
100.0
4.64
5.03
-
7.17
3.58
3.38
6.18
-
-
182
193
-
-
207
361
401
128
184
493
239
503
6.52
7.01
-
10.4
2.87
3.08
8.95
-
-
123
205
-
-
276
886
952
159
209
1,130
504
1,180
3.32
3.52
-
4.29
3.02
2.85
4.00
-
-
156
150
-
-
148
149
173
62.7
117
180
101
235
0.663
0.699
-
0.892
0.504
0.480
0.802
-
-
0.538
0.616
-
-
0.667
1.21
1.15
1.25
0.984
1.35
1.20
1.07
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                   M-48

-------
Table M-12b.   Chrysene (218-01-9):  Range of Potential Exposure in OH Preschool Children.
                Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
105
89
16
34
61
58
47
127
110
17
41
73
69
58
115
98
17
35
67
62
53

-------
Table M-12c.   Chrysene (218-01-9): Estimates of Potential Absorbed Dose in OH Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
105
89
16
34
61
58
47
127
110
17
41
73
69
58
115
98
17
35
67
62
53
64.8
70.8
31.3
82.4
54.1
53.4
78.7
48.8
48.2
52.9
58.5
45.2
42.0
56.9
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.030
0.033
-
0.045
0.024
0.023
0.039
-
-
1.27
1.31
-
-
1.36
2.40
2.67
0.829
1.30
3.25
1.82
3.08
0.041
0.044
-
0.065
0.019
0.023
0.055
-
-
1.03
1.55
-
-
1.93
5.25
5.63
1.05
1.71
6.65
4.60
5.89
0.022
0.023
-
0.027
0.020
0.019
0.025
-
-
1.02
0.969
-
-
0.930
0.981
1.14
0.412
0.761
1.19
0.688
1.48
0.677
0.712
-
0.920
0.519
0.497
0.828
-
-
0.623
0.680
-
-
0.707
1.23
1.17
1.23
1.04
1.36
1.23
1.10
Potential Absorbed Dose in OH Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
105
89
16
34
61
58
47
127
110
17
41
73
69
58
115
98
17
35
67
62
53
64.8
70.8
31.3
82.4
54.1
53.4
78.7
48.8
48.2
52.9
58.5
45.2
42.0
56.9
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.132
0.144
-
0.199
0.105
0.101
0.171
-
-
5.55
5.75
-
-
5.95
10.5
11.7
3.63
5.70
14.2
7.96
13.5
0.178
0.192
-
0.284
0.083
0.099
0.239
-
-
4.51
6.80
-
-
8.47
23.0
24.7
4.59
7.49
29.1
20.1
25.8
0.095
0.101
-
0.118
0.088
0.084
0.111
-
-
4.49
4.24
-
-
4.08
4.30
4.99
1.80
3.33
5.20
3.01
6.50
0.677
0.712
-
0.920
0.519
0.497
0.828
-
-
0.623
0.680
-
-
0.707
1.23
1.17
1.23
1.04
1.36
1.23
1.10
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                     M-50

-------
Table M-12d.   Chrysene (218-01-9): Range of Potential Absorbed Dose in OH Preschool Children.
                 Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
105
89
16
34
61
58
47
127
110
17
41
73
69
58
115
98
17
35
67
62
53

-------
Table M-13a.   Cyfluthrin (68359-37-5):  Estimates of Potential Exposure in OH Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
123
106
17
39
71
67
56
125
108
17
40
72
69
56
115
99
16
35
68
63
52
6.5
7.5
0.0
12.8
4.2
0.0
14.3
4.0
4.6
0.0
5.0
2.8
2.9
5.4
87.0
88.9
75.0
97.1
83.8
82.5
92.3
-
-
-
-
-
-
-
-
-
-
-
-
-
-
13.0
14.1
6.24
9.47
15.4
10.7
15.8
-
-
-
-
-
-
-
-
-
-
-
-
-
-
23.7
25.2
7.20
9.14
29.6
19.3
28.0
-
-
-
-
-
-
-
-
-
-
-
-
-
-
5.90
6.51
3.22
6.58
5.78
4.90
7.40
-
-
-
-
-
-
-
-
-
-
-
-
-
-
1.29
1.28
1.24
0.911
1.44
1.31
1.25
Potential Exposure in OH Preschool Children (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
123
106
17
39
71
67
56
125
108
17
40
72
69
56
115
99
16
35
68
63
52
6.5
7.5
0.0
12.8
4.2
0.0
14.3
4.0
4.6
0.0
5.0
2.8
2.9
5.4
87.0
88.9
75.0
97.1
83.8
82.5
92.3
-
-
-
-
-
-
-
-
-
-
-
-
-
-
30.0
32.5
14.4
21.8
35.4
24.7
36.4
-
-
-
-
-
-
-
-
-
-
-
-
-
-
54.6
58.1
16.6
21.0
68.2
44.5
64.6
-
-
-
-
-
-
-
-
-
-
-
-
-
-
13.6
15.0
7.42
15.2
13.3
11.3
17.0
-
-
-
-
-
-
-
-
-
-
-
-
-
-
1.29
1.28
1.24
0.911
1.44
1.31
1.25
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                   M-52

-------
Table M-13b.   Cyfluthrin (68359-37-5):  Range of Potential Exposure in OH Preschool Children.
                Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
123
106
17
39
71
67
56
125
108
17
40
72
69
56
115
99
16
35
68
63
52

-------
Table M-13c.   Cyfluthrin (68359-37-5):  Estimates of Potential Absorbed Dose in OH Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
123
106
17
39
71
67
56
125
108
17
40
72
69
56
115
99
16
35
68
63
52
6.5
7.5
0.0
12.8
4.2
0.0
14.3
4.0
4.6
0.0
5.0
2.8
2.9
5.4
87.0
88.9
75.0
97.1
83.8
82.5
92.3
-
-
-
-
-
-
-
-
-
-
-
-
-
-
0.388
0.422
0.184
0.280
0.463
0.350
0.435
-
-
-
-
-
-
-
-
-
-
-
-
-
-
0.742
0.791
0.230
0.334
0.924
0.789
0.687
-
-
-
-
-
-
-
-
-
-
-
-
-
-
0.170
0.188
0.091
0.188
0.167
0.146
0.203
-
-
-
-
-
-
-
-
-
-
-
-
-
-
1.32
1.30
1.28
0.910
1.47
1.35
1.27
Potential Absorbed Dose in OH Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
123
106
17
39
71
67
56
125
108
17
40
72
69
56
115
99
16
35
68
63
52
6.5
7.5
0.0
12.8
4.2
0.0
14.3
4.0
4.6
0.0
5.0
2.8
2.9
5.4
87.0
88.9
75.0
97.1
83.8
82.5
92.3
-
-
-
-
-
-
-
-
-
-
-
-
-
-
0.894
0.971
0.423
0.644
1.07
0.807
1.00
-
-
-
-
-
-
-
-
-
-
-
-
-
-
1.71
1.82
0.529
0.770
2.13
1.82
1.58
-
-
-
-
-
-
-
-
-
-
-
-
-
-
0.391
0.432
0.210
0.433
0.384
0.337
0.468
-
-
-
-
-
-
-
-
-
-
-
-
-
-
1.32
1.30
1.28
0.910
1.47
1.35
1.27
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      M-54

-------
Table M-13d.   Cyfluthrin (68359-37-5): Range of Potential Absorbed Dose in OH Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
123
106
17
39
71
67
56
125
108
17
40
72
69
56
115
99
16
35
68
63
52

-------
Table M-14a.   Diazinon (333-41-5):  Estimates of Potential Exposure in OH Preschool Children.
                 Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Potential Exposure
-Aggregated
(ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
125
108
17
40
72
69
56
116
99
17
35
68
63
53
112
95
17
32
67
63
49
99.2
99.1
100.0
100.0
98.6
98.6
100.0
25.6
26.9
17.6
42.5
19.4
11.6
42.9
99.1
99.0
100.0
100.0
98.5
98.4
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
Potential Exposure in OH
Potential Exposure
via Inhalation
(p moles/day)
Potential Exposure
via Dietary
Ingestion
(p moles/day)
Potential Exposure
via Indirect
Ingestion
(p moles/day)
Potential Exposure
-Aggregated
(p moles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
125
108
17
40
72
69
56
116
99
17
35
68
63
53
112
95
17
32
67
63
49
99.2
99.1
100.0
100.0
98.6
98.6
100.0
25.6
26.9
17.6
42.5
19.4
11.6
42.9
99.1
99.0
100.0
100.0
98.5
98.4
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
59.0
63.2
32.0
75.9
32.8
53.4
65.8
-
-
-
-
-
-
-
49.1
56.1
8.46
9.05
21.9
82.1
9.94
142
153
79.4
116
86.5
167
110
Preschool Children
194
208
105
249
108
176
216
-
-
-
-
-
-
-
161
184
27.8
29.7
72.0
270
32.7
466
503
261
382
284
547
362
183
195
43.8
169
110
209
145
-
-
-
-
-
-
-
367
397
16.1
30.0
134
496
26.0
534
579
88.0
190
183
699
162
12.0
11.7
14.4
16.9
9.12
9.36
16.5
-
-
-
-
-
-
-
1.50
1.55
1.24
1.81
1.31
1.03
2.36
54.1
53.9
55.1
66.2
46.3
46.0
66.6
1.46
1.49
1.26
1.58
1.27
1.36
1.53
-
-
-
-
-
-
-
1.93
1.93
1.95
1.63
1.90
2.11
1.59
0.980
1.02
0.784
0.906
0.868
1.02
0.900
pmoles/day)
600
642
144
554
362
688
475
-
-
-
-
-
-
-
1,210
1,300
52.8
98.6
440
1,630
85.4
1,760
1,900
289
625
601
2,300
533
39.6
38.5
47.2
55.7
30.0
30.8
54.1
-
-
-
-
-
-
-
4.93
5.10
4.06
5.96
4.30
3.37
7.75
178
177
181
217
152
151
219
1.46
1.49
1.26
1.58
1.27
1.36
1.53
-
-
-
-
-
-
-
1.93
1.93
1.95
1.63
1.90
2.11
1.59
0.980
1.02
0.784
0.906
0.868
1.02
0.900
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                   M-56

-------
Table M-14b.   Diazinon (333-41-5): Range of Potential Exposure in OH Preschool Children.
                Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Potential Exposure
- Aggregated
(ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
125
108
17
40
72
69
56
116
99
17
35
68
63
53
112
95
17
32
67
63
49
Potential E
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Potential Exposure
-Aggregated
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
125
108
17
40
72
69
56
116
99
17
35
68
63
53
112
95
17
32
67
63
49

-------
Table M-14c.   Diazinon (333-41-5):  Estimates of Potential Absorbed Dose in OH Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Potential Absorbed
Dose - Aggregated
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
125
108
17
40
72
69
56
116
99
17
35
68
63
53
112
95
17
32
67
63
49
99.2
99.1
100.0
100.0
98.6
98.6
100.0
25.6
26.9
17.6
42.5
19.4
11.6
42.9
99.1
99.0
100.0
100.0
98.5
98.4
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
1.82
1.96
0.926
2.26
0.859
1.75
1.90
-
-
-
-
-
-
-
1.81
2.08
0.250
0.272
0.630
3.09
0.291
4.62
5.04
2.30
3.39
2.38
5.81
3.08
6.43
6.89
1.34
5.13
2.71
7.75
4.37
-
-
-
-
-
-
-
14.7
15.9
0.497
0.895
3.88
19.9
0.777
21.3
23.1
2.53
5.56
4.99
28.1
4.71
0.345
0.335
0.414
0.476
0.263
0.277
0.451
-
-
-
-
-
-
-
0.043
0.045
0.036
0.052
0.038
0.031
0.065
1.56
1.55
1.59
1.89
1.33
1.37
1.83
1.48
1.51
1.25
1.63
1.24
1.38
1.56
-
-
-
-
-
-
-
1.94
1.95
1.96
1.66
1.90
2.14
1.61
0.988
1.02
0.796
0.932
0.832
1.03
0.910
Potential Absorbed Dose in OH Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose - Aggregated
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
125
108
17
40
72
69
56
116
99
17
35
68
63
53
112
95
17
32
67
63
49
99.2
99.1
100.0
100.0
98.6
98.6
100.0
25.6
26.9
17.6
42.5
19.4
11.6
42.9
99.1
99.0
100.0
100.0
98.5
98.4
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
5.97
6.44
3.04
7.42
2.82
5.76
6.24
-
-
-
-
-
-
-
5.95
6.83
0.822
0.894
2.07
10.2
0.957
15.2
16.5
7.54
11.1
7.83
19.1
10.1
21.1
22.7
4.42
16.8
8.89
25.5
14.4
-
-
-
-
-
-
-
48.2
52.2
1.63
2.94
12.7
65.3
2.55
69.8
75.7
8.33
18.3
16.4
92.3
15.5
1.13
1.10
1.36
1.56
0.864
0.912
1.48
-
-
-
-
-
-
-
0.142
0.147
0.117
0.170
0.124
0.101
0.214
5.12
5.10
5.22
6.22
4.37
4.52
6.01
1.48
1.51
1.25
1.63
1.24
1.38
1.56
-
-
-
-
-
-
-
1.94
1.95
1.96
1.66
1.90
2.14
1.61
0.988
1.02
0.796
0.932
0.832
1.03
0.910
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      M-58

-------
Table M-14d.   Diazinon (333-41-5):  Range of Potential Absorbed Dose in OH Preschool Children.
                 Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Potential Absorbed
Dose - Aggregated
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
125
108
17
40
72
69
56
116
99
17
35
68
63
53
112
95
17
32
67
63
49

-------
Table M-15a.   Dibenzora./ilanthracene (53-70-3):  Estimates of Potential Exposure in OH
                 Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
127
110
17
41
73
69
58
115
98
17
35
67
62
53
0.8
0.9
0.0
2.6
0.0
0.0
1.8
1.6
1.8
0.0
2.4
1.4
1.4
1.7
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
-
-
-
-
-
-
-
-
-
-
-
15.4
16.9
6.69
8.55
20.7
10.6
21.1
-
-
-
-
-
-
-
-
-
-
-
-
-
-
32.0
34.3
8.41
8.33
40.8
22.3
40.1
-
-
-
-
-
-
-
-
-
-
-
-
-
-
6.99
8.05
3.11
5.62
8.26
4.69
11.2
-
-
-
-
-
-
-
-
-
-
-
-
-
-
1.19
1.11
1.36
0.965
1.34
1.20
1.02
Potential Exposure in OH Preschool Children (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
127
110
17
41
73
69
58
115
98
17
35
67
62
53
0.8
0.9
0.0
2.6
0.0
0.0
1.8
1.6
1.8
0.0
2.4
1.4
1.4
1.7
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
-
-
-
-
-
-
-
-
-
-
-
55.4
60.8
24.0
30.7
74.2
38.0
75.7
-
-
-
-
-
-
-
-
-
-
-
-
-
-
115
123
30.2
29.9
147
80.0
144
-
-
-
-
-
-
-
-
-
-
-
-
-
-
25.1
28.9
11.2
20.2
29.7
16.8
40.1
-
-
-
-
-
-
-
-
-
-
-
-
-
-
1.19
1.11
1.36
0.965
1.34
1.20
1.02
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                   M-60

-------
Table M-15b.   Dibenzora./ilanthracene (53-70-3): Range of Potential Exposure in OH Preschool
                Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
127
110
17
41
73
69
58
115
98
17
35
67
62
53

-------
Table M-15c.   Dibenzora./ilanthracene (53-70-3):  Estimates of Potential Absorbed Dose in OH
                 Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
127
110
17
41
73
69
58
115
98
17
35
67
62
53
0.8
0.9
0.0
2.6
0.0
0.0
1.8
1.6
1.8
0.0
2.4
1.4
1.4
1.7
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
-
-
-
-
-
-
-
-
-
-
-
0.458
0.506
0.186
0.263
0.611
0.354
0.581
-
-
-
-
-
-
-
-
-
-
-
-
-
-
0.924
0.990
0.225
0.301
1.17
0.905
0.941
-
-
-
-
-
-
-
-
-
-
-
-
-
-
0.201
0.232
0.089
0.161
0.239
0.140
0.308
-
-
-
-
-
-
-
-
-
-
-
-
-
-
1.21
1.14
1.32
1.01
1.35
1.23
1.05
Potential Absorbed Dose in OH Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
127
110
17
41
73
69
58
115
98
17
35
67
62
53
0.8
0.9
0.0
2.6
0.0
0.0
1.8
1.6
1.8
0.0
2.4
1.4
1.4
1.7
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
-
-
-
-
-
-
-
-
-
-
-
1.65
1.82
0.667
0.943
2.20
1.27
2.09
-
-
-
-
-
-
-
-
-
-
-
-
-
-
3.32
3.56
0.810
1.08
4.20
3.25
3.38
-
-
-
-
-
-
-
-
-
-
-
-
-
-
0.724
0.833
0.321
0.577
0.857
0.503
1.11
-
-
-
-
-
-
-
-
-
-
-
-
-
-
1.21
1.14
1.32
1.01
1.35
1.23
1.05
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                     M-62

-------
Table M-15d.   Dibenzora./ilanthracene (53-70-3):  Range of Potential Absorbed Dose in OH
                 Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
127
110
17
41
73
69
58
115
98
17
35
67
62
53

-------
Table M-16a.   Di-n-butylphthalate (84-74-2):  Estimates of Potential Exposure in OH Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Potential Exposure
-Aggregated
(ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
107
17
38
73
69
55
48
42
6
14
30
34
14
112
96
16
35
65
61
51
43
37
6
12
27
30
13
100.0
100.0
100.0
100.0
100.0
100.0
100.0
31.3
28.6
50.0
42.9
26.7
20.6
57.1
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
2,160
2,070
2,740
2,420
2,020
1,860
2,530
-
-
22,400
-
-
-
27,200
347
363
247
286
380
270
438
19,500
18,500
25,400
24,600
16,100
14,200
31,500
1,160
1,180
844
1,530
955
847
1,380
-
-
30,200
-
-
-
38,000
432
456
227
242
523
323
523
27,600
27,500
30,200
24,000
27,900
19,400
39,100
1,870
1,770
2,620
2,010
1,780
1,630
2,200
-
-
12,500
-
-
-
15,900
224
236
164
215
224
175
301
12,200
11,700
16,200
16,600
10,600
9,780
20,600
0.568
0.581
0.319
0.638
0.544
0.556
0.542
-
-
1.11
-
-
-
0.970
0.899
0.885
0.948
0.780
0.976
0.913
0.792
0.826
0.806
0.970
0.895
0.717
0.708
0.869
Potential Exposure in OH Preschool Children (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Potential Exposure
-Aggregated
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
107
17
38
73
69
55
48
42
6
14
30
34
14
112
96
16
35
65
61
51
43
37
6
12
27
30
13
100.0
100.0
100.0
100.0
100.0
100.0
100.0
31.3
28.6
50.0
42.9
26.7
20.6
57.1
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
7,760
7,420
9,850
8,710
7,260
6,680
9,100
-
-
80,500
-
-
-
97,800
1,250
1,310
886
1,030
1,360
971
1,570
69,900
66,400
91,200
88,400
57,900
51,100
113,000
4,160
4,230
3,030
5,480
3,430
3,040
4,940
-
-
109,000
-
-
-
136,000
1,550
1,640
814
869
1,880
1,160
1,880
99,200
98,800
109,000
86,300
100,000
69,700
141,000
6,700
6,350
9,400
7,220
6,390
5,870
7,920
-
-
44,700
-
-
-
57,200
804
847
590
772
805
628
1,080
44,000
42,100
58,200
59,800
38,100
35,100
73,900
0.568
0.581
0.319
0.638
0.544
0.556
0.542
-
-
1.11
-
-
-
0.970
0.899
0.885
0.948
0.780
0.976
0.913
0.792
0.826
0.806
0.970
0.895
0.717
0.708
0.869
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                   M-64

-------
Table M-16b.   Di-n-butylphthalate (84-74-2):  Range of Potential Exposure in OH Preschool
                Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Potential Exposure
- Aggregated
(ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
107
17
38
73
69
55
48
42
6
14
30
34
14
112
96
16
35
65
61
51
43
37
6
12
27
30
13
286
286
1,540
475
286
286
636

-------
Table M-16c.   Di-n-butylphthalate (84-74-2):  Estimates of Potential Absorbed Dose in OH
                 Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Potential Absorbed
Dose - Aggregated
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
107
17
38
73
69
55
48
42
6
14
30
34
14
112
96
16
35
65
61
51
43
37
6
12
27
30
13
100.0
100.0
100.0
100.0
100.0
100.0
100.0
31.3
28.6
50.0
42.9
26.7
20.6
57.1
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
63.1
60.3
80.8
72.0
58.0
55.1
73.2
-
-
679
-
-
-
687
10.2
10.6
7.43
8.81
10.9
8.40
12.2
539
502
765
657
440
428
796
39.3
40.1
29.2
55.4
28.4
25.7
50.0
-
-
958
-
-
-
903
12.2
12.8
7.18
8.97
14.2
10.4
13.8
703
662
961
625
656
561
931
53.4
50.5
75.4
56.4
51.2
48.4
60.3
-
-
361
-
-
-
414
6.43
6.78
4.65
6.14
6.45
5.22
8.24
353
337
470
467
301
296
530
0.593
0.601
0.407
0.723
0.526
0.544
0.634
-
-
1.14
-
-
-
0.950
0.939
0.915
1.04
0.861
1.000
0.963
0.855
0.803
0.772
1.01
0.813
0.724
0.724
0.856
Potential Absorbed Dose in OH Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose - Aggregated
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
107
17
38
73
69
55
48
42
6
14
30
34
14
112
96
16
35
65
61
51
43
37
6
12
27
30
13
100.0
100.0
100.0
100.0
100.0
100.0
100.0
31.3
28.6
50.0
42.9
26.7
20.6
57.1
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
227
217
290
259
208
198
263
-
-
2,440
-
-
-
2,470
36.5
38.1
26.7
31.7
39.3
30.2
44.0
1,940
1,800
2,750
2,360
1,580
1,540
2,860
141
144
105
199
102
92.4
180
-
-
3,440
-
-
-
3,240
43.7
45.9
25.8
32.2
51.2
37.4
49.6
2,530
2,380
3,450
2,240
2,360
2,020
3,350
192
182
271
202
184
174
217
-
-
1,300
-
-
-
1,490
23.1
24.4
16.7
22.1
23.2
18.8
29.6
1,270
1,210
1,690
1,680
1,080
1,060
1,900
0.593
0.601
0.407
0.723
0.526
0.544
0.634
-
-
1.14
-
-
-
0.950
0.939
0.915
1.04
0.861
1.000
0.963
0.855
0.803
0.772
1.01
0.813
0.724
0.724
0.856
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      M-66

-------
Table M-16d.   Di-n-butylphthalate (84-74-2):  Range of Potential Absorbed Dose in OH Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Potential Absorbed
Dose - Aggregated
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
107
17
38
73
69
55
48
42
6
14
30
34
14
112
96
16
35
65
61
51
43
37
6
12
27
30
13
9.83
9.83
24.6
11.1
9.83
9.83
11.1

-------
Table M-17a.   p.p'-DDE (72-55-9):  Estimates of Potential Exposure in OH Preschool Children.
                 Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
125
108
17
40
72
69
56
116
99
17
35
68
63
53
40.0
38.9
47.1
46.2
41.1
36.2
44.6
82.4
83.3
76.5
85.0
79.2
76.8
89.3
67.2
64.6
82.4
74.3
66.2
63.5
71.7
-
-
-
-
-
-
-
107
111
82.3
107
109
104
111
0.559
0.599
0.322
0.535
0.530
0.561
0.556
-
-
-
-
-
-
-
138
146
51.1
177
125
155
114
0.908
0.972
0.262
0.949
0.731
0.911
0.912
-
-
-
-
-
-
-
71.5
72.3
66.5
69.8
70.3
65.7
79.4
0.253
0.257
0.229
0.250
0.261
0.250
0.256
-
-
-
-
-
-
-
0.869
0.894
0.703
0.843
0.932
0.903
0.820
1.25
1.30
0.888
1.26
1.21
1.27
1.24
Potential Exposure in OH Preschool Children (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
125
108
17
40
72
69
56
116
99
17
35
68
63
53
40.0
38.9
47.1
46.2
41.1
36.2
44.6
82.4
83.3
76.5
85.0
79.2
76.8
89.3
67.2
64.6
82.4
74.3
66.2
63.5
71.7
-
-
-
-
-
-
-
337
349
259
337
343
327
350
1.76
1.88
1.01
1.68
1.67
1.76
1.75
—
-
-
-
-
-
-
432
460
161
555
392
486
359
2.85
3.05
0.825
2.99
2.30
2.86
2.87
—
-
-
-
-
-
-
225
227
209
220
221
207
250
0.796
0.809
0.721
0.787
0.821
0.787
0.806
-
-
-
-
-
-
-
0.869
0.894
0.703
0.843
0.932
0.903
0.820
1.25
1.30
0.888
1.26
1.21
1.27
1.24
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                   M-68

-------
Table M-17b.   p.p'-DDE (72-55-9):  Range of Potential Exposure in OH Preschool Children.
                Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
125
108
17
40
72
69
56
116
99
17
35
68
63
53

-------
Table M-17c.   p.p'-DDE (72-55-9): Estimates of Potential Absorbed Dose in OH Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
125
108
17
40
72
69
56
116
99
17
35
68
63
53
40.0
38.9
47.1
46.2
41.1
36.2
44.6
82.4
83.3
76.5
85.0
79.2
76.8
89.3
67.2
64.6
82.4
74.3
66.2
63.5
71.7
-
-
-
-
-
-
-
3.10
3.22
2.31
2.97
3.22
3.03
3.18
0.017
0.018
0.010
0.017
0.015
0.017
0.017
-
-
-
-
-
-
-
3.97
4.22
1.36
4.52
3.98
4.06
3.88
0.031
0.034
0.009
0.038
0.021
0.030
0.034
-
-
-
-
-
-
-
2.05
2.07
1.91
1.98
2.02
1.95
2.18
0.007
0.007
0.007
0.007
0.008
0.007
0.007
-
-
-
-
-
-
-
0.888
0.920
0.664
0.832
0.966
0.927
0.841
1.27
1.32
0.963
1.28
1.23
1.30
1.25
Potential Absorbed Dose in OH Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
125
108
17
40
72
69
56
116
99
17
35
68
63
53
40.0
38.9
47.1
46.2
41.1
36.2
44.6
82.4
83.3
76.5
85.0
79.2
76.8
89.3
67.2
64.6
82.4
74.3
66.2
63.5
71.7
-
-
-
-
-
-
-
9.75
10.1
7.26
9.34
10.1
9.53
10.0
0.054
0.057
0.032
0.054
0.049
0.055
0.052
—
-
-
-
-
-
-
12.5
13.3
4.29
14.2
12.5
12.8
12.2
0.099
0.106
0.030
0.121
0.067
0.093
0.106
—
-
-
-
-
-
-
6.44
6.51
6.02
6.23
6.35
6.12
6.86
0.023
0.023
0.021
0.022
0.024
0.024
0.022
-
-
-
-
-
-
-
0.888
0.920
0.664
0.832
0.966
0.927
0.841
1.27
1.32
0.963
1.28
1.23
1.30
1.25
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      M-70

-------
Table M-17d.   p.p'-DDE (72-55-9): Range of Potential Absorbed Dose in OH Preschool Children.
                 Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
125
108
17
40
72
69
56
116
99
17
35
68
63
53

-------
Table M-18a.   2.4-D (2.4-dichlorophenoxyacetic acid) (94-75-7): Estimates of Potential Exposure
                in OH Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Potential Exposure
-Aggregated
(ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
105
96
9
34
62
63
42
127
110
17
41
73
69
58
115
99
16
35
67
62
53
95
87
8
29
57
58
37
74.3
74.0
77.8
70.6
72.6
66.7
85.7
54.3
59.1
23.5
63.4
54.8
44.9
65.5
99.1
99.0
100.0
97.1
100.0
98.4
100.0
98.9
98.9
100.0
96.6
100.0
98.3
100.0
3.63
3.23
7.90
3.39
3.43
3.54
3.78
319
348
-
463
274
-
391
18.1
20.0
5.92
5.77
24.8
21.0
14.7
350
373
106
444
335
311
413
4.54
3.55
9.78
4.30
3.32
3.34
5.95
759
811
-
924
715
-
786
52.1
55.9
6.67
9.66
66.7
67.4
24.5
736
766
25.1
699
808
802
625
2.29
2.15
4.29
2.14
2.32
2.38
2.15
150
155
-
182
142
-
180
5.42
5.89
3.22
2.53
7.53
5.13
5.77
175
184
103
205
169
154
214
0.888
0.837
1.19
0.866
0.864
0.883
0.902
0.968
1.02
-
1.15
0.908
-
1.03
1.52
1.54
1.25
1.35
1.50
1.64
1.38
0.975
1.00
0.250
1.11
0.957
0.929
1.03
Potential Exposure in OH Preschool Children (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Potential Exposure
-Aggregated
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
105
96
9
34
62
63
42
127
110
17
41
73
69
58
115
99
16
35
67
62
53
95
87
8
29
57
58
37
74.3
74.0
77.8
70.6
72.6
66.7
85.7
54.3
59.1
23.5
63.4
54.8
44.9
65.5
99.1
99.0
100.0
97.1
100.0
98.4
100.0
98.9
98.9
100.0
96.6
100.0
98.3
100.0
16.4
14.6
35.7
15.3
15.5
16.0
17.1
1,440
1,570
-
2,090
1,240
-
1,770
81.8
90.6
26.8
26.1
112
94.9
66.4
1,590
1,690
478
2,010
1,510
1,410
1,870
20.5
16.1
44.3
19.4
15.0
15.1
26.9
3,430
3,670
-
4,180
3,230
-
3,560
236
253
30.2
43.7
302
305
111
3,330
3,460
114
3,160
3,660
3,630
2,830
10.3
9.75
19.4
9.69
10.5
10.8
9.74
677
702
-
825
643
-
814
24.5
26.7
14.6
11.4
34.1
23.2
26.1
793
833
465
927
766
698
968
0.888
0.837
1.19
0.866
0.864
0.883
0.902
0.968
1.02
-
1.15
0.908
-
1.03
1.52
1.54
1.25
1.35
1.50
1.64
1.38
0.975
1.00
0.250
1.11
0.957
0.929
1.03
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                   M-72

-------
Table M-18b.   2.4-D (2.4-dichlorophenoxyacetic acid) (94-75-7): Range of Potential Exposure in
                OH Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Potential Exposure
- Aggregated
(ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
105
96
9
34
62
63
42
127
110
17
41
73
69
58
115
99
16
35
67
62
53
95
87
8
29
57
58
37

-------
Table M-18c.   2.4-D (2.4-dichlorophenoxyacetic acid) (94-75-7): Estimates of Potential Absorbed
                 Dose in OH Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Potential Absorbed
Dose - Aggregated
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
105
96
9
34
62
63
42
127
110
17
41
73
69
58
115
99
16
35
67
62
53
95
87
8
29
57
58
37
74.3
74.0
77.8
70.6
72.6
66.7
85.7
54.3
59.1
23.5
63.4
54.8
44.9
65.5
99.1
99.0
100.0
97.1
100.0
98.4
100.0
98.9
98.9
100.0
96.6
100.0
98.3
100.0
0.109
0.095
0.251
0.102
0.100
0.106
0.112
9.19
10.0
-
12.5
8.35
-
10.5
0.528
0.585
0.172
0.179
0.712
0.633
0.405
10.1
10.7
3.31
11.5
10.3
9.70
10.7
0.146
0.111
0.323
0.136
0.100
0.104
0.194
23.7
25.4
-
26.0
24.4
-
22.1
1.49
1.60
0.204
0.315
1.91
1.95
0.648
23.5
24.5
1.13
17.7
27.6
27.4
15.8
0.066
0.062
0.133
0.060
0.068
0.071
0.059
4.29
4.45
-
5.15
4.09
-
4.95
0.156
0.170
0.092
0.072
0.217
0.153
0.159
5.05
5.28
3.14
5.76
4.93
4.59
5.87
0.912
0.857
1.22
0.951
0.841
0.879
0.960
0.961
1.01
-
1.10
0.930
-
1.01
1.53
1.55
1.27
1.38
1.49
1.64
1.40
0.963
0.990
0.360
1.06
0.967
0.939
0.994
Potential Absorbed Dose in OH Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose - Aggregated
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
105
96
9
34
62
63
42
127
110
17
41
73
69
58
115
99
16
35
67
62
53
95
87
8
29
57
58
37
74.3
74.0
77.8
70.6
72.6
66.7
85.7
54.3
59.1
23.5
63.4
54.8
44.9
65.5
99.1
99.0
100.0
97.1
100.0
98.4
100.0
98.9
98.9
100.0
96.6
100.0
98.3
100.0
0.491
0.430
1.14
0.460
0.451
0.481
0.506
41.6
45.4
-
56.5
37.8
-
47.7
2.39
2.65
0.779
0.809
3.22
2.86
1.83
45.7
48.5
15.0
52.2
46.5
43.9
48.6
0.660
0.504
1.46
0.617
0.452
0.470
0.878
107
115
-
118
111
-
00.0
6.76
7.25
0.924
1.43
8.63
8.80
2.93
106
111
5.09
79.9
125
124
71.5
0.298
0.279
0.601
0.270
0.308
0.322
0.266
19.4
20.1
-
23.3
18.5
-
22.4
0.705
0.769
0.415
0.327
0.981
0.692
0.721
22.8
23.9
14.2
26.0
22.3
20.7
26.6
0.912
0.857
1.22
0.951
0.841
0.879
0.960
0.961
1.01
-
1.10
0.930
-
1.01
1.53
1.55
1.27
1.38
1.49
1.64
1.40
0.963
0.990
0.360
1.06
0.967
0.939
0.994
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                     M-74

-------
Table M-18d.   2.4-D (2.4-dichlorophenoxyacetic acid) (94-75-7): Range of Potential Absorbed
                 Dose in OH Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Potential Absorbed
Dose - Aggregated
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
105
96
9
34
62
63
42
127
110
17
41
73
69
58
115
99
16
35
67
62
53
95
87
8
29
57
58
37

-------
Table M-19a.   lndenon.2.3-cc/|pvrene (193-39-5):  Estimates of Potential Exposure in OH
                Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
127
110
17
41
73
69
58
115
98
17
35
67
62
53
36.8
41.7
5.9
64.1
27.4
20.3
57.1
7.1
8.2
0.0
12.2
5.5
1.4
13.8
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
1.11
-
-
0.914
-
-
-
-
-
-
-
75.7
83.5
30.9
40.2
102
51.8
104
-
-
-
1.45
-
-
1.14
-
-
-
-
-
-
-
164
176
38.3
43.7
209
115
205
-
-
-
0.778
-
-
0.706
-
-
-
-
-
-
-
32.8
37.7
14.8
25.5
39.4
22.1
52.2
-
-
-
0.692
-
-
0.570
-
-
-
-
-
-
-
1.20
1.14
1.28
0.991
1.34
1.19
1.06
Potential Exposure in OH Preschool Children (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
127
110
17
41
73
69
58
115
98
17
35
67
62
53
36.8
41.7
5.9
64.1
27.4
20.3
57.1
7.1
8.2
0.0
12.2
5.5
1.4
13.8
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
4.02
-
-
3.31
-
-
-
-
-
-
-
274
302
112
146
371
187
375
—
-
-
5.26
-
-
4.11
-
-
-
-
-
-
-
593
636
139
158
755
417
741
—
-
-
2.81
-
-
2.56
-
-
-
-
-
-
-
119
136
53.6
92.5
143
79.8
189
-
-
-
0.692
-
-
0.570
-
-
-
-
-
-
-
1.20
1.14
1.28
0.991
1.34
1.19
1.06
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                   M-76

-------
Table M-19b.   lndenon.2.3-cc/|pvrene (193-39-5): Range of Potential Exposure in OH Preschool
                Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
127
110
17
41
73
69
58
115
98
17
35
67
62
53

-------
Table M-19c.   lndenon.2.3-cc/|pvrene (193-39-5): Estimates of Potential Absorbed Dose in OH
                 Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
127
110
17
41
73
69
58
115
98
17
35
67
62
53
36.8
41.7
5.9
64.1
27.4
20.3
57.1
7.1
8.2
0.0
12.2
5.5
1.4
13.8
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
0.033
-
-
0.026
-
-
-
-
-
-
-
2.25
2.50
0.865
1.25
3.04
1.74
2.86
-
-
-
0.044
-
-
0.033
-
-
-
-
-
-
-
4.74
5.08
1.06
1.56
6.00
4.68
4.79
-
-
-
0.022
-
-
0.019
-
-
-
-
-
-
-
0.946
1.09
0.427
0.730
1.14
0.659
1.44
-
-
-
0.760
-
-
0.632
-
-
-
-
-
-
-
1.22
1.17
1.25
1.05
1.35
1.22
1.09
Potential Absorbed Dose in OH Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
127
110
17
41
73
69
58
115
98
17
35
67
62
53
36.8
41.7
5.9
64.1
27.4
20.3
57.1
7.1
8.2
0.0
12.2
5.5
1.4
13.8
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
0.119
-
-
0.094
-
-
-
-
-
-
-
8.16
9.03
3.13
4.51
11.0
6.30
10.3
—
-
-
0.160
-
-
0.119
-
-
-
-
-
-
-
17.2
18.4
3.85
5.66
21.7
16.9
17.3
—
-
-
0.079
-
-
0.070
-
-
-
-
-
-
-
3.42
3.93
1.54
2.64
4.12
2.39
5.22
-
-
-
0.760
-
-
0.632
-
-
-
-
-
-
-
1.22
1.17
1.25
1.05
1.35
1.22
1.09
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                     M-78

-------
Table M-19d.   lndenon.2.3-cc/|pvrene (193-39-5):  Range of Potential Absorbed Dose in OH
                 Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
127
110
17
41
73
69
58
115
98
17
35
67
62
53

-------
Table M-20a.   Pentachlorophenol (87-86-5): Estimates of Potential Exposure in OH Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
95
84
11
29
58
54
41
127
110
17
41
73
69
58
115
99
16
35
67
62
53
94.7
94.0
100.0
96.6
93.1
96.3
92.7
29.9
33.6
5.9
31.7
31.5
21.7
39.7
98.3
98.0
100.0
100.0
97.0
96.8
100.0
37.2
36.4
42.7
21.9
43.8
47.0
24.2
-
-
-
-
-
-
-
4.61
4.85
3.09
4.50
3.33
4.90
4.27
62.5
63.8
53.8
21.5
76.2
79.1
24.4
-
-
-
-
-
-
-
11.9
12.7
2.74
11.3
3.42
13.7
9.46
18.4
17.3
29.7
13.8
19.7
22.7
13.9
-
-
-
-
-
-
-
1.99
1.96
2.20
1.89
1.99
2.02
1.96
1.19
1.23
0.773
1.04
1.28
1.17
1.18
-
-
-
-
-
-
-
1.17
1.22
0.846
1.14
1.08
1.19
1.16
Potential Exposure in OH Preschool Children (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
95
84
11
29
58
54
41
127
110
17
41
73
69
58
115
99
16
35
67
62
53
94.7
94.0
100.0
96.6
93.1
96.3
92.7
29.9
33.6
5.9
31.7
31.5
21.7
39.7
98.3
98.0
100.0
100.0
97.0
96.8
100.0
139
137
160
82.4
164
177
90.7
-
-
-
-
-
-
-
17.3
18.2
11.6
16.9
12.5
18.4
16.0
235
240
202
80.6
286
297
91.5
-
-
-
-
-
-
-
44.6
47.8
10.3
42.6
12.8
51.3
35.5
69.0
64.8
111
51.7
74.1
85.1
52.3
-
-
-
-
-
-
-
7.48
7.36
8.27
7.11
7.48
7.57
7.37
1.19
1.23
0.773
1.04
1.28
1.17
1.18
-
-
-
-
-
-
-
1.17
1.22
0.846
1.14
1.08
1.19
1.16
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                   M-80

-------
Table M-20b.   Pentachlorophenol (87-86-5): Range of Potential Exposure in OH Preschool
                Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
95
84
11
29
58
54
41
127
110
17
41
73
69
58
115
99
16
35
67
62
53

-------
Table M-20c.   Pentachlorophenol (87-86-5):  Estimates of Potential Absorbed Dose in OH
                 Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
95
84
11
29
58
54
41
127
110
17
41
73
69
58
115
99
16
35
67
62
53
94.7
94.0
100.0
96.6
93.1
96.3
92.7
29.9
33.6
5.9
31.7
31.5
21.7
39.7
98.3
98.0
100.0
100.0
97.0
96.8
100.0
1.12
1.10
1.31
0.695
1.31
1.46
0.687
-
-
-
-
-
-
-
0.152
0.162
0.095
0.155
0.097
0.167
0.136
1.99
2.02
1.89
0.823
2.41
2.52
0.764
-
-
-
-
-
-
-
0.479
0.515
0.093
0.463
0.099
0.553
0.380
0.526
0.494
0.849
0.388
0.569
0.667
0.384
-
-
-
-
-
-
-
0.057
0.056
0.063
0.054
0.057
0.060
0.054
1.22
1.25
0.813
1.13
1.27
1.20
1.19
-
-
-
-
-
-
-
1.23
1.27
0.955
1.21
1.11
1.26
1.20
Potential Absorbed Dose in OH Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
95
84
11
29
58
54
41
127
110
17
41
73
69
58
115
99
16
35
67
62
53
94.7
94.0
100.0
96.6
93.1
96.3
92.7
29.9
33.6
5.9
31.7
31.5
21.7
39.7
98.3
98.0
100.0
100.0
97.0
96.8
100.0
4.22
4.13
4.92
2.61
4.90
5.47
2.58
-
-
-
-
-
-
-
0.572
0.607
0.355
0.581
0.364
0.626
0.509
7.48
7.57
7.09
3.09
9.05
9.45
2.87
-
-
-
-
-
-
-
1.80
1.93
0.349
1.74
0.373
2.08
1.43
1.97
1.85
3.19
1.46
2.14
2.50
1.44
-
-
-
-
-
-
-
0.215
0.212
0.236
0.203
0.215
0.226
0.204
1.22
1.25
0.813
1.13
1.27
1.20
1.19
-
-
-
-
-
-
-
1.23
1.27
0.955
1.21
1.11
1.26
1.20
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                     M-82

-------
Table M-20d.   Pentachlorophenol (87-86-5): Range of Potential Absorbed Dose in OH Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
95
84
11
29
58
54
41
127
110
17
41
73
69
58
115
99
16
35
67
62
53

-------
Table M-21a.   c/s-Permethrin (61949-76-6):  Estimates of Potential Exposure in OH Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Potential Exposure
-Aggregated
(ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
124
107
17
40
72
68
56
116
99
17
35
68
63
53
111
94
17
32
67
62
49
39.2
35.2
64.7
46.2
34.2
31.9
48.2
38.7
40.2
29.4
52.5
31.9
23.5
57.1
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
3.12
-
-
-
-
-
-
-
1,160
-
-
2,940
61.5
51.4
120
64.8
46.5
41.7
85.1
665
724
338
1,460
252
312
1,110
-
-
1.84
-
-
-
-
-
-
-
2,860
-
-
15,100
139
94.3
283
105
85.7
80.5
184
1,960
2,110
760
3,150
624
1,130
2,620
-
-
2.79
-
-
-
-
-
-
-
97.6
-
-
109
21.3
18.5
47.9
22.8
18.8
16.1
29.7
118
118
123
195
90.7
80.4
193
-
-
0.444
-
-
-
-
-
-
-
2.02
-
-
2.08
1.38
1.37
1.14
1.46
1.30
1.32
1.38
1.46
1.52
1.16
1.86
1.15
1.17
1.65
Potential Exposure in OH Preschool Children (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Potential Exposure
-Aggregated
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
124
107
17
40
72
68
56
116
99
17
35
68
63
53
111
94
17
32
67
62
49
39.2
35.2
64.7
46.2
34.2
31.9
48.2
38.7
40.2
29.4
52.5
31.9
23.5
57.1
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
7.97
-
-
-
-
-
-
-
2,970
-
-
7,500
157
131
307
166
119
107
218
1,700
1,850
865
3,730
645
797
2,840
-
-
4.70
-
-
-
-
-
-
-
7,310
-
-
38,700
355
241
723
270
219
206
471
5,020
5,380
1,940
8,050
1,600
2,880
6,690
-
-
7.12
-
-
-
-
-
-
-
249
-
-
279
54.4
47.4
122
58.3
48.0
41.2
75.8
303
301
313
499
232
205
494
-
-
0.444
-
-
-
-
-
-
-
2.02
-
-
2.08
1.38
1.37
1.14
1.46
1.30
1.32
1.38
1.46
1.52
1.16
1.86
1.15
1.17
1.65
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                   M-84

-------
Table M-21b.   c/s-Permethrin (61949-76-6):  Range of Potential Exposure in OH Preschool
                Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Potential Exposure
- Aggregated
(ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
124
107
17
40
72
68
56
116
99
17
35
68
63
53
111
94
17
32
67
62
49

-------
Table M-21c.   c/s-Permethrin (61949-76-6):  Estimates of Potential Absorbed Dose in OH
                 Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Potential Absorbed
Dose - Aggregated
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
124
107
17
40
72
68
56
116
99
17
35
68
63
53
111
94
17
32
67
62
49
39.2
35.2
64.7
46.2
34.2
31.9
48.2
38.7
40.2
29.4
52.5
31.9
23.5
57.1
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
0.086
-
-
-
-
-
-
-
30.0
-
-
98.4
1.92
1.54
4.18
2.01
1.36
1.23
2.75
18.3
19.5
11.8
37.8
7.11
9.19
29.9
-
-
0.039
-
-
-
-
-
-
-
74.4
-
-
553
4.92
2.86
10.8
3.44
2.45
2.30
6.77
54.1
57.5
28.3
82.0
18.0
36.7
68.9
-
-
0.080
-
-
-
-
-
-
-
2.77
-
-
3.00
0.614
0.534
1.38
0.652
0.543
0.481
0.819
3.40
3.37
3.53
5.59
2.61
2.39
5.30
-
-
0.371
-
-
-
-
-
-
-
1.98
-
-
2.09
1.41
1.39
1.24
1.50
1.33
1.34
1.45
1.45
1.48
1.27
1.81
1.13
1.14
1.67
Potential Absorbed Dose in OH Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose - Aggregated
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
124
107
17
40
72
68
56
116
99
17
35
68
63
53
111
94
17
32
67
62
49
39.2
35.2
64.7
46.2
34.2
31.9
48.2
38.7
40.2
29.4
52.5
31.9
23.5
57.1
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
0.221
-
-
-
-
-
-
-
76.7
-
-
251
4.92
3.92
10.7
5.14
3.48
3.13
7.03
46.8
49.8
30.3
96.5
18.2
23.5
76.3
-
-
0.100
-
-
-
-
-
-
-
190
-
-
1,410
12.6
7.32
27.7
8.80
6.27
5.87
17.3
138
147
72.2
210
46.1
93.8
176
-
-
0.205
-
-
-
-
-
-
-
7.08
-
-
7.66
1.57
1.37
3.52
1.67
1.39
1.23
2.09
8.68
8.62
9.02
14.3
6.67
6.11
13.5
-
-
0.371
-
-
-
-
-
-
-
1.98
-
-
2.09
1.41
1.39
1.24
1.50
1.33
1.34
1.45
1.45
1.48
1.27
1.81
1.13
1.14
1.67
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected.  Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                     M-86

-------
Table M-21d.   c/s-Permethrin (61949-76-6):  Range of Potential Absorbed Dose in OH Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Potential Absorbed
Dose - Aggregated
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
124
107
17
40
72
68
56
116
99
17
35
68
63
53
111
94
17
32
67
62
49

-------
Table M-22a.  frans-Permethrin (61949-77-7):  Estimates of Potential Exposure in OH Preschool
                Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Potential Exposure
-Aggregated
(ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
124
107
17
40
72
68
56
102
85
17
28
61
60
42
97
80
17
25
60
59
38
34.4
32.4
47.1
43.6
30.1
24.6
46.4
38.7
40.2
29.4
52.5
31.9
23.5
57.1
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
-
-
-
-
-
-
-
974
-
-
2,370
61.2
50.9
113
66.9
44.0
43.3
86.7
280
284
263
250
218
277
285
-
-
-
-
-
-
-
-
-
-
2,440
-
-
12,100
153
112
282
116
106
108
200
784
832
519
644
538
880
616
-
-
-
-
-
-
-
-
-
-
89.2
-
-
98.6
16.6
14.2
36.6
18.6
14.1
12.7
24.3
87.5
83.9
106
92.7
79.4
75.4
110
-
-
-
-
-
-
-
-
-
-
1.94
-
-
2.00
1.51
1.50
1.31
1.62
1.42
1.45
1.53
1.20
1.22
1.13
1.14
1.15
1.21
1.17
Potential Exposure in OH Preschool Children (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Potential Exposure
-Aggregated
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
124
107
17
40
72
68
56
102
85
17
28
61
60
42
97
80
17
25
60
59
38
34.4
32.4
47.1
43.6
30.1
24.6
46.4
38.7
40.2
29.4
52.5
31.9
23.5
57.1
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
-
-
-
-
-
-
-
2,490
-
-
6,060
156
130
288
171
113
111
222
716
725
673
639
557
708
727
-
-
-
-
-
-
-
-
-
-
6,230
-
-
31,000
392
286
719
296
272
275
511
2,000
2,130
1,330
1,650
1,380
2,250
1,570
-
-
-
-
-
-
-
-
-
-
228
-
-
252
42.5
36.2
93.6
47.7
35.9
32.5
62.1
224
215
272
237
203
193
282
-
-
-
-
-
-
-
-
-
-
1.94
-
-
2.00
1.51
1.50
1.31
1.62
1.42
1.45
1.53
1.20
1.22
1.13
1.14
1.15
1.21
1.17
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                   M-88

-------
Table M-22b.   frans-Permethrin (61949-77-7):  Range of Potential Exposure in OH Preschool
                Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Potential Exposure
- Aggregated
(ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
124
107
17
40
72
68
56
102
85
17
28
61
60
42
97
80
17
25
60
59
38

-------
Table M-22c.   frans-Permethrin (61949-77-7):  Estimates of Potential Absorbed Dose in OH
                 Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Potential Absorbed
Dose - Aggregated
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
124
107
17
40
72
68
56
102
85
17
28
61
60
42
97
80
17
25
60
59
38
34.4
32.4
47.1
43.6
30.1
24.6
46.4
38.7
40.2
29.4
52.5
31.9
23.5
57.1
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
-
-
-
-
-
-
-
25.0
-
-
79.1
1.91
1.51
3.93
2.06
1.29
1.26
2.84
8.39
8.23
9.15
7.59
5.95
8.00
9.01
-
-
-
-
-
-
-
-
-
-
63.0
-
-
442
5.31
3.31
10.7
3.66
3.04
3.06
7.38
25.1
26.2
19.5
20.1
14.2
27.7
20.5
-
-
-
-
-
-
-
-
-
-
2.53
-
-
2.71
0.481
0.411
1.05
0.547
0.404
0.380
0.672
2.52
2.42
3.06
2.73
2.27
2.24
3.02
-
-
-
-
-
-
-
-
-
-
1.91
-
-
2.02
1.53
1.51
1.40
1.62
1.45
1.46
1.58
1.20
1.20
1.25
1.14
1.13
1.17
1.25
Potential Absorbed Dose in OH Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose - Aggregated
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
124
107
17
40
72
68
56
102
85
17
28
61
60
42
97
80
17
25
60
59
38
34.4
32.4
47.1
43.6
30.1
24.6
46.4
38.7
40.2
29.4
52.5
31.9
23.5
57.1
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
-
-
-
-
-
-
-
64.0
-
-
202
4.88
3.85
10.1
5.28
3.29
3.22
7.26
21.5
21.0
23.4
19.4
15.2
20.4
23.0
-
-
-
-
-
-
-
-
-
-
161
-
-
1,130
13.6
8.46
27.4
9.36
7.78
7.83
18.9
64.0
67.0
49.7
51.5
36.3
70.9
52.5
-
-
-
-
-
-
-
-
-
-
6.47
-
-
6.93
1.23
1.05
2.69
1.40
1.03
0.972
1.72
6.44
6.18
7.83
6.99
5.80
5.73
7.72
-
-
-
-
-
-
-
-
-
-
1.91
-
-
2.02
1.53
1.51
1.40
1.62
1.45
1.46
1.58
1.20
1.20
1.25
1.14
1.13
1.17
1.25
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                     M-90

-------
Table M-22d.   frans-Permethrin (61949-77-7):  Range of Potential Absorbed Dose in OH Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Potential Absorbed
Dose - Aggregated
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
124
107
17
40
72
68
56
102
85
17
28
61
60
42
97
80
17
25
60
59
38

-------
Table M-23a.   PCB 52 (35693-99-3):  Estimates of Potential Exposure in OH Preschool Children.
                 Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
122
105
17
36
73
69
53







115
98
17
35
67
63
52
96.7
96.2
100.0
100.0
94.5
94.2
100.0







71.3
67.3
94.1
94.3
62.7
55.6
90.4
4.54
4.28
6.13
4.43
4.62
4.63
4.43







0.469
0.495
0.324
0.332
0.542
0.499
0.433
4.61
4.21
6.54
4.55
4.91
5.53
3.08







1.18
1.27
0.230
0.452
1.45
1.49
0.629
3.21
3.08
4.13
3.16
3.16
2.91
3.64







0.217
0.211
0.252
0.205
0.229
0.196
0.244
0.840
0.832
0.871
0.822
0.883
0.964
0.632







1.08
1.13
0.755
0.926
1.14
1.15
1.00
Potential Exposure in OH Preschool Children (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
122
105
17
36
73
69
53







115
98
17
35
67
63
52
96.7
96.2
100.0
100.0
94.5
94.2
100.0







71.3
67.3
94.1
94.3
62.7
55.6
90.4
15.6
14.7
21.0
15.2
15.8
15.9
15.2







1.61
1.69
1.11
1.14
1.86
1.71
1.48
15.8
14.4
22.4
15.6
16.8
19.0
10.5







4.03
4.35
0.787
1.55
4.98
5.10
2.15
11.0
10.5
14.2
10.8
10.8
9.96
12.5







0.742
0.723
0.862
0.702
0.786
0.672
0.837
0.840
0.832
0.871
0.822
0.883
0.964
0.632







1.08
1.13
0.755
0.926
1.14
1.15
1.00
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                   M-92

-------
Table M-23b.   PCB 52 (35693-99-3):  Range of Potential Exposure in OH Preschool Children.
                Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
122
105
17
36
73
69
53







115
98
17
35
67
63
52

-------
Table M-23c.   PCB 52 (35693-99-3):  Estimates of Potential Absorbed Dose in OH Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
122
105
17
36
73
69
53







115
98
17
35
67
63
52
96.7
96.2
100.0
100.0
94.5
94.2
100.0







71.3
67.3
94.1
94.3
62.7
55.6
90.4
0.133
0.124
0.188
0.128
0.134
0.137
0.127







0.014
0.015
0.010
0.010
0.016
0.016
0.012
0.138
0.126
0.191
0.127
0.147
0.165
0.093







0.039
0.042
0.008
0.017
0.049
0.050
0.018
0.092
0.088
0.119
0.089
0.091
0.086
0.100







0.006
0.006
0.007
0.006
0.007
0.006
0.007
0.863
0.839
0.990
0.865
0.876
0.955
0.727







1.12
1.16
0.890
0.994
1.16
1.18
1.05
Potential Absorbed Dose in OH Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
122
105
17
36
73
69
53







115
98
17
35
67
63
52
96.7
96.2
100.0
100.0
94.5
94.2
100.0







71.3
67.3
94.1
94.3
62.7
55.6
90.4
0.455
0.424
0.645
0.437
0.458
0.470
0.435







0.049
0.051
0.035
0.036
0.056
0.054
0.042
0.472
0.432
0.654
0.436
0.503
0.565
0.318







0.134
0.145
0.027
0.060
0.167
0.173
0.062
0.314
0.301
0.408
0.304
0.312
0.295
0.341







0.021
0.021
0.025
0.020
0.023
0.020
0.023
0.863
0.839
0.990
0.865
0.876
0.955
0.727







1.12
1.16
0.890
0.994
1.16
1.18
1.05
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                     M-94

-------
Table M-23d.   PCB 52 (35693-99-3): Range of Potential Absorbed Dose in OH Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
122
105
17
36
73
69
53







115
98
17
35
67
63
52

-------
Table M-24a.   PCB 95 (38379-99-6):  Estimates of Potential Exposure in OH Preschool Children.
                 Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56







115
98
17
35
67
63
52
81.6
79.6
94.1
87.2
78.1
71.0
94.6







66.1
63.3
82.4
80.0
61.2
49.2
86.5
1.59
1.56
1.79
1.93
1.46
1.45
1.77







0.424
0.447
0.296
0.230
0.531
-
0.336
2.66
2.75
2.12
3.81
2.03
2.44
2.93







1.53
1.65
0.256
0.277
1.97
-
0.640
0.890
0.864
1.08
0.895
0.883
0.787
1.04







0.170
0.164
0.208
0.139
0.190
-
0.182
0.966
0.965
0.980
1.07
0.941
0.982
0.932







1.06
1.09
0.904
0.957
1.08
-
0.983
Potential Exposure in OH Preschool Children (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56







115
98
17
35
67
63
52
81.6
79.6
94.1
87.2
78.1
71.0
94.6







66.1
63.3
82.4
80.0
61.2
49.2
86.5
4.88
4.78
5.50
5.90
4.48
4.44
5.42







1.30
1.37
0.908
0.705
1.63
-
1.03
8.16
8.42
6.49
11.7
6.22
7.47
8.98







4.69
5.07
0.785
0.848
6.03
-
1.96
2.73
2.65
3.30
2.74
2.71
2.41
3.18







0.521
0.503
0.636
0.426
0.583
-
0.558
0.966
0.965
0.980
1.07
0.941
0.982
0.932







1.06
1.09
0.904
0.957
1.08
-
0.983
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                   M-96

-------
Table M-24b.   PCB 95 (38379-99-6):  Range of Potential Exposure in OH Preschool Children.
                Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56







115
98
17
35
67
63
52

-------
Table M-24c.   PCB 95 (38379-99-6):  Estimates of Potential Absorbed Dose in OH Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56







115
98
17
35
67
63
52
81.6
79.6
94.1
87.2
78.1
71.0
94.6







66.1
63.3
82.4
80.0
61.2
49.2
86.5
0.047
0.046
0.056
0.057
0.042
0.043
0.052







0.013
0.013
0.009
0.007
0.016
-
0.009
0.084
0.086
0.068
0.119
0.063
0.073
0.096







0.051
0.055
0.009
0.009
0.066
-
0.014
0.025
0.025
0.031
0.025
0.025
0.023
0.028







0.005
0.005
0.006
0.004
0.005
-
0.005
0.984
0.970
1.08
1.11
0.928
0.975
0.994







1.10
1.11
1.03
0.997
1.11
-
1.03
Potential Absorbed Dose in OH Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56







115
98
17
35
67
63
52
81.6
79.6
94.1
87.2
78.1
71.0
94.6







66.1
63.3
82.4
80.0
61.2
49.2
86.5
0.144
0.140
0.172
0.174
0.130
0.131
0.160







0.039
0.041
0.029
0.021
0.050
-
0.028
0.257
0.264
0.209
0.366
0.193
0.224
0.294







0.157
0.170
0.029
0.027
0.203
-
0.044
0.078
0.076
0.095
0.077
0.078
0.071
0.087







0.015
0.014
0.018
0.012
0.017
-
0.015
0.984
0.970
1.08
1.11
0.928
0.975
0.994







1.10
1.11
1.03
0.997
1.11
-
1.03
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                     M-98

-------
Table M-24d.   PCB 95 (38379-99-6): Range of Potential Absorbed Dose in OH Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56







115
98
17
35
67
63
52

-------
Table M-25a.   PCB 101 (37680-73-2):  Estimates of Potential Exposure in OH Preschool Children.
                 Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56







115
98
17
35
67
63
52
71.2
67.6
94.1
69.2
71.2
58.0
87.5







68.7
65.3
88.2
85.7
62.7
54.0
86.5
1.58
1.57
1.68
2.08
1.41
1.30
1.93







0.579
0.620
0.347
0.299
0.734
0.704
0.429
3.27
3.43
1.96
5.18
1.94
2.34
4.13







2.34
2.53
0.321
0.372
3.02
3.09
0.790
0.784
0.754
1.00
0.779
0.814
0.650
0.988







0.199
0.192
0.240
0.166
0.221
0.190
0.210
1.05
1.06
1.01
1.19
1.00
1.03
1.04







1.16
1.20
0.896
1.07
1.18
1.21
1.11
Potential Exposure in OH Preschool Children (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56







115
98
17
35
67
63
52
71.2
67.6
94.1
69.2
71.2
58.0
87.5







68.7
65.3
88.2
85.7
62.7
54.0
86.5
4.84
4.80
5.15
6.36
4.32
3.99
5.90







1.78
1.90
1.06
0.917
2.25
2.16
1.31
10.0
10.5
6.00
15.9
5.93
7.18
12.6







7.17
7.76
0.983
1.14
9.25
9.46
2.42
2.40
2.31
3.07
2.39
2.49
1.99
3.03







0.608
0.589
0.735
0.508
0.677
0.581
0.643
1.05
1.06
1.01
1.19
1.00
1.03
1.04







1.16
1.20
0.896
1.07
1.18
1.21
1.11
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                  M-100

-------
Table M-25b.   PCB 101 (37680-73-2):  Range of Potential Exposure in OH Preschool Children.
                Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56







115
98
17
35
67
63
52

-------
Table M-25c.   PCB 101  (37680-73-2):  Estimates of Potential Absorbed Dose in OH Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56







115
98
17
35
67
63
52
71.2
67.6
94.1
69.2
71.2
58.0
87.5







68.7
65.3
88.2
85.7
62.7
54.0
86.5
0.047
0.046
0.053
0.062
0.041
0.039
0.057







0.018
0.019
0.011
0.009
0.023
0.023
0.012
0.106
0.111
0.062
0.168
0.061
0.071
0.137







0.079
0.086
0.011
0.012
0.103
0.106
0.018
0.022
0.022
0.029
0.022
0.023
0.019
0.027







0.006
0.006
0.007
0.005
0.006
0.006
0.006
1.07
1.06
1.14
1.20
1.01
1.03
1.09







1.20
1.23
1.01
1.13
1.19
1.24
1.15
Potential Absorbed Dose in OH Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56







115
98
17
35
67
63
52
71.2
67.6
94.1
69.2
71.2
58.0
87.5







68.7
65.3
88.2
85.7
62.7
54.0
86.5
0.144
0.141
0.162
0.190
0.126
0.119
0.176







0.054
0.058
0.033
0.028
0.069
0.069
0.036
0.324
0.340
0.190
0.515
0.188
0.216
0.420







0.242
0.262
0.035
0.036
0.314
0.324
0.055
0.069
0.066
0.088
0.067
0.072
0.059
0.083







0.017
0.017
0.021
0.015
0.019
0.017
0.018
1.07
1.06
1.14
1.20
1.01
1.03
1.09







1.20
1.23
1.01
1.13
1.19
1.24
1.15
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected.  Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                     M-102

-------
Table M-25d.   PCB 101 (37680-73-2):  Range of Potential Absorbed Dose in OH Preschool
                 Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56







115
98
17
35
67
63
52

-------
Table M-26a.   3.5.6-TCP (3.5.6-trichloro-2-pyridinol) (6515-38-4): Estimates of Potential Exposure
                 in OH Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Potential Exposure
-Aggregated
(ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
110
98
12
35
62
64
46
127
110
17
41
73
69
58
116
99
17
35
68
63
53
103
91
12
32
58
58
45
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
13.4
14.4
4.74
19.4
7.46
15.9
9.86
1,130
1,090
1,360
978
1,210
1,160
1,080
4.38
4.82
1.77
6.33
3.42
3.66
5.22
1,180
1,130
1,590
1,070
1,250
1,190
1,180
29.9
31.5
2.66
30.8
7.15
38.3
9.49
1,030
1,000
1,200
691
1,230
1,230
732
9.42
10.1
1.16
14.4
5.34
6.73
11.9
1,110
1,070
1,330
742
1,340
1,310
785
6.55
6.93
4.18
9.36
5.26
6.18
7.11
824
803
981
761
839
802
853
1.78
1.90
1.24
2.10
1.66
1.42
2.34
852
819
1,150
832
836
806
916
0.997
1.03
0.531
1.13
0.815
1.12
0.795
0.823
0.816
0.872
0.744
0.893
0.890
0.741
1.24
1.26
1.08
1.38
1.19
1.34
1.07
0.848
0.835
0.931
0.760
0.937
0.898
0.784
Potential Exposure in OH Preschool Children (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Potential Exposure
-Aggregated
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
110
98
12
35
62
64
46
127
110
17
41
73
69
58
116
99
17
35
68
63
53
103
91
12
32
58
58
45
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
67.3
72.6
23.9
97.6
37.6
79.9
49.7
5,680
5,500
6,840
4,930
6,090
5,870
5,460
22.1
24.3
8.92
31.9
17.2
18.5
26.3
5,970
5,690
8,030
5,400
6,300
5,980
5,950
151
159
13.4
155
36.0
193
47.8
5,200
5,060
6,050
3,480
6,200
6,210
3,690
47.5
51.0
5.85
72.8
26.9
33.9
59.8
5,570
5,390
6,730
3,740
6,750
6,600
3,960
33.0
34.9
21.1
47.2
26.5
31.2
35.8
4,150
4,040
4,940
3,840
4,230
4,040
4,300
8.99
9.57
6.24
10.6
8.36
7.15
11.8
4,290
4,130
5,790
4,190
4,210
4,060
4,610
0.997
1.03
0.531
1.13
0.815
1.12
0.795
0.823
0.816
0.872
0.744
0.893
0.890
0.741
1.24
1.26
1.08
1.38
1.19
1.34
1.07
0.848
0.835
0.931
0.760
0.937
0.898
0.784
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                  M-104

-------
Table M-26b.   3.5.6-TCP (3.5.6-trichloro-2-pyridinol) (6515-38-4):  Range of Potential Exposure in
                OH Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Preschool Children (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Potential Exposure
- Aggregated
(ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
110
98
12
35
62
64
46
127
110
17
41
73
69
58
116
99
17
35
68
63
53
103
91
12
32
58
58
45
1.07
1.07
1.35
1.37
1.07
1.07
1.37
100
100
127
132
100
100
118
0.102
0.147
0.102
0.108
0.102
0.102
0.463
103
103
141
146
103
103
124
3.31
3.31
3.30
3.95
2.74
2.83
4.01
474
474
525
431
485
443
527
0.830
0.825
0.966
0.825
0.733
0.569
1.04
488
487
768
485
451
451
579
5.10
5.62
4.55
7.08
4.36
4.31
6.06
858
841
1,210
782
860
860
846
1.64
1.59
1.70
2.11
1.58
1.28
2.20
930
865
1,370
880
940
873
1,050
12.3
12.8
5.30
14.1
10.9
11.0
12.5
1,470
1,470
1,700
1,340
1,500
1,570
1,460
3.62
4.65
2.73
4.95
3.14
3.19
4.37
1,500
1,490
1,930
1,450
1,500
1,580
1,490
49.7
51.6
12.1
113
20.4
55.3
29.7
2,610
2,610
5,250
2,550
2,900
2,610
2,900
16.6
27.0
4.37
61.9
13.4
16.6
12.6
2,610
2,610
5,250
2,610
3,000
2,610
2,910
253
253
12.1
143
37.6
253
49.7
8,680
8,680
5,250
2,920
8,680
8,680
2,990
64.2
64.2
4.37
64.2
28.3
34.5
64.2
8,700
8,700
5,250
2,920
8,700
8,700
3,000
Potential Exposure in OH Preschool Children (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Potential Exposure
-Aggregated
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
110
98
12
35
62
64
46
127
110
17
41
73
69
58
116
99
17
35
68
63
53
103
91
12
32
58
58
45
5.38
5.38
6.81
6.89
5.38
5.38
6.89
506
506
639
667
506
506
593
0.514
0.740
0.514
0.543
0.514
0.514
2.33
517
517
708
733
517
517
625
16.7
16.7
16.6
19.9
13.8
14.3
20.2
2,390
2,390
2,650
2,170
2,440
2,230
2,650
4.18
4.16
4.87
4.16
3.70
2.87
5.26
2,460
2,450
3,870
2,450
2,270
2,270
2,920
25.7
28.3
22.9
35.7
21.9
21.7
30.6
4,320
4,240
6,120
3,940
4,330
4,330
4,260
8.24
8.02
8.59
10.6
7.98
6.43
11.1
4,690
4,360
6,920
4,440
4,740
4,400
5,310
62.1
64.3
26.7
71.2
55.0
55.5
62.9
7,430
7,390
8,570
6,770
7,550
7,930
7,350
18.2
23.4
13.8
25.0
15.8
16.1
22.0
7,570
7,510
9,710
7,310
7,570
7,950
7,510
251
260
60.9
570
103
278
150
13,100
13,100
26,400
12,800
14,600
13,100
14,600
83.7
136
22.0
312
67.3
83.7
63.3
13,200
13,200
26,500
13,200
15,100
13,200
14,700
1,280
1,280
60.9
721
190
1,280
251
43,700
43,700
26,400
14,700
43,700
43,700
15,100
323
323
22.0
323
143
174
323
43,800
43,800
26,500
14,700
43,800
43,800
15,100
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.
                                                M-105

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Table M-26c.   3.5.6-TCP (3.5.6-trichloro-2-pyridinol) (6515-38-4): Estimates of Potential Absorbed
                 Dose in OH Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Potential Absorbed
Dose - Aggregated
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
110
98
12
35
62
64
46
127
110
17
41
73
69
58
116
99
17
35
68
63
53
103
91
12
32
58
58
45
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.433
0.468
0.145
0.625
0.211
0.547
0.274
32.5
31.5
39.4
27.4
35.2
34.4
30.3
0.141
0.156
0.053
0.216
0.101
0.119
0.167
34.1
32.4
47.1
30.0
36.2
35.3
32.7
1.16
1.22
0.098
1.09
0.202
1.50
0.274
30.7
28.9
41.1
19.8
36.7
36.2
22.7
0.346
0.372
0.039
0.540
0.165
0.239
0.441
32.9
30.6
46.9
21.6
39.7
38.2
24.8
0.188
0.198
0.122
0.266
0.151
0.183
0.194
23.6
23.0
28.2
21.5
24.2
23.8
23.5
0.051
0.055
0.036
0.060
0.048
0.042
0.065
24.4
23.4
33.6
23.4
24.1
24.1
24.9
1.03
1.07
0.609
1.21
0.793
1.18
0.806
0.816
0.813
0.834
0.723
0.886
0.873
0.749
1.29
1.31
1.13
1.47
1.20
1.38
1.13
0.838
0.828
0.883
0.740
0.922
0.881
0.789
Potential Absorbed Dose in OH Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose - Aggregated
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
110
98
12
35
62
64
46
127
110
17
41
73
69
58
116
99
17
35
68
63
53
103
91
12
32
58
58
45
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
2.18
2.36
0.732
3.15
1.06
2.75
1.38
164
159
199
138
177
173
153
0.712
0.788
0.267
1.09
0.507
0.602
0.842
172
163
237
151
183
178
165
5.84
6.17
0.494
5.50
1.02
7.54
1.38
155
146
207
99.6
185
183
114
1.74
1.87
0.195
2.72
0.830
1.21
2.22
166
154
236
109
200
193
125
0.946
0.997
0.616
1.34
0.760
0.924
0.977
119
116
142
108
122
120
118
0.259
0.276
0.180
0.303
0.241
0.213
0.326
123
118
169
118
122
121
125
1.03
1.07
0.609
1.21
0.793
1.18
0.806
0.816
0.813
0.834
0.723
0.886
0.873
0.749
1.29
1.31
1.13
1.47
1.20
1.38
1.13
0.838
0.828
0.883
0.740
0.922
0.881
0.789
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                     M-106

-------
Table M-26d.   3.5.6-TCP (3.5.6-trichloro-2-pyridinol) (6515-38-4):  Range of Potential Absorbed
                 Dose in OH Preschool Children. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in OH Preschool Children (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Potential Absorbed
Dose - Aggregated
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
110
98
12
35
62
64
46
127
110
17
41
73
69
58
116
99
17
35
68
63
53
103
91
12
32
58
58
45
0.037
0.037
0.048
0.047
0.037
0.037
0.047
3.25
3.25
4.36
3.47
3.25
3.25
3.47
0.003
0.005
0.003
0.003
0.004
0.003
0.010
3.32
3.32
4.84
3.82
3.32
3.32
3.79
0.095
0.095
0.081
0.108
0.083
0.085
0.110
13.9
13.8
14.8
13.8
14.3
12.5
14.6
0.021
0.021
0.031
0.020
0.021
0.017
0.029
15.2
14.8
24.6
15.1
14.7
14.8
15.3
0.139
0.147
0.129
0.220
0.125
0.125
0.159
25.3
25.0
34.2
21.1
26.7
26.3
25.3
0.049
0.048
0.057
0.061
0.049
0.037
0.061
25.4
24.2
37.2
22.2
27.5
26.0
25.4
0.335
0.359
0.163
0.441
0.304
0.373
0.325
40.9
41.2
40.5
36.2
41.2
41.2
40.5
0.104
0.116
0.072
0.155
0.096
0.098
0.107
42.3
42.3
48.6
41.2
41.4
41.4
42.3
1.30
1.78
0.416
4.15
0.561
2.03
0.880
75.7
75.7
186
70.2
91.0
75.7
84.6
0.725
0.762
0.160
2.14
0.398
0.725
0.346
80.3
80.3
186
80.3
123
80.3
84.8
10.3
10.3
0.416
4.92
1.18
10.3
1.30
228
228
186
84.6
228
228
123
2.52
2.52
0.160
2.52
0.848
1.41
2.52
228
228
186
84.8
228
228
123
Potential Absorbed Dose in OH Preschool Children (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose - Aggregated
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
110
98
12
35
62
64
46
127
110
17
41
73
69
58
116
99
17
35
68
63
53
103
91
12
32
58
58
45
0.184
0.184
0.242
0.237
0.184
0.184
0.237
16.4
16.4
22.0
17.5
16.4
16.4
17.5
0.013
0.024
0.013
0.013
0.018
0.013
0.051
16.7
16.7
24.4
19.2
16.7
16.7
19.1
0.476
0.476
0.410
0.546
0.421
0.427
0.556
70.0
69.6
74.7
69.3
72.0
63.0
73.6
0.107
0.107
0.155
0.101
0.105
0.085
0.147
76.5
74.4
124
76.3
73.9
74.4
77.3
0.701
0.742
0.652
1.11
0.627
0.627
0.802
127
126
173
107
135
133
127
0.245
0.241
0.288
0.308
0.245
0.186
0.309
128
122
188
112
139
131
128
1.69
1.81
0.823
2.22
1.53
1.88
1.64
206
208
204
182
208
208
204
0.525
0.584
0.361
0.779
0.484
0.492
0.539
213
213
245
207
208
208
213
6.57
8.96
2.10
20.9
2.83
10.2
4.43
381
381
939
354
459
381
427
3.65
3.84
0.809
10.8
2.00
3.65
1.74
405
405
940
405
621
405
427
52.1
52.1
2.10
24.8
5.96
52.1
6.57
1,150
1,150
939
427
1,150
1,150
619
12.7
12.7
0.809
12.7
4.27
7.08
12.7
1,150
1,150
940
427
1,150
1,150
621
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. "Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor
into the body), divided by the subject's body weight.
                                                   M-107

-------

-------
                                   Appendix N
Descriptive Statistics of Potential Exposure Level and Potential Absorbed Dose Estimates
                   for Target Pollutants in Participating NC Adults
                                        N-l

-------
N-2

-------
This appendix contains tables of descriptive statistics of potential exposure and potential absorbed dose
estimates (expressed in both ng and pmole units) in NC adults for the following pollutants and
metabolites:
Pollutant/Metabolite
Benz[a]anthracene
Benzo[£>]fluoranthene
Benzo[/<]fluoranthene
Benzo[g/7/]perylene
Benzo[a]pyrene
Benzo[e]pyrene
Benzylbutylphthalate
Bisphenol-A
a/p/?a-Chlordane
gamma-Chlordane
Chlorpyrifos
Chrysene
Cyfluthrin
Diazinon
Dibenzo[a,/?]anthracene
Di-n-butylphthalate
p,p'-DDE
2,4-D (2,4-dichlorophenoxyacetic acid)
Heptachlor
lndeno[1 ,2,3-cd]pyrene
Pentachlorophenol
c/s-Permethrin
frans-Permethrin
PCS 52
PCB95
PCS 101
3,5,6-TCP (3,5,6-trichloro-2-pvridinol)
Table Numbers for
Potential Exposure
Summaries
Tables N-1 a, N-1b
Tables N-2a, N-2b
Tables N-3a, N-3b
Tables N-4a, N-4b
Tables N-5a, N-5b
Tables N-6a, N-6b
Tables N-7a, N-7b
Tables N-8a, N-8b
Tables N-9a, N-9b
Tables N-1 Oa, N-1 Ob
Tables N-1 1 a, N-11b
Tables N-12a, N-12b
Tables N-1 3a, N-13b
Tables N-14a, N-14b
Tables N-1 5a, N-15b
Tables N-16a, N-16b
Tables N-1 7a, N-17b
Tables N-1 8a, N-18b
Tables N-19a, N-19b
Tables N-20a, N-20b
Tables N-21 a, N-21b
Tables N-22a, N-22b
Tables N-23a, N-23b
Tables N-24a, N-24b
Tables N-25a, N-25b
Tables N-26a, N-26b
Tables N-27a, N-27b
Table Numbers for
Potential Absorbed
Dose Summaries
Tables N-1 a, N-1b
Tables N-2a, N-2b
Tables N-3a, N-3b
Tables N-4a, N-4b
Tables N-5a, N-5b
Tables N-6a, N-6b
Tables N-7a, N-7b
Tables N-8a, N-8b
Tables N-9a, N-9b
Tables N-10a, N-1 Ob
Tables N-1 1 a, N-11b
Tables N-12a, N-12b
Tables N-1 3a, N-13b
Tables N-14a, N-14b
Tables N-1 5a, N-15b
Tables N-16a, N-16b
Tables N-1 7a, N-17b
Tables N-18c, N-18d
Tables N-1 9a, N-19b
Tables N-20a, N-20b
Tables N-21 c, N-21d
Tables N-22a, N-22b
Tables N-23a, N-23b
Tables N-24a, N-24b
Tables N-25a, N-25b
Tables N-26a, N-26b
Tables N-27c, N-27d
Descriptive statistics are presented separately for the following groups of NC adult participants:
        All participants
        Participants from urban areas
        Participants from rural areas
        Participants from low-income areas
        Participants from middle/upper-income areas
        Caregivers of stay-at-home children
        Caregivers of day care children
                                                  N-3

-------
Table N-1a.    Benzralanthracene (56-55-3):  Estimates of Exposure and Absorbed Dose in NC
                 Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
117
96
21
52
61
62
55
64.3
67.6
47.6
66.7
61.5
69.2
59.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
2.06
2.18
-
2.20
1.88
2.68
1.41
8.37
6.40
17.4
5.37
11.4
5.96
11.1
3.50
3.70
-
2.69
4.07
4.67
1.17
22.0
11.4
45.5
11.7
28.2
11.3
29.6
1.30
1.36
-
1.49
1.15
1.48
1.13
3.24
3.19
3.48
2.43
4.32
3.13
3.37
0.796
0.815
-
0.791
0.762
0.924
0.608
1.14
1.05
1.50
1.05
1.17
0.993
1.29
Potential Exposure in NC Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
117
96
21
52
61
62
55
64.3
67.6
47.6
66.7
61.5
69.2
59.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
9.04
9.53
-
9.66
8.22
11.7
6.17
36.7
28.1
76.0
23.5
49.7
26.1
48.5
15.3
16.2
-
11.8
17.8
20.5
5.12
96.2
50.2
199
51.1
124
49.7
130
5.70
5.94
-
6.51
5.03
6.50
4.96
14.2
14.0
15.2
10.7
18.9
13.7
14.8
0.796
0.815
-
0.791
0.762
0.924
0.608
1.14
1.05
1.50
1.05
1.17
0.993
1.29
Potential Absorbed Dose in NC Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
117
96
21
52
61
62
55
64.3
67.6
47.6
66.7
61.5
69.2
59.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.015
0.016
-
0.015
0.014
0.020
0.009
0.055
0.043
0.108
0.034
0.075
0.045
0.066
0.028
0.029
-
0.022
0.033
0.038
0.008
0.132
0.080
0.259
0.077
0.166
0.090
0.167
0.009
0.009
-
0.009
0.008
0.011
0.007
0.022
0.022
0.023
0.015
0.031
0.022
0.021
0.850
0.866
-
0.876
0.813
0.976
0.635
1.14
1.04
1.54
1.04
1.15
1.02
1.27
Potential Absorbed Dose in NC Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
117
96
21
52
61
62
55
64.3
67.6
47.6
66.7
61.5
69.2
59.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.065
0.069
-
0.066
0.063
0.090
0.039
0.240
0.189
0.474
0.149
0.330
0.196
0.290
0.123
0.129
-
0.094
0.145
0.165
0.036
0.578
0.349
1.14
0.339
0.729
0.393
0.734
0.038
0.040
-
0.040
0.036
0.047
0.031
0.096
0.095
0.099
0.067
0.135
0.098
0.094
0.850
0.866
-
0.876
0.813
0.976
0.635
1.14
1.04
1.54
1.04
1.15
1.02
1.27
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      N-4

-------
Table N-1b.     Benzralanthracene (56-55-3): Range of Potential Exposure and Absorbed Dose in
                 NC Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
117
96
21
52
61
62
55

-------
Table N-2a.    Benzorfrlfluoranthene (205-99-2): Estimates of Exposure and Absorbed Dose in
                 NC Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
117
96
21
52
61
62
55
78.6
78.1
81.0
89.5
67.7
75.4
82.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
2.81
2.93
2.21
3.44
2.30
2.91
2.71
23.0
16.2
54.2
15.4
30.8
13.1
34.2
2.97
3.12
1.94
3.01
2.93
3.48
2.32
66.0
29.4
141
34.5
85.4
23.1
92.3
1.95
2.00
1.69
2.52
1.54
1.86
2.04
8.44
8.27
9.27
6.59
11.0
7.66
9.42
0.808
0.828
0.704
0.782
0.788
0.880
0.729
1.15
1.06
1.55
1.11
1.16
0.950
1.35
Potential Exposure in NC Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
117
96
21
52
61
62
55
78.6
78.1
81.0
89.5
67.7
75.4
82.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
11.1
11.6
8.74
13.6
9.10
11.5
10.7
91.3
64.3
215
61.1
122
52.1
136
11.8
12.4
7.70
11.9
11.6
13.8
9.18
262
116
560
137
338
91.5
366
7.72
7.93
6.71
9.97
6.12
7.39
8.08
33.5
32.8
36.7
26.1
43.5
30.4
37.3
0.808
0.828
0.704
0.782
0.788
0.880
0.729
1.15
1.06
1.55
1.11
1.16
0.950
1.35
Potential Absorbed Dose in NC Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
117
96
21
52
61
62
55
78.6
78.1
81.0
89.5
67.7
75.4
82.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.019
0.020
0.015
0.022
0.017
0.021
0.017
0.149
0.107
0.345
0.098
0.201
0.097
0.209
0.021
0.022
0.016
0.022
0.021
0.026
0.015
0.404
0.186
0.858
0.222
0.518
0.174
0.557
0.013
0.013
0.011
0.016
0.011
0.013
0.013
0.057
0.056
0.060
0.041
0.078
0.055
0.060
0.834
0.858
0.691
0.832
0.827
0.911
0.749
1.15
1.03
1.63
1.11
1.13
0.961
1.34
Potential Absorbed Dose in NC Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
117
96
21
52
61
62
55
78.6
78.1
81.0
89.5
67.7
75.4
82.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.076
0.080
0.059
0.088
0.066
0.084
0.068
0.592
0.422
1.37
0.387
0.797
0.384
0.826
0.084
0.087
0.065
0.086
0.084
0.102
0.059
1.60
0.736
3.40
0.878
2.05
0.690
2.21
0.052
0.053
0.044
0.062
0.044
0.053
0.050
0.226
0.223
0.240
0.164
0.309
0.217
0.237
0.834
0.858
0.691
0.832
0.827
0.911
0.749
1.15
1.03
1.63
1.11
1.13
0.961
1.34
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      N-6

-------
Table N-2b.     Benzorfrlfluoranthene (205-99-2):  Range of Potential Exposure and Absorbed
                 Dose in NC Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
117
96
21
52
61
62
55

-------
Table N-3a.    Benzorftlfluoranthene (207-08-9):  Estimates of Exposure and Absorbed Dose in
                 NC Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
117
96
21
52
61
62
55
60.3
60.0
61.9
66.7
52.3
60.0
60.7
100.0
100.0
100.0
100.0
100.0
100.0
100.0
1.16
1.18
1.04
1.38
0.953
1.22
1.09
7.96
5.72
18.2
5.27
10.7
4.98
11.3
0.953
1.01
0.637
1.23
0.596
1.16
0.668
22.6
10.5
48.0
12.0
29.2
9.08
31.4
0.984
0.992
0.943
1.13
0.858
1.00
0.967
2.94
2.85
3.39
2.23
3.85
2.78
3.12
0.490
0.506
0.408
0.549
0.403
0.535
0.439
1.14
1.06
1.49
1.10
1.15
0.965
1.32
Potential Exposure in NC Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
117
96
21
52
61
62
55
60.3
60.0
61.9
66.7
52.3
60.0
60.7
100.0
100.0
100.0
100.0
100.0
100.0
100.0
4.58
4.67
4.13
5.46
3.78
4.84
4.30
31.6
22.7
72.3
20.9
42.3
19.7
44.9
3.78
3.98
2.52
4.88
2.36
4.60
2.65
89.6
41.8
190
47.6
116
36.0
124
3.90
3.93
3.74
4.49
3.40
3.96
3.83
11.6
11.3
13.4
8.85
15.3
11.0
12.4
0.490
0.506
0.408
0.549
0.403
0.535
0.439
1.14
1.06
1.49
1.10
1.15
0.965
1.32
Potential Absorbed Dose in NC Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
117
96
21
52
61
62
55
60.3
60.0
61.9
66.7
52.3
60.0
60.7
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.008
0.008
0.007
0.009
0.007
0.009
0.007
0.052
0.038
0.114
0.033
0.070
0.037
0.068
0.006
0.006
0.006
0.008
0.004
0.008
0.004
0.135
0.069
0.280
0.077
0.172
0.071
0.182
0.007
0.007
0.006
0.007
0.006
0.007
0.006
0.020
0.019
0.022
0.014
0.027
0.020
0.020
0.509
0.520
0.458
0.581
0.438
0.553
0.446
1.14
1.04
1.54
1.09
1.13
0.979
1.31
Potential Absorbed Dose in NC Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
117
96
21
52
61
62
55
60.3
60.0
61.9
66.7
52.3
60.0
60.7
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.031
0.031
0.028
0.034
0.027
0.035
0.027
0.205
0.151
0.452
0.131
0.277
0.147
0.270
0.024
0.025
0.023
0.031
0.016
0.030
0.015
0.537
0.275
1.11
0.307
0.682
0.280
0.722
0.026
0.026
0.024
0.028
0.024
0.028
0.024
0.078
0.077
0.088
0.055
0.109
0.078
0.078
0.509
0.520
0.458
0.581
0.438
0.553
0.446
1.14
1.04
1.54
1.09
1.13
0.979
1.31
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.

-------
Table N-3b.     Benzorftlfluoranthene (207-08-9):  Range of Potential Exposure and Absorbed Dose
                 in NC Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
117
96
21
52
61
62
55

-------
Table N-4a.    Benzorq/i/lperylene (191-24-2):  Estimates of Exposure and Absorbed Dose in NC
                 Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
117
96
21
52
61
62
55
73.0
74.3
66.7
87.7
58.5
73.8
72.1
100.0
100.0
100.0
100.0
100.0
100.0
100.0
2.48
2.57
1.99
2.80
2.21
2.71
2.22
11.7
8.42
26.7
7.75
15.6
7.39
16.6
2.68
2.82
1.80
2.37
2.98
3.33
1.74
32.5
14.2
70.0
17.0
42.0
11.5
45.6
1.74
1.79
1.52
2.13
1.45
1.71
1.78
4.73
4.71
4.79
3.55
6.21
4.63
4.83
0.768
0.782
0.692
0.728
0.777
0.879
0.635
1.08
0.970
1.50
1.04
1.07
0.883
1.27
Potential Exposure in NC Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
117
96
21
52
61
62
55
73.0
74.3
66.7
87.7
58.5
73.8
72.1
100.0
100.0
100.0
100.0
100.0
100.0
100.0
8.96
9.31
7.19
10.1
7.98
9.81
8.05
42.4
30.5
96.6
28.1
56.5
26.7
60.0
9.71
10.2
6.53
8.56
10.8
12.1
6.28
118
51.3
253
61.3
152
41.8
165
6.31
6.48
5.51
7.70
5.26
6.17
6.45
17.1
17.0
17.3
12.8
22.5
16.8
17.5
0.768
0.782
0.692
0.728
0.777
0.879
0.635
1.08
0.970
1.50
1.04
1.07
0.883
1.27
Potential Absorbed Dose in NC Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
117
96
21
52
61
62
55
73.0
74.3
66.7
87.7
58.5
73.8
72.1
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.017
0.018
0.013
0.017
0.016
0.020
0.014
0.077
0.056
0.170
0.049
0.103
0.054
0.101
0.020
0.021
0.015
0.015
0.024
0.026
0.009
0.203
0.092
0.433
0.109
0.261
0.088
0.280
0.012
0.012
0.010
0.013
0.010
0.012
0.011
0.032
0.032
0.031
0.022
0.044
0.033
0.031
0.773
0.790
0.675
0.730
0.811
0.899
0.614
1.08
0.960
1.55
1.04
1.05
0.906
1.26
Potential Absorbed Dose in NC Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
117
96
21
52
61
62
55
73.0
74.3
66.7
87.7
58.5
73.8
72.1
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.061
0.063
0.048
0.063
0.059
0.072
0.049
0.277
0.203
0.614
0.178
0.374
0.197
0.367
0.073
0.076
0.053
0.056
0.087
0.094
0.034
0.734
0.332
1.57
0.395
0.943
0.317
1.01
0.042
0.044
0.036
0.048
0.037
0.044
0.040
0.115
0.116
0.113
0.080
0.160
0.120
0.111
0.773
0.790
0.675
0.730
0.811
0.899
0.614
1.08
0.960
1.55
1.04
1.05
0.906
1.26
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      N-10

-------
Table N-4b.     Benzorq/i/lperylene (191-24-2): Range of Potential Exposure and Absorbed Dose
                 in NC Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
117
96
21
52
61
62
55

-------
Table N-5a.    BenzoMpyrene (50-32-8): Estimates of Exposure and Absorbed Dose in NC
                 Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
117
96
21
52
61
62
55
65.9
66.7
61.9
77.2
53.8
63.1
68.9
100.0
100.0
100.0
100.0
100.0
100.0
100.0
2.08
2.04
2.26
2.65
1.55
2.15
2.00
12.4
8.78
28.9
7.63
17.1
7.61
17.8
2.34
2.19
3.03
2.61
2.01
2.68
1.92
35.5
14.8
77.0
16.4
46.5
12.1
49.8
1.44
1.44
1.43
1.88
1.11
1.40
1.47
4.72
4.77
4.49
3.50
6.32
4.56
4.90
0.777
0.764
0.859
0.797
0.676
0.827
0.727
1.12
0.993
1.60
1.04
1.15
0.929
1.31
Potential Exposure in NC Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
117
96
21
52
61
62
55
65.9
66.7
61.9
77.2
53.8
63.1
68.9
100.0
100.0
100.0
100.0
100.0
100.0
100.0
8.23
8.09
8.94
10.5
6.14
8.53
7.91
49.1
34.8
114
30.2
67.7
30.1
70.5
9.27
8.69
12.0
10.3
7.95
10.6
7.62
141
58.5
305
65.0
184
48.0
198
5.69
5.70
5.69
7.45
4.40
5.56
5.84
18.7
18.9
17.8
13.9
25.0
18.1
19.4
0.777
0.764
0.859
0.797
0.676
0.827
0.727
1.12
0.993
1.60
1.04
1.15
0.929
1.31
Potential Absorbed Dose in NC Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
117
96
21
52
61
62
55
65.9
66.7
61.9
77.2
53.8
63.1
68.9
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.014
0.013
0.016
0.017
0.011
0.015
0.012
0.081
0.059
0.181
0.049
0.113
0.057
0.108
0.016
0.013
0.026
0.019
0.012
0.020
0.011
0.216
0.097
0.463
0.105
0.281
0.094
0.299
0.010
0.010
0.009
0.012
0.008
0.010
0.009
0.032
0.032
0.029
0.022
0.045
0.033
0.031
0.772
0.755
0.869
0.810
0.692
0.829
0.709
1.14
1.00
1.65
1.06
1.13
0.977
1.30
Potential Absorbed Dose in NC Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
117
96
21
52
61
62
55
65.9
66.7
61.9
77.2
53.8
63.1
68.9
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.055
0.053
0.063
0.067
0.043
0.061
0.048
0.321
0.234
0.718
0.193
0.446
0.226
0.428
0.064
0.053
0.105
0.077
0.049
0.077
0.045
0.858
0.384
1.83
0.417
1.11
0.374
1.18
0.038
0.038
0.037
0.046
0.031
0.040
0.036
0.126
0.129
0.116
0.087
0.178
0.129
0.123
0.772
0.755
0.869
0.810
0.692
0.829
0.709
1.14
1.00
1.65
1.06
1.13
0.977
1.30
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      N-12

-------
Table N-5b.    BenzoMpyrene (50-32-8):  Range of Potential Exposure and Absorbed Dose in NC
                 Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
117
96
21
52
61
62
55

-------
Table N-6a.    Benzorelpyrene (192-97-2):  Estimates of Exposure and Absorbed Dose in NC
                 Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
117
96
21
52
61
62
55
66.7
66.7
66.7
78.9
53.8
66.2
67.2
100.0
100.0
100.0
100.0
100.0
100.0
100.0
1.43
1.44
1.39
1.77
1.13
1.45
1.41
12.2
8.54
29.1
7.89
16.5
7.43
17.7
1.14
1.12
1.26
1.33
0.868
1.22
1.05
35.3
14.7
76.5
17.0
46.1
12.3
49.5
1.16
1.17
1.12
1.43
0.962
1.16
1.17
4.69
4.61
5.09
3.65
6.03
4.47
4.95
0.593
0.596
0.591
0.624
0.506
0.612
0.576
1.10
0.999
1.50
1.04
1.12
0.905
1.29
Potential Exposure in NC Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
117
96
21
52
61
62
55
66.7
66.7
66.7
78.9
53.8
66.2
67.2
100.0
100.0
100.0
100.0
100.0
100.0
100.0
5.67
5.71
5.50
7.00
4.49
5.75
5.59
48.5
33.9
115
31.3
65.6
29.4
70.0
4.51
4.43
4.99
5.28
3.44
4.84
4.16
140
58.1
303
67.4
183
48.9
196
4.61
4.65
4.45
5.66
3.81
4.60
4.63
18.6
18.3
20.2
14.5
23.9
17.7
19.6
0.593
0.596
0.591
0.624
0.506
0.612
0.576
1.10
0.999
1.50
1.04
1.12
0.905
1.29
Potential Absorbed Dose in NC Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
117
96
21
52
61
62
55
66.7
66.7
66.7
78.9
53.8
66.2
67.2
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.010
0.010
0.010
0.011
0.008
0.010
0.009
0.080
0.057
0.185
0.050
0.109
0.055
0.108
0.008
0.007
0.011
0.010
0.006
0.009
0.006
0.219
0.096
0.470
0.110
0.284
0.095
0.303
0.008
0.008
0.007
0.009
0.007
0.008
0.007
0.032
0.031
0.033
0.023
0.043
0.032
0.031
0.594
0.594
0.607
0.635
0.537
0.615
0.569
1.10
0.982
1.55
1.03
1.10
0.922
1.28
Potential Absorbed Dose in NC Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
117
96
21
52
61
62
55
66.7
66.7
66.7
78.9
53.8
66.2
67.2
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.038
0.038
0.038
0.044
0.032
0.041
0.035
0.316
0.225
0.733
0.197
0.432
0.218
0.427
0.031
0.028
0.045
0.038
0.023
0.035
0.025
0.869
0.379
1.86
0.435
1.13
0.376
1.20
0.031
0.031
0.029
0.035
0.027
0.033
0.029
0.125
0.124
0.132
0.091
0.170
0.126
0.124
0.594
0.594
0.607
0.635
0.537
0.615
0.569
1.10
0.982
1.55
1.03
1.10
0.922
1.28
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      N-14

-------
Table N-6b.     Benzorelpyrene (192-97-2): Range of Potential Exposure and Absorbed Dose in
                 NC Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
117
96
21
52
61
62
55

-------
Table N-7a.    Benzylbutylphthalate (85-68-7): Estimates of Exposure and Absorbed Dose in NC
                 Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
117
96
21
50
63
63
54
38.9
41.0
28.6
50.9
29.2
36.9
41.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
2,580
-
-
-
922
880
1,120
1,300
661
861
993
-
-
-
1 1 ,200
-
-
-
1,200
1,180
1,330
1,580
720
1,080
1,330
-
-
-
879
-
-
-
498
467
669
651
424
465
539
-
-
-
0.931
-
-
-
1.09
1.11
0.970
1.25
0.922
1.10
1.09
Potential Exposure in NC Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
117
96
21
50
63
63
54
38.9
41.0
28.6
50.9
29.2
36.9
41.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
8,250
-
-
-
2,950
2,820
3,570
4,180
2,120
2,760
3,180
-
-
-
35,800
-
-
-
3,850
3,770
4,250
5,050
2,300
3,470
4,270
-
-
-
2,820
-
-
-
1,590
1,490
2,140
2,080
1,360
1,490
1,730
-
-
-
0.931
-
-
-
1.09
1.11
0.970
1.25
0.922
1.10
1.09
Potential Absorbed Dose in NC Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
117
96
21
50
63
63
54
38.9
41.0
28.6
50.9
29.2
36.9
41.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
16.7
-
-
-
6.08
5.85
7.11
7.84
4.93
6.03
6.14
-
-
-
67.6
-
-
-
8.05
7.96
8.57
9.87
6.26
7.46
8.75
-
-
-
5.45
-
-
-
3.36
3.17
4.36
4.03
3.04
3.31
3.42
-
-
-
1.04
-
-
-
1.07
1.09
0.935
1.22
0.936
1.09
1.04
Potential Absorbed Dose in NC Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
117
96
21
50
63
63
54
38.9
41.0
28.6
50.9
29.2
36.9
41.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
53.5
-
-
-
19.5
18.7
22.7
25.1
15.8
19.3
19.6
-
-
-
216
-
-
-
25.8
25.5
27.4
31.6
20.0
23.9
28.0
-
-
-
17.4
-
-
-
10.8
10.2
14.0
12.9
9.73
10.6
10.9
-
-
-
1.04
-
-
-
1.07
1.09
0.935
1.22
0.936
1.09
1.04
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      N-16

-------
Table N-7b.     Benzylbutylphthalate (85-68-7):  Range of Potential Exposure and Absorbed Dose
                 in NC Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
117
96
21
50
63
63
54

-------
Table N-8a.    Bisphenol-A (80-05-7):  Estimates of Exposure and Absorbed Dose in NC Adults.
                 Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
116
96
20
50
62
63
53
76.2
75.2
81.0
82.5
72.3
81.5
70.5
28.4
27.1
35.0
34.0
25.8
22.2
35.8
48.9
51.7
35.1
37.8
58.2
68.7
27.8
-
-
-
-
-
-
-
192
210
37.2
56.0
263
265
30.9
-
-
-
-
-
-
-
22.6
22.3
23.7
25.2
20.2
24.1
21.0
-
-
-
-
-
-
-
0.881
0.890
0.851
0.780
0.925
1.05
0.661
-
-
-
-
-
-
-
Potential Exposure in NC Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
116
96
20
50
62
63
53
76.2
75.2
81.0
82.5
72.3
81.5
70.5
28.4
27.1
35.0
34.0
25.8
22.2
35.8
214
226
154
166
255
301
122
-
-
-
-
-
-
-
842
919
163
245
1,150
1,160
135
-
-
-
-
-
-
-
98.9
97.9
104
110
88.5
106
92.1
-
-
-
-
-
-
-
0.881
0.890
0.851
0.780
0.925
1.05
0.661
-
-
-
-
-
-
-
Potential Absorbed Dose in NC Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
116
96
20
50
62
63
53
76.2
75.2
81.0
82.5
72.3
81.5
70.5
28.4
27.1
35.0
34.0
25.8
22.2
35.8
0.358
0.380
0.252
0.254
0.445
0.524
0.182
-
-
-
-
-
-
-
1.52
1.66
0.292
0.403
2.08
2.09
0.276
-
-
-
-
-
-
-
0.151
0.151
0.155
0.156
0.144
0.173
0.131
-
-
-
-
-
-
-
0.926
0.925
0.951
0.862
0.957
1.10
0.668
-
-
-
-
-
-
-
Potential Absorbed Dose in NC Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
116
96
20
50
62
63
53
76.2
75.2
81.0
82.5
72.3
81.5
70.5
28.4
27.1
35.0
34.0
25.8
22.2
35.8
1.57
1.66
1.10
1.11
1.95
2.29
0.798
-
-
-
-
-
-
-
6.66
7.27
1.28
1.77
9.12
9.17
1.21
-
-
-
-
-
-
-
0.663
0.660
0.677
0.683
0.630
0.757
0.575
-
-
-
-
-
-
-
0.926
0.925
0.951
0.862
0.957
1.10
0.668
-
-
-
-
-
-
-
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      N-18

-------
Table N-8b.    Bisphenol-A (80-05-7): Range of Potential Exposure and Absorbed Dose in NC
                 Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
116
96
20
50
62
63
53

-------
Table N-9a.    a/p/ia-Chlordane (5103-71-9):  Estimates of Exposure and Absorbed Dose in NC
                 Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
121
100
21
52
65
66
55
98.4
98.1
100.0
100.0
98.5
96.9
100.0
96.7
97.0
95.2
100.0
93.8
93.9
100.0
37.2
35.5
45.8
36.3
31.4
41.1
33.0
2.33
2.50
1.48
2.02
2.48
2.07
2.64
77.5
77.4
79.0
65.1
60.5
89.4
62.8
6.41
6.95
2.53
6.19
6.65
3.33
8.82
13.7
13.3
15.8
15.9
12.1
12.7
14.9
0.661
0.669
0.623
0.516
0.781
0.773
0.548
1.27
1.25
1.40
1.14
1.30
1.45
1.06
1.43
1.47
1.26
1.46
1.38
1.43
1.42
Potential Exposure in NC Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
121
100
21
52
65
66
55
98.4
98.1
100.0
100.0
98.5
96.9
100.0
96.7
97.0
95.2
100.0
93.8
93.9
100.0
90.8
86.6
112
88.6
76.7
100
80.6
5.68
6.11
3.61
4.93
6.06
5.04
6.44
189
189
193
159
148
218
153
15.6
17.0
6.17
15.1
16.2
8.13
21.5
33.4
32.5
38.6
38.8
29.5
31.0
36.3
1.61
1.63
1.52
1.26
1.91
1.89
1.34
1.27
1.25
1.40
1.14
1.30
1.45
1.06
1.43
1.47
1.26
1.46
1.38
1.43
1.42
Potential Absorbed Dose in NC Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
121
100
21
52
65
66
55
98.4
98.1
100.0
100.0
98.5
96.9
100.0
96.7
97.0
95.2
100.0
93.8
93.9
100.0
0.238
0.232
0.267
0.218
0.208
0.278
0.195
0.015
0.016
0.009
0.011
0.017
0.015
0.015
0.493
0.506
0.433
0.380
0.363
0.593
0.358
0.039
0.043
0.014
0.029
0.046
0.026
0.051
0.092
0.090
0.103
0.098
0.086
0.091
0.093
0.004
0.005
0.004
0.003
0.006
0.006
0.003
1.23
1.22
1.31
1.12
1.26
1.41
1.03
1.42
1.46
1.22
1.42
1.38
1.41
1.40
Potential Absorbed Dose in NC Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
121
100
21
52
65
66
55
98.4
98.1
100.0
100.0
98.5
96.9
100.0
96.7
97.0
95.2
100.0
93.8
93.9
100.0
0.580
0.566
0.650
0.531
0.507
0.679
0.475
0.037
0.040
0.022
0.027
0.043
0.036
0.038
1.20
1.23
1.06
0.928
0.886
1.45
0.873
0.096
0.104
0.034
0.071
0.112
0.063
0.125
0.224
0.219
0.252
0.240
0.210
0.222
0.226
0.011
0.011
0.010
0.008
0.014
0.013
0.008
1.23
1.22
1.31
1.12
1.26
1.41
1.03
1.42
1.46
1.22
1.42
1.38
1.41
1.40
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      N-20

-------
Table N-9b.     a/p/ia-Chlordane (5103-71-9):  Range of Potential Exposure and Absorbed Dose in
                 NC Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
121
100
21
52
65
66
55

-------
Table INMOa.   qa/n/na-Chlordane (5103-74-2):  Estimates of Exposure and Absorbed Dose in NC
                 Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
120
99
21
51
65
65
55
100.0
100.0
100.0
100.0
100.0
100.0
100.0
98.3
99.0
95.2
100.0
96.9
96.9
100.0
66.1
62.3
85.3
69.8
52.1
74.5
57.2
3.16
3.28
2.61
2.94
3.18
3.08
3.25
128
123
150
118
84.6
151
96.7
6.91
7.24
5.19
6.94
6.79
4.53
8.99
24.2
23.6
27.4
28.5
21.0
22.4
26.2
0.958
0.969
0.909
0.750
1.13
1.12
0.793
1.32
1.30
1.44
1.23
1.32
1.51
1.09
1.46
1.49
1.34
1.52
1.39
1.47
1.44
Potential Exposure in NC Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
120
99
21
51
65
65
55
100.0
100.0
100.0
100.0
100.0
100.0
100.0
98.3
99.0
95.2
100.0
96.9
96.9
100.0
161
152
208
170
127
182
140
7.71
7.99
6.37
7.17
7.76
7.51
7.94
311
300
367
288
206
369
236
16.9
17.7
12.7
16.9
16.6
11.1
21.9
59.0
57.5
66.8
69.7
51.2
54.6
64.0
2.34
2.36
2.22
1.83
2.75
2.74
1.93
1.32
1.30
1.44
1.23
1.32
1.51
1.09
1.46
1.49
1.34
1.52
1.39
1.47
1.44
Potential Absorbed Dose in NC Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
120
99
21
51
65
65
55
100.0
100.0
100.0
100.0
100.0
100.0
100.0
98.3
99.0
95.2
100.0
96.9
96.9
100.0
0.426
0.411
0.498
0.425
0.349
0.498
0.349
0.020
0.021
0.015
0.016
0.022
0.021
0.019
0.837
0.840
0.837
0.746
0.519
0.998
0.622
0.042
0.045
0.028
0.034
0.046
0.032
0.052
0.162
0.159
0.179
0.177
0.149
0.160
0.164
0.006
0.007
0.006
0.005
0.008
0.008
0.005
1.28
1.27
1.36
1.21
1.28
1.46
1.07
1.44
1.48
1.28
1.46
1.38
1.43
1.42
Potential Absorbed Dose in NC Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
120
99
21
51
65
65
55
100.0
100.0
100.0
100.0
100.0
100.0
100.0
98.3
99.0
95.2
100.0
96.9
96.9
100.0
1.04
1.00
1.22
1.04
0.852
1.21
0.853
0.049
0.052
0.037
0.039
0.054
0.051
0.047
2.04
2.05
2.04
1.82
1.27
2.43
1.52
0.103
0.109
0.069
0.083
0.113
0.078
0.127
0.395
0.388
0.436
0.432
0.364
0.391
0.399
0.016
0.016
0.014
0.011
0.020
0.020
0.012
1.28
1.27
1.36
1.21
1.28
1.46
1.07
1.44
1.48
1.28
1.46
1.38
1.43
1.42
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      N-22

-------
Table INMOb.   qa/n/na-Chlordane (5103-74-2): Range of Potential Exposure and Absorbed Dose in
                 NC Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
120
99
21
51
65
65
55
1.64
1.64
5.47
4.22
1.64
1.64
7.74

-------
Table N-11a.   Chlorpyrifos (2921-88-2): Estimates of Exposure and Absorbed Dose in NC Adults.
                 Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
120
100
20
51
65
65
55
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
165
166
162
184
152
152
179
9.51
6.81
23.0
13.1
6.78
6.93
12.6
286
301
202
314
270
257
316
32.2
11.1
74.9
48.2
9.35
11.7
45.8
82.6
82.0
85.2
94.8
72.6
68.6
101
3.25
3.15
3.82
2.95
3.39
3.04
3.52
1.11
1.09
1.23
1.13
1.10
1.23
0.933
1.29
1.20
1.70
1.44
1.19
1.25
1.35
Potential Exposure in NC Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
120
100
20
51
65
65
55
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
472
474
461
524
434
434
512
27.1
19.4
65.7
37.4
19.3
19.8
35.8
816
858
577
894
770
732
901
91.8
31.7
214
138
26.7
33.5
131
235
234
243
270
207
196
287
9.28
8.99
10.9
8.41
9.68
8.68
10.0
1.11
1.09
1.23
1.13
1.10
1.23
0.933
1.29
1.20
1.70
1.44
1.19
1.25
1.35
Potential Absorbed Dose in NC Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
120
100
20
51
65
65
55
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
1.13
1.16
0.961
1.23
1.05
1.02
1.24
0.060
0.047
0.129
0.077
0.048
0.047
0.076
2.13
2.29
1.03
2.61
1.69
1.53
2.63
0.174
0.069
0.400
0.259
0.060
0.067
0.247
0.553
0.553
0.556
0.587
0.517
0.491
0.628
0.022
0.021
0.025
0.018
0.024
0.022
0.022
1.10
1.09
1.19
1.13
1.10
1.21
0.971
1.31
1.24
1.66
1.44
1.21
1.25
1.39
Potential Absorbed Dose in NC Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
120
100
20
51
65
65
55
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
3.21
3.31
2.74
3.50
3.00
2.92
3.53
0.172
0.133
0.368
0.218
0.136
0.134
0.218
6.08
6.53
2.93
7.46
4.81
4.37
7.51
0.498
0.198
1.14
0.739
0.170
0.192
0.706
1.58
1.58
1.59
1.67
1.47
1.40
1.79
0.063
0.061
0.071
0.053
0.069
0.062
0.064
1.10
1.09
1.19
1.13
1.10
1.21
0.971
1.31
1.24
1.66
1.44
1.21
1.25
1.39
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      N-24

-------
Table N-11b.   Chlorpyrifos (2921-88-2):  Range of Potential Exposure and Absorbed Dose in NC
                 Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
120
100
20
51
65
65
55
3.50
5.62
3.50
3.50
5.62
3.50
28.4
0.279
0.279
0.307
0.307
0.279
0.307
0.279
35.9
38.7
35.7
49.8
35.7
29.8
52.7
1.16
1.25
0.937
0.920
1.45
1.07
1.37
69.1
66.8
89.5
91.9
57.5
57.8
78.7
3.19
3.19
3.59
2.74
3.65
2.57
3.47
164
159
166
167
139
154
166
6.51
6.21
10.4
6.47
6.55
6.43
7.58
572
541
674
674
572
572
487
29.5
29.5
182
34.8
28.8
24.2
34.8
2,180
2,180
711
2,180
1,690
1,690
2,180
340
75.6
340
340
43.2
75.6
340
Potential Exposure in NC Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
120
100
20
51
65
65
55
9.99
16.0
9.99
9.99
16.0
9.99
80.9
0.795
0.795
0.877
0.877
0.795
0.877
0.795
102
110
102
142
102
85.0
150
3.30
3.55
2.67
2.62
4.13
3.06
3.91
197
191
255
262
164
165
224
9.10
9.10
10.2
7.81
10.4
7.32
9.88
467
453
473
476
397
440
473
18.6
17.7
29.6
18.5
18.7
18.3
21.6
1,630
1,540
1,920
1,920
1,630
1,630
1,390
84.2
84.2
520
99.2
82.1
69.0
99.2
6,220
6,220
2,030
6,220
4,830
4,830
6,220
969
216
969
969
123
216
969
Potential Absorbed Dose in NC Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
120
100
20
51
65
65
55
0.019
0.050
0.019
0.019
0.050
0.019
0.179
0.002
0.002
0.002
0.002
0.002
0.002
0.002
0.270
0.283
0.263
0.323
0.260
0.247
0.327
0.009
0.009
0.007
0.007
0.011
0.009
0.010
0.453
0.436
0.624
0.495
0.387
0.429
0.478
0.021
0.019
0.027
0.016
0.027
0.019
0.021
1.08
1.03
1.14
1.01
1.08
1.01
1.13
0.051
0.047
0.071
0.038
0.054
0.054
0.049
3.80
4.70
3.24
3.80
4.70
3.80
3.33
0.199
0.199
0.992
0.304
0.188
0.176
0.262
19.1
19.1
3.80
19.1
9.10
9.10
19.1
1.82
0.385
1.82
1.82
0.262
0.385
1.82
Potential Absorbed Dose in NC Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
120
100
20
51
65
65
55
0.056
0.142
0.056
0.056
0.142
0.056
0.510
0.005
0.005
0.007
0.005
0.006
0.007
0.005
0.770
0.807
0.750
0.922
0.743
0.703
0.931
0.025
0.026
0.020
0.021
0.032
0.025
0.029
1.29
1.24
1.78
1.41
1.10
1.22
1.36
0.059
0.054
0.078
0.047
0.078
0.055
0.060
3.08
2.94
3.25
2.88
3.08
2.88
3.21
0.146
0.135
0.204
0.108
0.155
0.155
0.139
10.9
13.4
9.23
10.9
13.4
10.9
9.49
0.567
0.567
2.83
0.867
0.537
0.503
0.747
54.3
54.3
10.9
54.3
25.9
25.9
54.3
5.18
1.10
5.18
5.18
0.747
1.10
5.18
a  Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries."Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into
the body), divided by the subject's body weight.
                                                    N-25

-------
Table N-12a.   Chrysene (218-01-9):  Estimates of Exposure and Absorbed Dose in NC Adults.
                 Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
117
96
21
52
61
62
55
81.0
82.9
71.4
89.5
72.3
80.0
82.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
2.26
2.28
2.16
2.82
1.75
2.65
1.84
13.3
8.99
32.9
8.40
18.1
7.94
19.3
2.82
2.71
3.39
3.00
2.61
3.62
1.50
40.4
16.5
87.6
19.1
52.8
14.6
56.5
1.57
1.60
1.41
1.98
1.27
1.64
1.49
4.56
4.47
4.99
3.61
5.79
4.20
5.01
0.750
0.749
0.762
0.784
0.650
0.875
0.591
1.18
1.07
1.62
1.09
1.23
1.03
1.33
Potential Exposure in NC Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
117
96
21
52
61
62
55
81.0
82.9
71.4
89.5
72.3
80.0
82.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
9.89
9.98
9.46
12.4
7.67
11.6
8.05
58.2
39.4
144
36.8
79.5
34.8
84.6
12.4
11.9
14.9
13.1
11.4
15.9
6.55
177
72.3
384
83.8
231
64.1
247
6.88
7.02
6.19
8.68
5.58
7.20
6.55
20.0
19.6
21.9
15.8
25.4
18.4
21.9
0.750
0.749
0.762
0.784
0.650
0.875
0.591
1.18
1.07
1.62
1.09
1.23
1.03
1.33
Potential Absorbed Dose in NC Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
117
96
21
52
61
62
55
81.0
82.9
71.4
89.5
72.3
80.0
82.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.016
0.016
0.016
0.019
0.013
0.020
0.012
0.086
0.060
0.208
0.053
0.119
0.059
0.117
0.023
0.021
0.031
0.024
0.021
0.030
0.009
0.246
0.109
0.526
0.123
0.319
0.113
0.338
0.011
0.011
0.009
0.012
0.009
0.012
0.009
0.031
0.030
0.033
0.023
0.041
0.030
0.032
0.795
0.793
0.810
0.867
0.699
0.926
0.611
1.18
1.05
1.68
1.09
1.21
1.05
1.32
Potential Absorbed Dose in NC Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
117
96
21
52
61
62
55
81.0
82.9
71.4
89.5
72.3
80.0
82.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.070
0.070
0.069
0.084
0.057
0.088
0.051
0.377
0.261
0.910
0.231
0.520
0.258
0.512
0.099
0.092
0.134
0.107
0.093
0.130
0.041
1.08
0.477
2.30
0.540
1.40
0.496
1.48
0.046
0.047
0.040
0.054
0.040
0.052
0.041
0.135
0.133
0.143
0.099
0.181
0.131
0.139
0.795
0.793
0.810
0.867
0.699
0.926
0.611
1.18
1.05
1.68
1.09
1.21
1.05
1.32
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      N-26

-------
Table N-12b.   Chrysene (218-01-9): Range of Potential Exposure and Absorbed Dose in NC
                 Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
117
96
21
52
61
62
55

-------
Table N-13a.   Cyfluthrin (68359-37-5):  Estimates of Exposure and Absorbed Dose in NC Adults.
                 Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
121
100
21
52
65
66
55
4.0
3.8
4.8
7.0
1.5
0.0
8.2
52.9
52.0
57.1
53.8
52.3
56.1
49.1
-
-
-
-
-
-
-
7.40
6.87
9.92
4.72
9.80
6.71
-
-
-
-
-
-
-
-
14.8
14.4
17.1
10.1
17.8
11.1
-
-
-
-
-
-
-
-
1.89
1.85
2.12
1.21
2.67
2.22
-
-
-
-
-
-
-
-
1.63
1.57
1.94
1.56
1.65
1.55
-
Potential Exposure in NC Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
121
100
21
52
65
66
55
4.0
3.8
4.8
7.0
1.5
0.0
8.2
52.9
52.0
57.1
53.8
52.3
56.1
49.1
-
-
-
-
-
-
-
17.0
15.8
22.8
10.9
22.6
15.4
-
-
-
-
-
-
-
-
34.2
33.1
39.3
23.3
41.1
25.6
-
-
-
-
-
-
-
-
4.35
4.25
4.87
2.78
6.14
5.11
-
-
-
-
-
-
-
-
1.63
1.57
1.94
1.56
1.65
1.55
-
Potential Absorbed Dose in NC Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
121
100
21
52
65
66
55
4.0
3.8
4.8
7.0
1.5
0.0
8.2
52.9
52.0
57.1
53.8
52.3
56.1
49.1
-
-
-
-
-
-
-
0.049
0.046
0.067
0.031
0.066
0.051
-
-
-
-
-
-
-
-
0.098
0.092
0.123
0.074
0.114
0.094
-
-
-
-
-
-
-
-
0.013
0.013
0.014
0.008
0.019
0.016
-
-
-
-
-
-
-
-
1.62
1.56
1.95
1.55
1.61
1.56
-
Potential Absorbed Dose in NC Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
121
100
21
52
65
66
55
4.0
3.8
4.8
7.0
1.5
0.0
8.2
52.9
52.0
57.1
53.8
52.3
56.1
49.1
-
-
-
-
-
-
-
0.114
0.105
0.154
0.072
0.151
0.118
-
-
-
-
-
-
-
-
0.225
0.211
0.283
0.170
0.262
0.216
-
-
-
-
-
-
-
-
0.029
0.029
0.032
0.017
0.044
0.037
-
-
-
-
-
-
-
-
1.62
1.56
1.95
1.55
1.61
1.56
-
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      N-28

-------
Table N-13b.   Cyfluthrin (68359-37-5):  Range of Potential Exposure and Absorbed Dose in NC
                 Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
121
100
21
52
65
66
55

-------
Table N-14a.    Diazinon (333-41-5):  Estimates of Exposure and Absorbed Dose in NC Adults.
                  Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
121
100
21
52
65
66
55
100.0
100.0
100.0
100.0
100.0
100.0
100.0
95.9
95.0
100.0
100.0
92.3
95.5
96.4
333
384
79.9
167
495
411
250
7.19
8.38
1.49
5.66
8.68
9.27
4.69
1,950
2,130
147
481
2,680
2,300
1,510
34.5
37.8
1.81
23.0
42.4
39.3
27.8
30.0
29.3
33.7
46.2
20.8
26.5
34.3
0.592
0.571
0.699
0.776
0.460
0.681
0.500
1.48
1.53
1.25
1.30
1.54
1.68
1.23
1.64
1.70
1.31
1.59
1.66
1.79
1.45
Potential Exposure in NC Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
121
100
21
52
65
66
55
100.0
100.0
100.0
100.0
100.0
100.0
100.0
95.9
95.0
100.0
100.0
92.3
95.5
96.4
1,090
1,260
263
548
1,630
1,350
821
23.6
27.5
4.89
18.6
28.5
30.4
15.4
6,400
7,010
483
1,580
8,790
7,550
4,950
113
124
5.94
75.6
139
129
91.2
98.6
96.4
111
152
68.4
86.9
113
1.94
1.88
2.30
2.55
1.51
2.24
1.64
1.48
1.53
1.25
1.30
1.54
1.68
1.23
1.64
1.70
1.31
1.59
1.66
1.79
1.45
Potential Absorbed Dose in NC Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
121
100
21
52
65
66
55
100.0
100.0
100.0
100.0
100.0
100.0
100.0
95.9
95.0
100.0
100.0
92.3
95.5
96.4
2.22
2.54
0.599
1.19
3.23
2.83
1.56
0.048
0.056
0.010
0.038
0.058
0.064
0.029
12.6
13.8
1.31
3.64
17.3
15.1
9.37
0.224
0.245
0.014
0.152
0.274
0.259
0.173
0.201
0.198
0.220
0.286
0.148
0.190
0.214
0.004
0.004
0.005
0.005
0.003
0.005
0.003
1.49
1.53
1.28
1.35
1.55
1.70
1.22
1.66
1.72
1.32
1.59
1.71
1.80
1.45
Potential Absorbed Dose in NC Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
121
100
21
52
65
66
55
100.0
100.0
100.0
100.0
100.0
100.0
100.0
95.9
95.0
100.0
100.0
92.3
95.5
96.4
7.28
8.35
1.97
3.91
10.6
9.31
5.12
0.158
0.185
0.033
0.125
0.191
0.210
0.097
41.6
45.5
4.30
11.9
56.8
49.8
30.8
0.735
0.806
0.046
0.500
0.900
0.850
0.568
0.661
0.649
0.723
0.941
0.487
0.623
0.704
0.013
0.013
0.015
0.016
0.011
0.016
0.010
1.49
1.53
1.28
1.35
1.55
1.70
1.22
1.66
1.72
1.32
1.59
1.71
1.80
1.45
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      N-30

-------
Table N-14b.   Diazinon (333-41-5):  Range of Potential Exposure and Absorbed Dose in NC
                 Adults. Summarized  by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
121
100
21
52
65
66
55
4.13
4.13
5.22
6.57
4.13
4.13
9.37

-------
Table N-15a.   Dibenzora./ilanthracene (53-70-3): Estimates of Exposure and Absorbed Dose in
                 NC Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
118
97
21
52
62
63
55
9.5
11.4
0.0
12.3
7.7
10.8
8.2
98.3
97.9
100.0
100.0
98.4
96.8
100.0
-
-
-
-
-
-
-
2.43
2.01
4.38
1.88
3.01
1.80
3.16
-
-
-
-
-
-
-
5.22
3.50
9.78
4.02
6.15
2.90
6.95
-
-
-
-
-
-
-
1.08
1.03
1.34
0.827
1.41
1.05
1.10
-
-
-
-
-
-
-
1.15
1.12
1.29
1.19
1.07
0.999
1.31
Potential Exposure in NC Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
118
97
21
52
62
63
55
9.5
11.4
0.0
12.3
7.7
10.8
8.2
98.3
97.9
100.0
100.0
98.4
96.8
100.0
-
-
-
-
-
-
-
8.74
7.23
15.7
6.77
10.8
6.45
11.4
-
-
-
-
-
-
-
18.7
12.6
35.1
14.4
22.1
10.4
25.0
-
-
-
-
-
-
-
3.87
3.69
4.81
2.97
5.05
3.78
3.96
-
-
-
-
-
-
-
1.15
1.12
1.29
1.19
1.07
0.999
1.31
Potential Absorbed Dose in NC Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
118
97
21
52
62
63
55
9.5
11.4
0.0
12.3
7.7
10.8
8.2
98.3
97.9
100.0
100.0
98.4
96.8
100.0
-
-
-
-
-
-
-
0.016
0.013
0.029
0.012
0.020
0.013
0.020
-
-
-
-
-
-
-
0.034
0.023
0.062
0.026
0.039
0.022
0.043
-
-
-
-
-
-
-
0.007
0.007
0.009
0.005
0.010
0.008
0.007
-
-
-
-
-
-
-
1.15
1.10
1.37
1.18
1.06
1.01
1.30
Potential Absorbed Dose in NC Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
118
97
21
52
62
63
55
9.5
11.4
0.0
12.3
7.7
10.8
8.2
98.3
97.9
100.0
100.0
98.4
96.8
100.0
-
-
-
-
-
-
-
0.058
0.048
0.104
0.043
0.074
0.048
0.070
-
-
-
-
-
-
-
0.121
0.082
0.224
0.094
0.141
0.080
0.155
-
-
-
-
-
-
-
0.026
0.025
0.031
0.019
0.036
0.027
0.025
-
-
-
-
-
-
-
1.15
1.10
1.37
1.18
1.06
1.01
1.30
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      N-32

-------
Table N-15b.   Dibenzora./ilanthracene (53-70-3):  Range of Potential Exposure and Absorbed
                 Dose in NC Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
118
97
21
52
62
63
55

-------
Table N-16a.   Di-n-butylphthalate (84-74-2): Estimates of Exposure and Absorbed Dose in NC
                 Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
118
97
21
51
63
63
55
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
2,910
2,970
2,650
3,180
2,610
2,580
3,270
215
229
154
197
226
226
203
1,460
1,540
951
1,510
1,140
1,500
1,350
216
232
104
210
217
238
190
2,590
2,620
2,460
2,880
2,340
2,230
3,040
153
159
129
131
172
164
142
0.498
0.514
0.415
0.440
0.508
0.551
0.376
0.791
0.828
0.579
0.866
0.695
0.740
0.846
Potential Exposure in NC Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
118
97
21
51
63
63
55
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
10,500
10,700
9,510
1 1 ,400
9,390
9,260
11,700
774
822
553
707
811
813
729
5,250
5,540
3,420
5,410
4,080
5,370
4,830
778
833
374
754
781
854
684
9,310
9,410
8,840
10,300
8,410
8,010
10,900
551
572
465
472
617
590
509
0.498
0.514
0.415
0.440
0.508
0.551
0.376
0.791
0.828
0.579
0.866
0.695
0.740
0.846
Potential Absorbed Dose in NC Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
118
97
21
51
63
63
55
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
19.8
20.3
17.6
20.6
18.5
18.6
21.2
1.47
1.56
1.05
1.19
1.65
1.66
1.25
11.1
11.6
7.49
11.9
8.34
11.3
10.7
1.54
1.64
0.835
1.22
1.70
1.81
1.14
17.4
17.6
16.1
17.8
16.7
16.0
19.0
1.03
1.08
0.844
0.815
1.22
1.17
0.899
0.518
0.532
0.448
0.537
0.483
0.559
0.459
0.814
0.845
0.629
0.852
0.722
0.797
0.818
Potential Absorbed Dose in NC Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
118
97
21
51
63
63
55
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
71.3
72.9
63.2
74.1
66.5
66.9
76.0
5.28
5.61
3.76
4.28
5.91
5.97
4.49
39.7
41.7
26.9
42.7
29.9
40.8
38.4
5.54
5.90
3.00
4.39
6.10
6.50
4.08
62.4
63.4
57.7
64.1
59.9
57.4
68.2
3.71
3.88
3.03
2.93
4.40
4.19
3.23
0.518
0.532
0.448
0.537
0.483
0.559
0.459
0.814
0.845
0.629
0.852
0.722
0.797
0.818
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      N-34

-------
Table N-16b.   Di-n-butylphthalate (84-74-2):  Range of Potential Exposure and Absorbed Dose in
                 NC Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
118
97
21
51
63
63
55
426
426
743
1,130
426
426
1,430
24.4
24.4
50.1
24.4
35.6
50.1
24.4
1,910
1,900
2,120
2,070
1,780
1,600
2,380
89.5
89.5
92.7
71.9
102
94.2
76.6
2,610
2,660
2,560
2,870
2,500
2,300
2,910
131
147
119
108
152
145
128
3,490
3,490
3,450
3,780
3,330
3,230
3,780
241
244
175
223
285
244
223
5,850
6,300
4,050
6,370
4,640
4,550
5,850
651
758
359
581
548
758
581
9,580
9,580
4,640
7,580
5,850
9,580
7,580
1,410
1,410
418
949
1,410
1,410
949
Potential Exposure in NC Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
118
97
21
51
63
63
55
1,530
1,530
2,670
4,050
1,530
1,530
5,150
87.5
87.5
180
87.5
128
180
87.5
6,880
6,840
7,630
7,440
6,390
5,740
8,530
321
321
333
258
368
338
275
9,370
9,540
9,190
10,300
8,980
8,250
10,500
471
528
427
386
546
520
459
12,600
12,600
12,400
13,600
12,000
1 1 ,600
13,600
865
877
630
800
1,020
877
800
21,000
22,600
14,600
22,900
16,700
16,400
21,000
2,340
2,720
1,290
2,090
1,970
2,720
2,090
34,400
34,400
16,700
27,200
21,000
34,400
27,200
5,070
5,070
1,500
3,410
5,070
5,070
3,410
Potential Absorbed Dose in NC Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
118
97
21
51
63
63
55
3.75
3.75
5.84
5.04
3.75
3.75
8.13
0.185
0.185
0.283
0.185
0.278
0.283
0.185
12.3
12.3
12.6
11.9
12.6
11.2
13.4
0.589
0.648
0.583
0.448
0.774
0.661
0.542
17.7
17.9
15.9
17.9
17.3
17.3
18.8
0.958
1.05
0.713
0.661
1.13
1.13
0.796
23.3
23.5
22.8
23.3
23.5
20.9
24.2
1.68
1.79
1.24
1.55
1.79
1.76
1.61
44.0
44.7
28.8
48.7
32.2
38.3
44.0
4.58
5.31
2.74
3.41
4.43
4.58
3.21
71.8
71.8
36.3
55.2
47.7
71.8
55.2
11.6
11.6
3.72
5.90
11.6
11.6
5.53
Potential Absorbed Dose in NC Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
118
97
21
51
63
63
55
13.5
13.5
21.0
18.1
13.5
13.5
29.2
0.666
0.666
1.02
0.666
1.00
1.02
0.666
44.1
44.1
45.4
42.8
45.4
40.3
48.1
2.12
2.33
2.09
1.61
2.78
2.37
1.95
63.6
64.5
57.0
64.5
62.3
62.1
67.4
3.44
3.77
2.56
2.37
4.07
4.07
2.86
83.8
84.4
81.8
83.6
84.4
75.0
86.9
6.02
6.42
4.45
5.56
6.42
6.32
5.78
158
161
103
175
116
138
158
16.4
19.1
9.85
12.3
15.9
16.4
11.5
258
258
130
198
172
258
198
41.6
41.6
13.3
21.2
41.6
41.6
19.9
a  Estimates are labeled as "detected" if any measurement entering into the calculation was detected.  Thus, N specifies the number of subjects having
data entering into the summaries."Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into
the body), divided by the subject's body weight.
                                                     N-35

-------
Table N-17a.   p.p'-DDE (72-55-9):  Estimates of Exposure and Absorbed Dose in NC Adults.
                 Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
121
100
21
52
65
66
55
34.1
33.3
38.1
47.4
23.1
30.8
37.7
43.8
40.0
61.9
57.7
33.8
42.4
45.5
-
-
-
-
-
-
-
-
-
0.314
0.311
-
-
-
-
-
-
-
-
-
-
-
-
0.472
0.704
-
-
-
-
-
-
-
-
-
-
-
-
0.133
0.112
-
-
-
-
-
-
-
-
-
-
-
-
1.31
1.31
-
-
-
Potential Exposure in NC Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
121
100
21
52
65
66
55
34.1
33.3
38.1
47.4
23.1
30.8
37.7
43.8
40.0
61.9
57.7
33.8
42.4
45.5
-
-
-
-
-
-
-
-
-
0.988
0.977
-
-
-
-
-
-
-
-
-
-
-
-
1.48
2.21
-
-
-
-
-
-
-
-
-
-
-
-
0.417
0.353
-
-
-
-
-
-
-
-
-
-
-
-
1.31
1.31
-
-
-
Potential Absorbed Dose in NC Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
121
100
21
52
65
66
55
34.1
33.3
38.1
47.4
23.1
30.8
37.7
43.8
40.0
61.9
57.7
33.8
42.4
45.5
-
-
-
-
-
-
-
-
-
0.002
0.002
-
-
-
-
-
-
-
-
-
-
-
-
0.004
0.003
-
-
-
-
-
-
-
-
-
-
-
-
0.001
0.001
-
-
-
-
-
-
-
-
-
-
-
-
1.33
1.24
-
-
-
Potential Absorbed Dose in NC Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
121
100
21
52
65
66
55
34.1
33.3
38.1
47.4
23.1
30.8
37.7
43.8
40.0
61.9
57.7
33.8
42.4
45.5
-
-
-
-
-
-
-
-
-
0.007
0.005
-
-
-
-
-
-
-
-
-
-
-
-
0.012
0.010
-
-
-
-
-
-
-
-
-
-
-
-
0.003
0.002
-
-
-
-
-
-
-
-
-
-
-
-
1.33
1.24
-
-
-
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      N-36

-------
Table N-17b.   p.p'-DDE (72-55-9): Range of Potential Exposure and Absorbed Dose in NC Adults.
                 Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
121
100
21
52
65
66
55

-------
Table N-18a.   2.4-D (2.4-dichlorophenoxyacetic acid) (94-75-7):  Estimates of Exposure and
                Absorbed Dose in NC Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Potential Exposure
-Aggregated
(ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
104
21
56
65
65
60
126
105
21
57
65
65
61
117
97
20
50
63
65
52
110
90
20
45
61
63
47
52.8
52.9
52.4
64.3
44.6
46.2
60.0
54.0
58.1
33.3
52.6
56.9
52.3
55.7
72.6
74.2
65.0
48.0
90.5
87.7
53.8
96.4
96.7
95.0
91.1
100.0
100.0
91.5
6.84
7.09
5.63
9.17
-
-
8.21
305
323
-
286
329
349
259
5.24
6.16
0.764
-
7.96
6.76
3.34
318
348
183
315
327
360
263
8.34
8.83
5.20
10.2
-
-
9.09
430
458
-
421
451
513
317
17.9
19.6
1.43
-
23.4
22.3
10.0
441
477
150
444
454
520
299
3.78
3.79
3.69
5.24
-
-
4.67
162
165
-
129
197
189
137
0.755
0.963
0.232
-
1.68
1.38
0.356
183
194
141
158
203
200
162
1.06
1.08
0.950
1.09
-
-
1.08
1.15
1.20
-
1.35
0.948
1.03
1.26
2.00
2.02
1.45
-
1.86
1.75
2.06
0.993
1.04
0.721
1.14
0.893
1.00
0.981
Potential Exposure in NC Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Potential Exposure
-Aggregated
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
104
21
56
65
65
60
126
105
21
57
65
65
61
117
97
20
50
63
65
52
110
90
20
45
61
63
47
52.8
52.9
52.4
64.3
44.6
46.2
60.0
54.0
58.1
33.3
52.6
56.9
52.3
55.7
72.6
74.2
65.0
48.0
90.5
87.7
53.8
96.4
96.7
95.0
91.1
100.0
100.0
91.5
31.0
32.1
25.4
41.5
-
-
37.1
1,380
1,460
-
1,290
1,490
1,580
1,170
23.7
27.9
3.46
-
36.0
30.6
15.1
1,440
1,580
828
1,420
1,480
1,630
1,190
37.7
40.0
23.5
45.9
-
-
41.1
1,950
2,070
-
1,910
2,040
2,320
1,430
81.1
88.5
6.46
-
106
101
45.5
1,990
2,160
678
2,010
2,050
2,350
1,350
17.1
17.2
16.7
23.7
-
-
21.1
731
746
-
582
890
856
618
3.42
4.36
1.05
-
7.60
6.23
1.61
828
878
636
716
918
906
734
1.06
1.08
0.950
1.09
-
-
1.08
1.15
1.20
-
1.35
0.948
1.03
1.26
2.00
2.02
1.45
-
1.86
1.75
2.06
0.993
1.04
0.721
1.14
0.893
1.00
0.981
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected.  Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                   N-38

-------
Table N-18b.   2.4-D (2.4-dichlorophenoxyacetic acid) (94-75-7):  Range of Potential Exposure and
                Absorbed Dose in NC Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Potential Exposure
- Aggregated
(ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
104
21
56
65
65
60
126
105
21
57
65
65
61
117
97
20
50
63
65
52
110
90
20
45
61
63
47

-------
Table N-18c.   2.4-D (2.4-dichlorophenoxyacetic acid) (94-75-7): Estimates of Exposure and
                 Absorbed Dose in NC Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in NC Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Potential Absorbed
Dose - Aggregated
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
104
21
56
65
65
60
126
105
21
57
65
65
61
117
97
20
50
63
65
52
110
90
20
45
61
63
47
52.8
52.9
52.4
64.3
44.6
46.2
60.0
54.0
58.1
33.3
52.6
56.9
52.3
55.7
72.6
74.2
65.0
48.0
90.5
87.7
53.8
96.4
96.7
95.0
91.1
100.0
100.0
91.5
0.044
0.046
0.036
0.056
-
-
0.049
2.03
2.15
-
1.79
2.27
2.49
1.55
0.039
0.046
0.006
-
0.060
0.054
0.020
2.11
2.32
1.19
1.96
2.25
2.57
1.51
0.052
0.055
0.035
0.063
-
-
0.053
2.84
3.01
-
2.82
2.93
3.54
1.72
0.145
0.158
0.012
-
0.190
0.188
0.054
2.90
3.14
0.980
2.99
2.93
3.58
1.40
0.025
0.026
0.024
0.032
-
-
0.029
1.09
1.12
-
0.806
1.40
1.35
0.865
0.005
0.007
0.002
-
0.012
0.010
0.002
1.24
1.32
0.915
0.989
1.44
1.43
1.02
1.02
1.04
0.919
1.06
-
-
1.03
1.16
1.22
-
1.36
0.928
1.04
1.24
2.09
2.10
1.53
-
1.93
1.84
2.10
0.981
1.02
0.712
1.12
0.865
1.01
0.912
Potential Absorbed Dose in NC Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose - Aggregated
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
104
21
56
65
65
60
126
105
21
57
65
65
61
117
97
20
50
63
65
52
110
90
20
45
61
63
47
52.8
52.9
52.4
64.3
44.6
46.2
60.0
54.0
58.1
33.3
52.6
56.9
52.3
55.7
72.6
74.2
65.0
48.0
90.5
87.7
53.8
96.4
96.7
95.0
91.1
100.0
100.0
91.5
0.199
0.206
0.164
0.252
-
-
0.222
9.19
9.74
-
8.12
10.3
11.3
6.99
0.177
0.208
0.027
-
0.270
0.245
0.093
9.56
10.5
5.37
8.87
10.2
11.6
6.82
0.236
0.249
0.157
0.286
-
-
0.238
12.8
13.6
-
12.8
13.2
16.0
111
0.655
0.716
0.055
-
0.862
0.848
0.245
13.1
14.2
4.43
13.5
13.3
16.2
6.33
0.115
0.116
0.109
0.146
-
-
0.132
4.92
5.05
-
3.64
6.33
6.10
3.91
0.023
0.030
0.007
-
0.054
0.045
0.010
5.60
5.99
4.14
4.47
6.53
6.46
4.63
1.02
1.04
0.919
1.06
-
-
1.03
1.16
1.22
-
1.36
0.928
1.04
1.24
2.09
2.10
1.53
-
1.93
1.84
2.10
0.981
1.02
0.712
1.12
0.865
1.01
0.912
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                     N-40

-------
Table N-18d.   2.4-D (2.4-dichlorophenoxyacetic acid) (94-75-7): Range of Potential Exposure and
                 Absorbed Dose in NC Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in NC Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Potential Absorbed
Dose - Aggregated
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
104
21
56
65
65
60
126
105
21
57
65
65
61
117
97
20
50
63
65
52
110
90
20
45
61
63
47

-------
Table N-19a.   Heptachlor (76-44-8):  Estimates of Exposure and Absorbed Dose in NC Adults.
                 Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
120
99
21
51
65
65
55
94.4
95.2
90.5
94.7
93.8
95.4
93.4
42.5
43.4
38.1
39.2
41.5
43.1
41.8
259
255
278
242
233
290
226
-
-
-
-
-
-
-
563
586
443
416
554
685
398
-
-
-
-
-
-
-
98.6
99.8
92.7
106
89.4
85.1
115
-
-
-
-
-
-
-
1.30
1.22
1.70
1.32
1.24
1.52
1.00
-
-
-
-
-
-
-
Potential Exposure in NC Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
120
99
21
51
65
65
55
94.4
95.2
90.5
94.7
93.8
95.4
93.4
42.5
43.4
38.1
39.2
41.5
43.1
41.8
693
682
744
648
624
776
604
-
-
-
-
-
-
-
1,510
1,570
1,190
1,120
1,490
1,830
1,070
-
-
-
-
-
-
-
264
267
248
285
240
228
309
-
-
-
-
-
-
-
1.30
1.22
1.70
1.32
1.24
1.52
1.00
-
-
-
-
-
-
-
Potential Absorbed Dose in NC Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
120
99
21
51
65
65
55
94.4
95.2
90.5
94.7
93.8
95.4
93.4
42.5
43.4
38.1
39.2
41.5
43.1
41.8
1.76
1.77
1.71
1.50
1.70
2.07
1.43
-
-
-
-
-
-
-
4.05
4.28
2.65
2.48
4.32
5.12
2.42
-
-
-
-
-
-
-
0.661
0.672
0.605
0.658
0.637
0.610
0.719
-
-
-
-
-
-
-
1.30
1.22
1.69
1.34
1.23
1.52
1.03
-
-
-
-
-
-
-
Potential Absorbed Dose in NC Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
120
99
21
51
65
65
55
94.4
95.2
90.5
94.7
93.8
95.4
93.4
42.5
43.4
38.1
39.2
41.5
43.1
41.8
4.71
4.74
4.59
4.02
4.55
5.55
3.82
-
-
-
-
-
-
-
10.8
11.5
7.09
6.64
11.6
13.7
6.49
-
-
-
-
-
-
-
1.77
1.80
1.62
1.76
1.71
1.63
1.93
-
-
-
-
-
-
-
1.30
1.22
1.69
1.34
1.23
1.52
1.03
-
-
-
-
-
-
-
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      N-42

-------
Table N-19b.   Heptachlor (76-44-8): Range of Potential Exposure and Absorbed Dose in NC
                 Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
120
99
21
51
65
65
55

-------
Table N-20a.   lndenori.2.3-cc/|pvrene (193-39-5):  Estimates of Exposure and Absorbed Dose in
                 NC Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
117
96
21
52
61
62
55
66.7
66.7
66.7
82.5
52.3
64.6
68.9
100.0
100.0
100.0
100.0
100.0
100.0
100.0
2.00
2.04
1.83
2.51
1.57
2.13
1.87
9.96
8.38
17.2
7.68
12.4
7.40
12.9
2.17
2.22
1.92
2.48
1.82
2.61
1.59
26.0
14.8
53.2
17.4
32.2
11.8
35.8
1.43
1.45
1.36
1.83
1.15
1.40
1.46
4.38
4.43
4.14
3.32
5.71
4.48
4.26
0.737
0.747
0.704
0.750
0.669
0.807
0.661
1.07
1.02
1.33
1.07
1.03
0.926
1.22
Potential Exposure in NC Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
117
96
21
52
61
62
55
66.7
66.7
66.7
82.5
52.3
64.6
68.9
100.0
100.0
100.0
100.0
100.0
100.0
100.0
7.25
7.38
6.61
9.08
5.67
7.70
6.76
36.1
30.3
62.3
27.8
44.7
26.8
46.5
7.85
8.04
6.93
8.98
6.59
9.43
5.74
94.2
53.4
193
63.1
117
42.6
130
5.18
5.23
4.93
6.61
4.15
5.08
5.29
15.8
16.0
15.0
12.0
20.7
16.2
15.4
0.737
0.747
0.704
0.750
0.669
0.807
0.661
1.07
1.02
1.33
1.07
1.03
0.926
1.22
Potential Absorbed Dose in NC Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
117
96
21
52
61
62
55
66.7
66.7
66.7
82.5
52.3
64.6
68.9
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.013
0.013
0.013
0.016
0.011
0.015
0.011
0.067
0.056
0.120
0.049
0.086
0.055
0.082
0.014
0.014
0.017
0.017
0.012
0.018
0.009
0.177
0.095
0.367
0.112
0.221
0.090
0.240
0.010
0.010
0.009
0.011
0.008
0.010
0.009
0.030
0.030
0.027
0.021
0.041
0.032
0.027
0.728
0.735
0.708
0.751
0.686
0.806
0.638
1.08
1.01
1.40
1.07
1.02
0.941
1.22
Potential Absorbed Dose in NC Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
117
96
21
52
61
62
55
66.7
66.7
66.7
82.5
52.3
64.6
68.9
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.048
0.049
0.045
0.057
0.040
0.055
0.041
0.243
0.202
0.433
0.176
0.311
0.197
0.295
0.052
0.051
0.061
0.061
0.044
0.065
0.033
0.640
0.344
1.33
0.404
0.801
0.326
0.868
0.035
0.035
0.032
0.041
0.030
0.036
0.033
0.107
0.109
0.098
0.075
0.147
0.116
0.098
0.728
0.735
0.708
0.751
0.686
0.806
0.638
1.08
1.01
1.40
1.07
1.02
0.941
1.22
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      N-44

-------
Table N-20b.   lndenori.2.3-cc/|pvrene (193-39-5):  Range of Potential Exposure and Absorbed
                 Dose in NC Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
117
96
21
52
61
62
55

-------
Table N-21a.   Pentachlorophenol (87-86-5): Estimates of Exposure and Absorbed Dose in NC
                Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
104
21
56
65
65
60
125
104
21
57
64
65
60
118
97
21
50
64
65
53
99.2
99.0
100.0
100.0
98.5
98.5
100.0
8.8
9.6
4.8
7.0
10.9
6.2
11.7
94.1
93.8
95.2
96.0
92.2
93.8
94.3
30.0
29.0
35.0
36.9
24.9
33.5
26.2
-
-
-
-
-
-
-
4.19
4.39
3.26
3.23
5.11
4.05
4.37
44.2
40.4
60.4
49.0
40.5
58.4
19.3
-
-
-
-
-
-
-
10.4
11.3
4.47
4.62
13.6
5.67
14.3
18.2
17.6
21.0
24.1
14.4
15.9
21.0
-
-
-
-
-
-
-
1.62
1.61
1.65
1.40
1.85
1.95
1.29
0.920
0.927
0.893
0.851
0.939
1.10
0.659
-
-
-
-
-
-
-
1.37
1.42
1.18
1.45
1.34
1.24
1.51
Potential Exposure in NC Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
104
21
56
65
65
60
125
104
21
57
64
65
60
118
97
21
50
64
65
53
99.2
99.0
100.0
100.0
98.5
98.5
100.0
8.8
9.6
4.8
7.0
10.9
6.2
11.7
94.1
93.8
95.2
96.0
92.2
93.8
94.3
113
109
131
139
93.4
126
98.5
-
-
-
-
-
-
-
15.7
16.5
12.2
12.1
19.2
15.2
16.4
166
152
227
184
152
219
72.4
-
-
-
-
-
-
-
39.2
42.6
16.8
17.3
50.9
21.3
53.9
68.2
66.2
78.9
90.5
54.0
59.6
79.0
-
-
-
-
-
-
-
6.07
6.05
6.20
5.25
6.95
7.30
4.84
0.920
0.927
0.893
0.851
0.939
1.10
0.659
-
-
-
-
-
-
-
1.37
1.42
1.18
1.45
1.34
1.24
1.51
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                   N-46

-------
Table N-21b.   Pentachlorophenol (87-86-5):  Range of Potential Exposure and Absorbed Dose in
                NC Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
104
21
56
65
65
60
125
104
21
57
64
65
60
118
97
21
50
64
65
53

-------
Table N-21c.   Pentachlorophenol (87-86-5):  Estimates of Exposure and Absorbed Dose in NC
                 Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in NC Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
104
21
56
65
65
60
125
104
21
57
64
65
60
118
97
21
50
64
65
53
99.2
99.0
100.0
100.0
98.5
98.5
100.0
8.8
9.6
4.8
7.0
10.9
6.2
11.7
94.1
93.8
95.2
96.0
92.2
93.8
94.3
0.204
0.192
0.259
0.248
0.171
0.242
0.162
-
-
-
-
-
-
-
0.029
0.030
0.022
0.020
0.036
0.029
0.027
Potential Absorbed Dose in NC Adults (pmo
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
104
21
56
65
65
60
125
104
21
57
64
65
60
118
97
21
50
64
65
53
99.2
99.0
100.0
100.0
98.5
98.5
100.0
8.8
9.6
4.8
7.0
10.9
6.2
11.7
94.1
93.8
95.2
96.0
92.2
93.8
94.3
0.765
0.723
0.974
0.929
0.641
0.910
0.608
-
-
-
-
-
-
-
0.107
0.113
0.082
0.076
0.136
0.111
0.103
0.324
0.259
0.549
0.394
0.258
0.432
0.120
-
-
-
-
-
-
-
0.071
0.077
0.031
0.029
0.093
0.044
0.095
es/kg/day)
1.22
0.973
2.06
1.48
0.970
1.62
0.450
-
-
-
-
-
-
-
0.267
0.289
0.115
0.109
0.348
0.164
0.356
0.122
0.119
0.137
0.149
0.103
0.114
0.131
-
-
-
-
-
-
-
0.011
0.011
0.011
0.009
0.013
0.014
0.008

0.458
0.447
0.515
0.559
0.386
0.427
0.494
-
-
-
-
-
-
-
0.041
0.041
0.040
0.033
0.050
0.052
0.031
0.911
0.911
0.923
0.906
0.910
1.11
0.635
-
-
-
-
-
-
-
1.37
1.41
1.21
1.45
1.32
1.24
1.47

0.911
0.911
0.923
0.906
0.910
1.11
0.635
-
-
-
-
-
-
-
1.37
1.41
1.21
1.45
1.32
1.24
1.47
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected.  Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      N-48

-------
Table N-21d.   Pentachlorophenol (87-86-5): Range of Potential Exposure and Absorbed Dose in
                 NC Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in NC Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
F
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
104
21
56
65
65
60
125
104
21
57
64
65
60
118
97
21
50
64
65
53
otentia
125
104
21
56
65
65
60
125
104
21
57
64
65
60
118
97
21
50
64
65
53

-------
Table N-22a.   c/s-Permethrin (61949-76-6):  Estimates of Exposure and Absorbed Dose in NC
                 Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
121
100
21
52
65
66
55
69.0
65.7
85.7
87.7
52.3
61.5
77.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
19.1
19.2
18.6
32.6
8.00
13.8
24.7
144
95.7
374
61.8
217
91.6
207
42.9
44.4
35.3
59.7
12.8
25.4
55.5
689
239
1,580
120
931
231
992
6.07
5.88
7.11
11.3
3.59
4.62
8.11
23.9
23.9
23.9
24.6
24.2
24.5
23.2
1.40
1.43
1.28
1.43
1.17
1.45
1.31
1.53
1.50
1.68
1.26
1.74
1.51
1.56
Potential Exposure in NC Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
121
100
21
52
65
66
55
69.0
65.7
85.7
87.7
52.3
61.5
77.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
48.8
49.1
47.6
83.4
20.4
35.3
63.2
368
244
955
158
555
234
528
110
113
90.2
153
32.7
64.9
142
1,760
612
4,040
306
2,380
589
2,530
15.5
15.0
18.2
28.9
9.18
11.8
20.7
61.0
61.0
61.1
62.9
62.0
62.5
59.3
1.40
1.43
1.28
1.43
1.17
1.45
1.31
1.53
1.50
1.68
1.26
1.74
1.51
1.56
Potential Absorbed Dose in NC Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
121
100
21
52
65
66
55
69.0
65.7
85.7
87.7
52.3
61.5
77.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.129
0.129
0.130
0.217
0.058
0.100
0.160
1.00
0.739
2.26
0.404
1.53
0.712
1.35
0.309
0.313
0.297
0.434
0.097
0.203
0.391
4.30
2.03
9.40
0.817
5.79
1.90
6.04
0.041
0.040
0.046
0.070
0.026
0.033
0.051
0.162
0.163
0.156
0.154
0.173
0.175
0.147
1.39
1.42
1.24
1.46
1.17
1.44
1.31
1.57
1.55
1.69
1.30
1.78
1.53
1.61
Potential Absorbed Dose in NC Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
121
100
21
52
65
66
55
69.0
65.7
85.7
87.7
52.3
61.5
77.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.330
0.330
0.332
0.553
0.147
0.255
0.410
2.56
1.89
5.76
1.03
3.91
1.82
3.45
0.790
0.800
0.759
1.11
0.248
0.519
1.00
11.0
5.19
24.0
2.09
14.8
4.87
15.4
0.104
0.101
0.118
0.179
0.065
0.085
0.129
0.413
0.416
0.399
0.394
0.442
0.447
0.375
1.39
1.42
1.24
1.46
1.17
1.44
1.31
1.57
1.55
1.69
1.30
1.78
1.53
1.61
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      N-50

-------
Table N-22b.   c/s-Permethrin (61949-76-6):  Range of Potential Exposure and Absorbed Dose in
                 NC Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
121
100
21
52
65
66
55

-------
Table N-23a.   frans-Permethrin (61949-77-7): Estimates of Exposure and Absorbed Dose in NC
                 Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
121
100
21
52
65
66
55
68.3
64.8
85.7
87.7
52.3
60.0
77.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
17.0
17.2
16.1
29.8
6.65
12.3
22.1
145
95.6
380
59.9
221
89.9
211
44.2
46.0
34.1
62.3
12.0
25.0
57.9
713
241
1,640
136
962
236
1,030
4.64
4.51
5.35
8.76
2.74
3.64
6.01
20.0
20.0
20.0
19.3
21.3
21.4
18.5
1.43
1.45
1.35
1.47
1.17
1.47
1.35
1.63
1.63
1.67
1.39
1.84
1.58
1.71
Potential Exposure in NC Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
121
100
21
52
65
66
55
68.3
64.8
85.7
87.7
52.3
60.0
77.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
43.6
44.0
41.1
76.0
17.0
31.5
56.4
371
244
972
153
565
230
540
113
118
87.2
159
30.6
63.8
148
1,820
615
4,190
347
2,460
604
2,620
11.9
11.5
13.7
22.4
7.01
9.31
15.3
51.2
51.2
51.1
49.4
54.6
54.7
47.2
1.43
1.45
1.35
1.47
1.17
1.47
1.35
1.63
1.63
1.67
1.39
1.84
1.58
1.71
Potential Absorbed Dose in NC Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
121
100
21
52
65
66
55
68.3
64.8
85.7
87.7
52.3
60.0
77.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.117
0.117
0.116
0.203
0.047
0.090
0.146
1.00
0.734
2.27
0.388
1.54
0.707
1.35
0.333
0.341
0.297
0.474
0.088
0.202
0.430
4.42
1.99
9.76
0.893
5.94
1.94
6.21
0.031
0.030
0.035
0.054
0.020
0.026
0.037
0.136
0.137
0.130
0.121
0.152
0.153
0.117
1.42
1.44
1.32
1.51
1.17
1.46
1.36
1.67
1.68
1.63
1.42
1.88
1.61
1.74
Potential Absorbed Dose in NC Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
121
100
21
52
65
66
55
68.3
64.8
85.7
87.7
52.3
60.0
77.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.299
0.300
0.297
0.518
0.121
0.230
0.373
2.56
1.88
5.81
0.992
3.95
1.81
3.46
0.850
0.870
0.760
1.21
0.224
0.517
1.10
11.3
5.10
25.0
2.28
15.2
4.97
15.9
0.079
0.078
0.089
0.139
0.050
0.067
0.096
0.346
0.349
0.333
0.310
0.390
0.391
0.299
1.42
1.44
1.32
1.51
1.17
1.46
1.36
1.67
1.68
1.63
1.42
1.88
1.61
1.74
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                     N-52

-------
Table N-23b.   frans-Permethrin (61949-77-7):  Range of Potential Exposure and Absorbed Dose in
                 NC Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
121
100
21
52
65
66
55

-------
Table N-24a.   PCB 52 (35693-99-3):  Estimates of Exposure and Absorbed Dose in NC Adults.
                 Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
121
100
21
52
65
66
55
96.0
95.2
100.0
98.2
96.9
95.4
96.7
33.9
35.0
28.6
30.8
36.9
27.3
41.8
8.19
8.09
8.69
9.54
7.33
6.78
9.69
-
-
-
-
-
-
-
11.3
11.7
9.23
15.8
5.20
5.80
15.0
-
-
-
-
-
-
-
6.08
5.94
6.80
6.44
6.14
5.56
6.68
-
-
-
-
-
-
-
0.683
0.699
0.597
0.739
0.587
0.612
0.745
-
-
-
-
-
-
-
Potential Exposure in NC Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
121
100
21
52
65
66
55
96.0
95.2
100.0
98.2
96.9
95.4
96.7
33.9
35.0
28.6
30.8
36.9
27.3
41.8
28.0
27.7
29.8
32.7
25.1
23.2
33.2
-
-
-
-
-
-
-
38.6
40.0
31.6
54.0
17.8
19.9
51.4
-
-
-
-
-
-
-
20.8
20.4
23.3
22.0
21.0
19.1
22.9
-
-
-
-
-
-
-
0.683
0.699
0.597
0.739
0.587
0.612
0.745
-
-
-
-
-
-
-
Potential Absorbed Dose in NC Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
121
100
21
52
65
66
55
96.0
95.2
100.0
98.2
96.9
95.4
96.7
33.9
35.0
28.6
30.8
36.9
27.3
41.8
0.056
0.057
0.053
0.064
0.052
0.048
0.065
-
-
-
-
-
-
-
0.084
0.090
0.042
0.119
0.035
0.035
0.115
-
-
-
-
-
-
-
0.041
0.040
0.044
0.040
0.044
0.040
0.042
-
-
-
-
-
-
-
0.713
0.740
0.567
0.818
0.580
0.619
0.805
-
-
-
-
-
-
-
Potential Absorbed Dose in NC Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
121
100
21
52
65
66
55
96.0
95.2
100.0
98.2
96.9
95.4
96.7
33.9
35.0
28.6
30.8
36.9
27.3
41.8
0.193
0.195
0.182
0.219
0.177
0.165
0.223
-
-
-
-
-
-
-
0.287
0.308
0.143
0.407
0.118
0.118
0.393
-
-
-
-
-
-
-
0.140
0.137
0.152
0.137
0.150
0.137
0.143
-
-
-
-
-
-
-
0.713
0.740
0.567
0.818
0.580
0.619
0.805
-
-
-
-
-
-
-
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      N-54

-------
Table N-24b.   PCB 52 (35693-99-3):  Range of Potential Exposure and Absorbed Dose in NC
                 Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
121
100
21
52
65
66
55

-------
Table N-25a.   PCB 95 (38379-99-6):  Estimates of Exposure and Absorbed Dose in NC Adults.
                 Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
121
100
21
52
65
66
55
81.0
81.0
81.0
80.7
86.2
76.9
85.2
36.4
35.0
42.9
34.6
36.9
36.4
36.4
1.76
1.65
2.35
2.34
1.34
1.52
2.02
-
-
-
-
-
-
-
3.89
3.67
4.92
5.55
1.45
2.81
4.80
-
-
-
-
-
-
-
1.10
1.09
1.16
1.24
1.04
1.03
1.17
-
-
-
-
-
-
-
0.750
0.706
0.957
0.853
0.627
0.731
0.770
-
-
-
-
-
-
-
Potential Exposure in NC Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
121
100
21
52
65
66
55
81.0
81.0
81.0
80.7
86.2
76.9
85.2
36.4
35.0
42.9
34.6
36.9
36.4
36.4
5.40
5.04
7.19
7.16
4.10
4.65
6.20
-
-
-
-
-
-
-
11.9
11.3
15.1
17.0
4.44
8.61
14.7
-
-
-
-
-
-
-
3.36
3.33
3.54
3.79
3.19
3.16
3.59
-
-
-
-
-
-
-
0.750
0.706
0.957
0.853
0.627
0.731
0.770
-
-
-
-
-
-
-
Potential Absorbed Dose in NC Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
121
100
21
52
65
66
55
81.0
81.0
81.0
80.7
86.2
76.9
85.2
36.4
35.0
42.9
34.6
36.9
36.4
36.4
0.012
0.012
0.013
0.015
0.010
0.010
0.013
-
-
-
-
-
-
-
0.027
0.028
0.022
0.038
0.009
0.013
0.036
-
-
-
-
-
-
-
0.007
0.007
0.008
0.008
0.007
0.007
0.007
-
-
-
-
-
-
-
0.755
0.732
0.883
0.870
0.643
0.736
0.781
-
-
-
-
-
-
-
Potential Absorbed Dose in NC Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
121
100
21
52
65
66
55
81.0
81.0
81.0
80.7
86.2
76.9
85.2
36.4
35.0
42.9
34.6
36.9
36.4
36.4
0.036
0.035
0.040
0.046
0.029
0.031
0.041
-
-
-
-
-
-
-
0.082
0.084
0.068
0.117
0.029
0.041
0.110
-
-
-
-
-
-
-
0.023
0.022
0.023
0.023
0.023
0.023
0.022
-
-
-
-
-
-
-
0.755
0.732
0.883
0.870
0.643
0.736
0.781
-
-
-
-
-
-
-
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      N-56

-------
Table N-25b.   PCB 95 (38379-99-6):  Range of Potential Exposure and Absorbed Dose in NC
                 Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
121
100
21
52
65
66
55

-------
Table N-26a.   PCB 101 (37680-73-2):  Estimates of Exposure and Absorbed Dose in NC Adults.
                 Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
121
100
21
52
65
66
55
57.1
54.3
71.4
56.1
61.5
61.5
52.5
36.4
35.0
42.9
36.5
35.4
36.4
36.4
1.47
1.31
2.28
1.94
1.12
1.39
1.55
-
-
-
-
-
-
-
3.39
2.88
5.27
4.77
1.44
3.04
3.74
-
-
-
-
-
-
-
0.827
0.799
0.981
0.901
0.800
0.845
0.807
-
-
-
-
-
-
-
0.834
0.785
1.05
0.950
0.727
0.818
0.857
-
-
-
-
-
-
-
Potential Exposure in NC Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
121
100
21
52
65
66
55
57.1
54.3
71.4
56.1
61.5
61.5
52.5
36.4
35.0
42.9
36.5
35.4
36.4
36.4
4.50
4.00
6.99
5.93
3.44
4.27
4.75
-
-
-
-
-
-
-
10.4
8.81
16.1
14.6
4.41
9.30
11.5
-
-
-
-
-
-
-
2.53
2.45
3.01
2.76
2.45
2.59
2.47
-
-
-
-
-
-
-
0.834
0.785
1.05
0.950
0.727
0.818
0.857
-
-
-
-
-
-
-
Potential Absorbed Dose in NC Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
121
100
21
52
65
66
55
57.1
54.3
71.4
56.1
61.5
61.5
52.5
36.4
35.0
42.9
36.5
35.4
36.4
36.4
0.010
0.009
0.012
0.012
0.008
0.009
0.010
-
-
-
-
-
-
-
0.022
0.021
0.024
0.031
0.010
0.014
0.028
-
-
-
-
-
-
-
0.006
0.005
0.006
0.006
0.006
0.006
0.005
-
-
-
-
-
-
-
0.849
0.823
0.979
0.972
0.747
0.826
0.870
-
-
-
-
-
-
-
Potential Absorbed Dose in NC Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
121
100
21
52
65
66
55
57.1
54.3
71.4
56.1
61.5
61.5
52.5
36.4
35.0
42.9
36.5
35.4
36.4
36.4
0.030
0.028
0.038
0.037
0.025
0.028
0.031
-
-
-
-
-
-
-
0.067
0.066
0.073
0.094
0.029
0.044
0.085
-
-
-
-
-
-
-
0.017
0.016
0.020
0.017
0.017
0.019
0.015
-
-
-
-
-
-
-
0.849
0.823
0.979
0.972
0.747
0.826
0.870
-
-
-
-
-
-
-
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      N-58

-------
Table N-26b.   PCB 101 (37680-73-2):  Range of Potential Exposure and Absorbed Dose in NC
                 Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
121
100
21
52
65
66
55

-------
Table N-27a.   3.5.6-TCP (3.5.6-trichloro-2-pyridinol) (6515-38-4): Estimates of Exposure and
                Absorbed Dose in NC Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Potential Exposure
-Aggregated
(ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
128
107
21
59
65
65
63
121
100
21
52
65
66
55
117
96
21
50
63
64
53
100.0
100.0
100.0
100.0
100.0
100.0
100.0
98.4
98.1
100.0
98.3
98.5
98.5
98.4
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
43.5
44.8
37.1
48.6
40.1
38.6
48.8
1,620
1,680
1,310
1,110
2,060
1,880
1,340
7.33
5.31
16.9
8.32
5.42
6.74
8.03
1,660
1,720
1,360
1,200
2,010
1,950
1,310
87.5
93.9
44.9
102
75.6
76.0
98.7
2,180
2,360
742
1,760
2,470
2,400
1,920
18.3
9.73
37.7
23.3
8.75
13.9
22.6
2,130
2,330
757
1,900
2,300
2,410
1,700
23.1
23.2
22.8
25.2
21.4
19.2
28.2
911
890
1,030
598
1,300
1,110
746
2.52
2.33
3.65
2.59
2.33
2.62
2.40
1,010
993
1,080
681
1,340
1,180
831
1.00
1.00
1.01
1.01
1.02
1.09
0.870
1.20
1.26
0.880
1.26
1.04
1.14
1.24
1.36
1.28
1.70
1.35
1.34
1.37
1.37
1.06
1.11
0.848
1.08
0.967
1.08
1.01
Potential Exposure in NC Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Potential Exposure
-Aggregated
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
128
107
21
59
65
65
63
121
100
21
52
65
66
55
117
96
21
50
63
64
53
100.0
100.0
100.0
100.0
100.0
100.0
100.0
98.4
98.1
100.0
98.3
98.5
98.5
98.4
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
219
226
187
245
202
194
246
8,150
8,460
6,610
5,610
10,400
9,480
6,780
36.9
26.8
85.2
41.9
27.3
34.0
40.5
8,350
8,680
6,880
6,050
10,100
9,810
6,600
441
473
226
516
381
383
497
1 1 ,000
1 1 ,900
3,740
8,890
12,500
12,100
9,660
92.2
49.0
190
118
44.1
70.0
114
10,800
1 1 ,700
3,810
9,550
1 1 ,600
12,200
8,560
117
117
115
127
108
96.9
142
4,590
4,480
5,170
3,010
6,550
5,570
3,760
12.7
11.7
18.4
13.0
11.7
13.2
12.1
5,080
5,000
5,440
3,430
6,770
5,960
4,190
1.00
1.00
1.01
1.01
1.02
1.09
0.870
1.20
1.26
0.880
1.26
1.04
1.14
1.24
1.36
1.28
1.70
1.35
1.34
1.37
1.37
1.06
1.11
0.848
1.08
0.967
1.08
1.01
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                   N-60

-------
Table N-27b.   3.5.6-TCP (3.5.6-trichloro-2-pyridinol) (6515-38-4): Range of Potential Exposure
                and Absorbed Dose in NC Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in NC Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Potential Exposure
- Aggregated
(ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
128
107
21
59
65
65
63
121
100
21
52
65
66
55
117
96
21
50
63
64
53
2.13
2.13
2.94
2.94
2.13
2.13
7.00

-------
Table N-27c.   3.5.6-TCP (3.5.6-trichloro-2-pyridinol) (6515-38-4):  Estimates of Exposure and
                 Absorbed Dose in NC Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in NC Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Potential Absorbed
Dose - Aggregated
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
128
107
21
59
65
65
63
121
100
21
52
65
66
55
117
96
21
50
63
64
53
100.0
100.0
100.0
100.0
100.0
100.0
100.0
98.4
98.1
100.0
98.3
98.5
98.5
98.4
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.300
0.316
0.222
0.336
0.274
0.258
0.345
11.2
11.8
8.38
7.59
14.4
13.9
8.41
0.051
0.038
0.108
0.054
0.039
0.048
0.053
11.6
12.2
8.71
8.27
14.0
14.4
8.15
0.665
0.721
0.238
0.874
0.439
0.432
0.848
15.7
17.0
4.70
14.9
16.1
18.9
11.0
0.121
0.078
0.231
0.144
0.059
0.105
0.139
15.5
16.9
4.74
16.1
15.0
19.0
8.73
0.155
0.157
0.149
0.156
0.153
0.138
0.176
6.10
5.99
6.70
3.71
9.24
7.88
4.69
0.017
0.016
0.024
0.016
0.017
0.019
0.015
6.81
6.76
7.05
4.26
9.57
8.45
5.25
1.00
1.02
0.945
1.04
1.00
1.06
0.925
1.24
1.31
0.808
1.32
1.02
1.15
1.29
1.38
1.31
1.68
1.35
1.37
1.35
1.41
1.10
1.16
0.776
1.15
0.945
1.10
1.06
Potential Absorbed Dose in NC Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose - Aggregated
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
128
107
21
59
65
65
63
121
100
21
52
65
66
55
117
96
21
50
63
64
53
100.0
100.0
100.0
100.0
100.0
100.0
100.0
98.4
98.1
100.0
98.3
98.5
98.5
98.4
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
1.51
1.59
1.12
1.69
1.38
1.30
1.74
56.5
59.3
42.2
38.2
72.4
70.2
42.4
0.255
0.194
0.546
0.271
0.195
0.244
0.267
58.3
61.4
43.9
41.7
70.7
72.5
41.1
3.35
3.63
1.20
4.41
2.21
2.18
4.27
79.0
85.6
23.7
75.3
81.1
95.0
55.5
0.611
0.395
1.17
0.725
0.300
0.527
0.703
77.9
85.1
23.9
81.0
75.4
95.6
44.0
0.783
0.789
0.751
0.788
0.769
0.695
0.889
30.7
30.2
33.7
18.7
46.6
39.7
23.6
0.086
0.080
0.120
0.082
0.084
0.094
0.077
34.3
34.1
35.5
21.5
48.2
42.6
26.5
1.00
1.02
0.945
1.04
1.00
1.06
0.925
1.24
1.31
0.808
1.32
1.02
1.15
1.29
1.38
1.31
1.68
1.35
1.37
1.35
1.41
1.10
1.16
0.776
1.15
0.945
1.10
1.06
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected.  Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      N-62

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Table N-27d.   3.5.6-TCP (3.5.6-trichloro-2-pyridinol) (6515-38-4):  Range of Potential Exposure
                 and Absorbed Dose in NC Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in NC Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Potential Absorbed
Dose - Aggregated
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
126
105
21
57
65
65
61
128
107
21
59
65
65
63
121
100
21
52
65
66
55
117
96
21
50
63
64
53
0.016
0.017
0.016
0.016
0.017
0.016
0.046

-------

-------
                                   Appendix O
Descriptive Statistics of Potential Exposure Level and Potential Absorbed Dose Estimates
                   for Target Pollutants in Participating OH Adults
                                        0-1

-------
0-2

-------
This appendix contains tables of descriptive statistics of potential exposure and potential absorbed dose
estimates (expressed in both ng and pmole units) in OH adults for the following pollutants and
metabolites:
Pollutant/Metabolite
Benz[a]anthracene
Benzo[£>]fluoranthene
Benzo[/<]fluoranthene
Benzo[g/7/]perylene
Benzo[a]pyrene
Benzo[e]pyrene
Benzylbutylphthalate
Bisphenol-A
a/p/?a-Chlordane
gamma-Chlordane
Chlorpyrifos
Chrysene
Cyfluthrin
Diazinon
Dibenzo[a,/?]anthracene
Di-n-butylphthalate
p,p'-DDE
2,4-D (2,4-dichlorophenoxyacetic acid)
lndeno[1 ,2,3-cd]pyrene
Pentachlorophenol
c/s-Permethrin
frans-Permethrin
PCS 52
PCB95
PCS 101
3,5,6-TCP (3,5,6-trichloro-2-Dvridinol)
Table Numbers for
Potential Exposure
Summaries
Tables O-1a, O-1b
Tables O-2a, O-2b
Tables O-3a, O-3b
Tables O-4a, O-4b
Tables O-5a, O-5b
Tables O-6a, O-6b
Tables O-7a, O-7b
Tables O-8a, O-8b
Tables O-9a, O-9b
Tables O-10a, O-10b
Tables O-11 a, O-11b
Tables O-12a, O-12b
Tables O-13a, O-13b
Tables O-14a, O-14b
Tables O-15a, O-15b
Tables O-16a, O-16b
Tables O-17a, O-17b
Tables O-18a, O-18b
Tables O-19a, O-19b
Tables O-20a, O-20b
Tables O-21 a, O-21b
Tables O-22a, O-22b
Tables O-23a, O-23b
Tables O-24a, O-24b
Tables O-25a, O-25b
Tables O-26a, O-26b
Table Numbers for
Potential Absorbed
Dose Summaries
Tables O-1a, O-1b
Tables O-2a, O-2b
Tables O-3a, O-3b
Tables O-4a, O-4b
Tables O-5a, O-5b
Tables O-6a, O-6b
Tables O-7a, O-7b
Tables O-8a, O-8b
Tables O-9a, O-9b
Tables O-10a, O-10b
Tables O-11 a, O-11b
Tables O-12a, O-12b
Tables O-13a, O-13b
Tables O-14a, O-14b
Tables O-15a, O-15b
Tables O-16a, O-16b
Tables O-17a, O-17b
Tables O-18c, O-18d
Tables O-19a, O-19b
Tables O-20c, O-20d
Tables O-21 a, O-21b
Tables O-22a, O-22b
Tables O-23a, O-23b
Tables O-24a, O-24b
Tables O-25a, O-25b
Tables O-26c, O-26d
Descriptive statistics are presented separately for the following groups of OH adult participants:
        All participants
        Participants from urban areas
        Participants from rural areas
        Participants from low-income areas
        Participants from middle/upper-income areas
        Caregivers of stay-at-home children
        Caregivers of day care children
                                                  0-3

-------
Table O-1a.    Benzralanthracene (56-55-3): Estimates of Potential Exposure and Potential
                 Absorbed Dose in OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
109
93
16
33
65
60
49
119
102
17
38
68
62
57
39.4
45.2
6.3
51.5
36.9
36.7
42.9
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
1.88
-
-
-
39.1
43.1
15.0
25.7
51.3
32.2
46.6
-
-
-
2.62
-
-
-
91.9
97.6
38.1
41.5
116
64.8
114
-
-
-
1.20
-
-
-
13.9
16.5
4.95
12.9
15.1
11.8
16.6
-
-
-
0.815
-
-
-
1.28
1.21
1.23
1.13
1.43
1.31
1.24
Potential Exposure in OH Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
109
93
16
33
65
60
49
119
102
17
38
68
62
57
39.4
45.2
6.3
51.5
36.9
36.7
42.9
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
8.24
-
-
-
171
189
65.7
113
225
141
204
—
-
-
11.5
-
-
-
402
427
167
182
510
284
501
—
-
-
5.26
-
-
-
60.9
72.3
21.7
56.7
66.1
51.7
72.7
-
-
-
0.815
-
-
-
1.28
1.21
1.23
1.13
1.43
1.31
1.24
Potential Absorbed Dose in OH Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
109
93
16
33
65
60
49
119
102
17
38
68
62
57
39.4
45.2
6.3
51.5
36.9
36.7
42.9
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
0.014
-
-
-
0.274
0.304
0.094
0.169
0.367
0.247
0.304
-
-
-
0.020
-
-
-
0.667
0.711
0.232
0.273
0.849
0.539
0.787
-
-
-
0.008
-
-
-
0.095
0.113
0.033
0.086
0.105
0.083
0.109
-
-
-
0.903
-
-
-
1.30
1.24
1.20
1.12
1.46
1.35
1.24
Potential Absorbed Dose in OH Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
109
93
16
33
65
60
49
119
102
17
38
68
62
57
39.4
45.2
6.3
51.5
36.9
36.7
42.9
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
0.060
-
-
-
1.20
1.33
0.410
0.741
1.61
1.08
1.33
—
-
-
0.089
-
-
-
2.92
3.11
1.02
1.19
3.72
2.36
3.45
—
-
-
0.035
-
-
-
0.415
0.494
0.145
0.376
0.459
0.363
0.479
-
-
-
0.903
-
-
-
1.30
1.24
1.20
1.12
1.46
1.35
1.24
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      0-4

-------
Table O-1b.    Benzralanthracene (56-55-3):  Range of Potential Exposure and Potential Absorbed
                 Dose in OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
109
93
16
33
65
60
49
119
102
17
38
68
62
57

-------
Table O-2a.    Benzorfrlfluoranthene (205-99-2):  Estimates of Potential Exposure and Potential
                 Absorbed Dose in OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
119
102
17
38
68
62
57
45.6
48.1
29.4
56.4
42.5
37.7
55.4
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
2.45
-
-
1.84
91.4
101
34.2
62.9
117
72.7
112
-
-
-
4.91
-
-
3.83
216
230
75.3
108
271
136
278
-
-
-
1.25
-
-
1.12
34.9
41.0
13.5
31.2
38.3
30.9
39.9
-
-
-
0.920
-
-
0.753
1.23
1.17
1.18
1.11
1.34
1.22
1.23
Potential Exposure in OH Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
119
102
17
38
68
62
57
45.6
48.1
29.4
56.4
42.5
37.7
55.4
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
9.71
-
-
7.28
362
400
136
249
465
288
443
—
-
-
19.4
-
-
15.2
855
911
299
429
1,080
538
1,100
—
-
-
4.97
-
-
4.43
138
162
53.4
124
152
123
158
-
-
-
0.920
-
-
0.753
1.23
1.17
1.18
1.11
1.34
1.22
1.23
Potential Absorbed Dose in OH Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
119
102
17
38
68
62
57
45.6
48.1
29.4
56.4
42.5
37.7
55.4
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
0.018
-
-
0.013
0.641
0.712
0.215
0.418
0.837
0.553
0.737
-
-
-
0.038
-
-
0.030
1.57
1.67
0.459
0.717
1.99
1.12
1.95
-
-
-
0.008
-
-
0.007
0.238
0.280
0.090
0.207
0.266
0.217
0.263
-
-
-
1.01
-
-
0.839
1.25
1.19
1.16
1.11
1.37
1.27
1.23
Potential Absorbed Dose in OH Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
119
102
17
38
68
62
57
45.6
48.1
29.4
56.4
42.5
37.7
55.4
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
0.073
-
-
0.053
2.54
2.82
0.853
1.66
3.32
2.19
2.92
—
-
-
0.152
-
-
0.119
6.21
6.64
1.82
2.84
7.87
4.44
7.72
—
-
-
0.033
-
-
0.029
0.943
1.11
0.356
0.819
1.05
0.861
1.04
-
-
-
1.01
-
-
0.839
1.25
1.19
1.16
1.11
1.37
1.27
1.23
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      0-6

-------
Table O-2b.    Benzorfrlfluoranthene (205-99-2): Range of Potential Exposure and Potential
                 Absorbed Dose in OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
119
102
17
38
68
62
57

-------
Table O-3a.    Benzor/dfluoranthene (207-08-9):  Estimates of Potential Exposure and Potential
                 Absorbed Dose in OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
119
102
17
38
68
62
57
35.2
36.1
29.4
41.0
32.9
30.4
41.1
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
-
-
-
-
32.5
35.7
12.8
21.9
41.8
26.8
38.6
-
-
-
-
-
-
-
74.8
79.6
27.6
37.3
94.1
51.9
93.6
-
-
-
-
-
-
-
12.4
14.5
4.89
11.1
13.5
11.1
14.0
-
-
-
-
-
-
-
1.24
1.17
1.24
1.10
1.37
1.24
1.24
Potential Exposure in OH Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
119
102
17
38
68
62
57
35.2
36.1
29.4
41.0
32.9
30.4
41.1
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
-
-
-
-
129
142
50.7
86.6
166
106
153
—
-
-
-
-
-
-
296
315
109
148
373
206
371
—
-
-
-
-
-
-
49.2
57.5
19.4
44.0
53.6
44.2
55.3
-
-
-
-
-
-
-
1.24
1.17
1.24
1.10
1.37
1.24
1.24
Potential Absorbed Dose in OH Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
119
102
17
38
68
62
57
35.2
36.1
29.4
41.0
32.9
30.4
41.1
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
-
-
-
-
0.229
0.254
0.080
0.145
0.301
0.205
0.254
-
-
-
-
-
-
-
0.547
0.584
0.168
0.246
0.693
0.434
0.651
-
-
-
-
-
-
-
0.085
0.099
0.033
0.074
0.094
0.078
0.092
-
-
-
-
-
-
-
1.26
1.21
1.21
1.10
1.40
1.28
1.25
Potential Absorbed Dose in OH Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
119
102
17
38
68
62
57
35.2
36.1
29.4
41.0
32.9
30.4
41.1
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
-
-
-
-
0.907
1.01
0.318
0.575
1.19
0.814
1.01
—
-
-
-
-
-
-
2.17
2.31
0.666
0.977
2.75
1.72
2.58
—
-
-
-
-
-
-
0.335
0.393
0.129
0.292
0.372
0.310
0.364
-
-
-
-
-
-
-
1.26
1.21
1.21
1.10
1.40
1.28
1.25
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.

-------
Table O-3b.    Benzo|7(1fluoranthene (207-08-9): Range of Potential Exposure and Potential
                 Absorbed Dose in OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
119
102
17
38
68
62
57

-------
Table O-4a.    Benzorq/i/lperylene (191-24-2): Estimates of Potential Exposure and Potential
                 Absorbed Dose in OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
119
102
17
38
68
62
57
35.2
39.8
5.9
53.8
27.4
30.4
41.1
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
1.51
-
-
-
46.7
51.2
19.7
31.7
59.9
38.3
55.8
-
-
-
1.55
-
-
-
105
112
43.1
50.1
133
73.4
131
-
-
-
1.15
-
-
-
18.5
21.4
7.83
16.1
20.5
16.5
21.0
-
-
-
0.647
-
-
-
1.21
1.17
1.18
1.11
1.33
1.20
1.23
Potential Exposure in OH Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
119
102
17
38
68
62
57
35.2
39.8
5.9
53.8
27.4
30.4
41.1
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
5.46
-
-
-
169
185
71.2
115
217
139
202
—
-
-
5.62
-
-
-
380
404
156
181
480
266
475
—
-
-
4.15
-
-
-
67.0
77.4
28.3
58.4
74.1
59.7
76.0
-
-
-
0.647
-
-
-
1.21
1.17
1.18
1.11
1.33
1.20
1.23
Potential Absorbed Dose in OH Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
119
102
17
38
68
62
57
35.2
39.8
5.9
53.8
27.4
30.4
41.1
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
0.011
-
-
-
0.330
0.364
0.124
0.212
0.432
0.293
0.370
-
-
-
0.013
-
-
-
0.781
0.833
0.262
0.335
0.993
0.617
0.932
-
-
-
0.008
-
-
-
0.126
0.146
0.052
0.107
0.142
0.116
0.138
-
-
-
0.741
-
-
-
1.24
1.20
1.15
1.11
1.36
1.24
1.24
Potential Absorbed Dose in OH Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
119
102
17
38
68
62
57
35.2
39.8
5.9
53.8
27.4
30.4
41.1
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
0.040
-
-
-
1.19
1.32
0.448
0.767
1.56
1.06
1.34
—
-
-
0.046
-
-
-
2.83
3.01
0.950
1.21
3.59
2.23
3.37
—
-
-
0.028
-
-
-
0.457
0.529
0.189
0.387
0.514
0.420
0.500
-
-
-
0.741
-
-
-
1.24
1.20
1.15
1.11
1.36
1.24
1.24
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                     O-10

-------
Table O-4b.    Benzorq/i/lperylene (191-24-2): Range of Potential Exposure and Potential
                 Absorbed Dose in OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
119
102
17
38
68
62
57

-------
Table O-5a.    BenzoMpyrene (50-32-8):  Estimates of Potential Exposure and Potential
                 Absorbed Dose in OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
119
102
17
38
68
62
57
26.4
29.6
5.9
41.0
20.5
23.2
30.4
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
-
-
-
-
53.2
58.5
21.7
34.4
69.9
43.2
64.1
-
-
-
-
-
-
-
128
137
51.2
56.9
163
86.6
162
-
-
-
-
-
-
-
19.0
22.2
7.65
16.6
21.1
16.7
22.0
-
-
-
-
-
-
-
1.27
1.22
1.24
1.16
1.40
1.27
1.26
Potential Exposure in OH Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
119
102
17
38
68
62
57
26.4
29.6
5.9
41.0
20.5
23.2
30.4
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
-
-
-
-
211
232
86.1
136
277
171
254
—
-
-
-
-
-
-
509
542
203
226
646
343
644
—
-
-
-
-
-
-
75.5
87.9
30.3
65.9
83.6
66.0
87.4
-
-
-
-
-
-
-
1.27
1.22
1.24
1.16
1.40
1.27
1.26
Potential Absorbed Dose in OH Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
119
102
17
38
68
62
57
26.4
29.6
5.9
41.0
20.5
23.2
30.4
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
-
-
-
-
0.376
0.415
0.136
0.228
0.502
0.332
0.423
-
-
-
-
-
-
-
0.945
1.01
0.312
0.376
1.21
0.724
1.14
-
-
-
-
-
-
-
0.130
0.152
0.051
0.110
0.147
0.117
0.145
-
-
-
-
-
-
-
1.29
1.25
1.20
1.15
1.43
1.32
1.27
Potential Absorbed Dose in OH Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
119
102
17
38
68
62
57
26.4
29.6
5.9
41.0
20.5
23.2
30.4
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
-
-
-
-
1.49
1.65
0.538
0.903
1.99
1.32
1.68
—
-
-
-
-
-
-
3.74
3.99
1.24
1.49
4.78
2.87
4.53
—
-
-
-
-
-
-
0.514
0.601
0.202
0.437
0.581
0.464
0.575
-
-
-
-
-
-
-
1.29
1.25
1.20
1.15
1.43
1.32
1.27
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      O-12

-------
Table O-5b.    Benzolalpyrene (50-32-8):  Range of Potential Exposure and Potential Absorbed
                 Dose in OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
119
102
17
38
68
62
57

-------
Table O-6a.    Benzorelpyrene (192-97-2):  Estimates of Potential Exposure and Potential
                 Absorbed Dose in OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
119
102
17
38
68
62
57
35.2
39.8
5.9
48.7
30.1
30.4
41.1
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
-
-
-
-
48.9
53.8
19.2
33.0
62.9
39.9
58.7
-
-
-
-
-
-
-
113
120
42.3
56.0
143
76.3
143
-
-
-
-
-
-
-
19.0
22.1
111
16.8
20.9
17.0
21.5
-
-
-
-
-
-
-
1.21
1.16
1.14
1.08
1.33
1.20
1.22
Potential Exposure in OH Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
119
102
17
38
68
62
57
35.2
39.8
5.9
48.7
30.1
30.4
41.1
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
-
-
-
-
194
213
76.1
131
249
158
233
-
-
-
-
-
-
-
449
477
168
222
565
303
567
-
-
-
-
-
-
-
75.5
87.6
30.8
66.4
83.0
67.5
85.2
-
-
-
-
-
-
-
1.21
1.16
1.14
1.08
1.33
1.20
1.22
Potential Absorbed Dose in OH Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
119
102
17
38
68
62
57
35.2
39.8
5.9
48.7
30.1
30.4
41.1
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
-
-
-
-
0.345
0.382
0.121
0.220
0.453
0.305
0.389
-
-
-
-
-
-
-
0.835
0.891
0.258
0.371
1.06
0.636
1.01
-
-
-
-
-
-
-
0.130
0.151
0.052
0.111
0.145
0.120
0.142
-
-
-
-
-
-
-
1.23
1.19
1.11
1.08
1.37
1.24
1.23
Potential Absorbed Dose in OH Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
119
102
17
38
68
62
57
35.2
39.8
5.9
48.7
30.1
30.4
41.1
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
-
-
-
-
1.37
1.52
0.478
0.870
1.79
1.21
1.54
-
-
-
-
-
-
-
3.31
3.53
1.02
1.47
4.20
2.52
4.01
-
-
-
-
-
-
-
0.514
0.599
0.205
0.440
0.576
0.474
0.561
-
-
-
-
-
-
-
1.23
1.19
1.11
1.08
1.37
1.24
1.23
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                     O-14

-------
Table O-6b.    BenzoTelpyrene (192-97-2):  Range of Potential Exposure and Potential Absorbed
                 Dose in OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
119
102
17
38
68
62
57

-------
Table O-7a.    Benzylbutylphthalate (85-68-7):  Estimates of Potential Exposure and Potential
                 Absorbed Dose in OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
107
17
38
73
69
55
118
102
16
38
68
62
56
37.1
35.5
47.1
50.0
28.8
29.0
47.3
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
552
-
-
-
689
690
687
817
655
531
865
-
-
-
469
-
-
-
1,090
1,150
609
928
1,250
582
1,450
-
-
-
441
-
-
-
386
377
451
533
332
330
460
-
-
-
0.616
-
-
-
1.06
1.07
1.06
0.997
1.10
0.992
1.12
Potential Exposure in OH Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
107
17
38
73
69
55
118
102
16
38
68
62
56
37.1
35.5
47.1
50.0
28.8
29.0
47.3
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
1,770
-
-
-
2,210
2,210
2,200
2,620
2,100
1,700
2,770
-
-
-
1,500
-
-
-
3,490
3,680
1,950
2,970
3,990
1,860
4,630
-
-
-
1,410
-
-
-
1,240
1,210
1,440
1,710
1,060
1,060
1,470
-
-
-
0.616
-
-
-
1.06
1.07
1.06
0.997
1.10
0.992
1.12
Potential Absorbed Dose in OH Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
107
17
38
73
69
55
118
102
16
38
68
62
56
37.1
35.5
47.1
50.0
28.8
29.0
47.3
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
3.73
-
-
-
4.84
4.91
4.40
6.07
4.47
3.67
6.13
-
-
-
2.93
-
-
-
8.19
8.71
3.49
9.70
7.90
3.99
11.0
-
-
-
2.97
-
-
-
2.63
2.58
2.97
3.53
2.30
2.32
3.01
-
-
-
0.653
-
-
-
1.08
1.09
1.07
1.05
1.11
0.982
1.18
Potential Absorbed Dose in OH Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
107
17
38
73
69
55
118
102
16
38
68
62
56
37.1
35.5
47.1
50.0
28.8
29.0
47.3
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
12.0
-
-
-
15.5
15.7
14.1
19.4
14.3
11.8
19.6
-
-
-
9.38
-
-
-
26.2
27.9
11.2
31.1
25.3
12.8
35.3
-
-
-
9.51
-
-
-
8.41
8.25
9.50
11.3
7.36
7.42
9.65
-
-
-
0.653
-
-
-
1.08
1.09
1.07
1.05
1.11
0.982
1.18
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                     O-16

-------
Table O-7b.    Benzylbutylphthalate (85-68-7):  Range of Potential Exposure and Potential
                 Absorbed Dose in OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
107
17
38
73
69
55
118
102
16
38
68
62
56

-------
Table O-8a.    Bisphenol-A (80-05-7):  Estimates of Potential Exposure and Potential Absorbed
                 Dose in OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
101
85
16
32
59
59
42
115
99
16
37
66
60
55
72.3
74.1
62.5
81.3
67.8
71.2
73.8
47.8
46.5
56.3
62.2
40.9
55.0
40.0
17.6
17.7
16.8
26.0
14.0
14.7
21.7
-
-
1.17
0.818
-
1.30
-
19.7
18.8
24.5
30.9
10.1
15.5
24.0
-
-
1.55
0.460
-
1.75
-
13.3
13.6
11.9
16.8
12.0
11.7
15.9
-
-
0.717
0.713
-
0.897
-
0.635
0.634
0.649
0.841
0.511
0.564
0.690
-
-
0.896
0.524
-
0.758
-
Potential Exposure in OH Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
101
85
16
32
59
59
42
115
99
16
37
66
60
55
72.3
74.1
62.5
81.3
67.8
71.2
73.8
47.8
46.5
56.3
62.2
40.9
55.0
40.0
77.0
77.7
73.5
114
61.2
64.2
95.1
-
-
5.11
3.58
-
5.71
-
86.3
82.5
107
135
44.1
68.1
105
-
-
6.81
2.01
-
7.68
-
58.3
59.6
52.2
73.8
52.4
51.4
69.6
-
-
3.14
3.12
-
3.93
-
0.635
0.634
0.649
0.841
0.511
0.564
0.690
-
-
0.896
0.524
-
0.758
-
Potential Absorbed Dose in OH Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
101
85
16
32
59
59
42
115
99
16
37
66
60
55
72.3
74.1
62.5
81.3
67.8
71.2
73.8
47.8
46.5
56.3
62.2
40.9
55.0
40.0
0.122
0.121
0.126
0.184
0.094
0.104
0.146
-
-
0.007
0.006
-
0.009
-
0.140
0.122
0.218
0.220
0.070
0.127
0.156
-
-
0.008
0.004
-
0.011
-
0.090
0.092
0.080
0.114
0.081
0.082
0.102
-
-
0.005
0.005
-
0.006
-
0.671
0.658
0.748
0.923
0.506
0.573
0.778
-
-
0.876
0.588
-
0.758
-
Potential Absorbed Dose in OH Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
101
85
16
32
59
59
42
115
99
16
37
66
60
55
72.3
74.1
62.5
81.3
67.8
71.2
73.8
47.8
46.5
56.3
62.2
40.9
55.0
40.0
0.533
0.529
0.552
0.806
0.412
0.457
0.640
-
-
0.032
0.024
-
0.040
-
0.615
0.536
0.953
0.962
0.305
0.555
0.682
-
-
0.035
0.016
-
0.050
-
0.394
0.403
0.349
0.499
0.354
0.359
0.449
-
-
0.021
0.021
-
0.028
-
0.671
0.658
0.748
0.923
0.506
0.573
0.778
-
-
0.876
0.588
-
0.758
-
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected.  Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      O-18

-------
Table O-8b.    Bisphenol-A (80-05-7):  Range of Potential Exposure and Potential Absorbed Dose
                 in OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
101
85
16
32
59
59
42
115
99
16
37
66
60
55

-------
Table O-9a.    a/p/ia-Chlordane (5103-71-9):  Estimates of Potential Exposure and Potential
                 Absorbed Dose in OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
120
103
17
38
69
63
57
95.2
95.4
94.1
94.9
95.9
95.7
94.6
92.5
92.2
94.1
97.4
89.9
88.9
96.5
11.1
11.5
8.27
11.7
9.38
15.2
6.05
1.22
1.34
0.436
1.58
0.965
1.52
0.875
27.3
29.0
11.6
27.9
25.4
35.3
9.96
3.30
3.54
0.606
4.12
2.58
3.83
2.58
4.16
4.17
4.11
4.54
3.73
4.56
3.71
0.335
0.363
0.204
0.400
0.327
0.394
0.280
1.12
1.13
1.13
1.12
1.07
1.31
0.844
1.40
1.41
1.26
1.45
1.31
1.47
1.31
Potential Exposure in OH Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
120
103
17
38
69
63
57
95.2
95.4
94.1
94.9
95.9
95.7
94.6
92.5
92.2
94.1
97.4
89.9
88.9
96.5
27.1
28.2
20.2
28.6
22.9
37.1
14.8
2.97
3.28
1.06
3.86
2.36
3.72
2.13
66.7
70.9
28.4
68.1
62.1
86.1
24.3
8.04
8.63
1.48
10.1
6.30
9.34
6.30
10.1
10.2
10.0
11.1
9.11
11.1
9.05
0.817
0.887
0.498
0.976
0.798
0.961
0.684
1.12
1.13
1.13
1.12
1.07
1.31
0.844
1.40
1.41
1.26
1.45
1.31
1.47
1.31
Potential Absorbed Dose in OH Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
120
103
17
38
69
63
57
95.2
95.4
94.1
94.9
95.9
95.7
94.6
92.5
92.2
94.1
97.4
89.9
88.9
96.5
0.076
0.078
0.062
0.086
0.063
0.103
0.042
0.008
0.009
0.003
0.010
0.007
0.010
0.006
0.179
0.189
0.098
0.214
0.152
0.230
0.068
0.020
0.022
0.005
0.023
0.018
0.025
0.013
0.028
0.028
0.027
0.031
0.026
0.032
0.024
0.002
0.002
0.001
0.003
0.002
0.003
0.002
1.16
1.15
1.21
1.18
1.11
1.31
0.916
1.41
1.42
1.30
1.43
1.34
1.45
1.36
Potential Absorbed Dose in OH Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
120
103
17
38
69
63
57
95.2
95.4
94.1
94.9
95.9
95.7
94.6
92.5
92.2
94.1
97.4
89.9
88.9
96.5
0.185
0.190
0.152
0.210
0.154
0.252
0.102
0.019
0.021
0.008
0.023
0.017
0.025
0.014
0.437
0.461
0.239
0.521
0.372
0.561
0.166
0.049
0.053
0.012
0.057
0.044
0.061
0.031
0.069
0.069
0.067
0.074
0.063
0.078
0.060
0.006
0.006
0.003
0.006
0.006
0.007
0.005
1.16
1.15
1.21
1.18
1.11
1.31
0.916
1.41
1.42
1.30
1.43
1.34
1.45
1.36
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                     O-20

-------
Table O-9b.    a/p/ia-Chlordane (5103-71-9):  Range of Potential Exposure and Potential
                 Absorbed Dose in OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
120
103
17
38
69
63
57

-------
Table O-10a.   qa/n/na-Chlordane (5103-74-2): Estimates of Potential Exposure and Potential
                 Absorbed Dose in OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
120
103
17
38
69
63
57
98.4
98.1
100.0
97.4
98.6
98.6
98.2
91.7
91.3
94.1
97.4
88.4
87.3
96.5
17.8
18.9
10.9
17.3
16.8
25.3
8.57
1.37
1.51
0.512
1.73
1.16
1.73
0.973
57.9
62.0
14.4
45.0
65.8
76.4
13.6
3.80
4.08
0.705
4.53
3.37
4.40
2.99
5.78
5.80
5.62
6.32
5.17
6.23
5.26
0.356
0.383
0.228
0.432
0.345
0.415
0.300
1.16
1.17
1.13
1.13
1.13
1.36
0.852
1.43
1.44
1.32
1.47
1.36
1.52
1.33
Potential Exposure in OH Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
120
103
17
38
69
63
57
98.4
98.1
100.0
97.4
98.6
98.6
98.2
91.7
91.3
94.1
97.4
88.4
87.3
96.5
43.5
46.1
26.7
42.2
41.0
61.8
20.9
3.35
3.69
1.25
4.23
2.83
4.23
2.37
141
151
35.2
110
161
186
33.1
9.27
9.95
1.72
11.1
8.22
10.7
7.30
14.1
14.2
13.7
15.4
12.6
15.2
12.8
0.868
0.935
0.556
1.05
0.842
1.01
0.732
1.16
1.17
1.13
1.13
1.13
1.36
0.852
1.43
1.44
1.32
1.47
1.36
1.52
1.33
Potential Absorbed Dose in OH Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
120
103
17
38
69
63
57
98.4
98.1
100.0
97.4
98.6
98.6
98.2
91.7
91.3
94.1
97.4
88.4
87.3
96.5
0.120
0.126
0.082
0.127
0.110
0.169
0.060
0.009
0.010
0.004
0.010
0.008
0.011
0.006
0.361
0.385
0.121
0.347
0.384
0.474
0.094
0.023
0.024
0.006
0.025
0.022
0.028
0.014
0.039
0.040
0.037
0.043
0.036
0.044
0.035
0.002
0.003
0.002
0.003
0.002
0.003
0.002
1.19
1.19
1.20
1.19
1.17
1.37
0.921
1.44
1.44
1.36
1.44
1.39
1.49
1.36
Potential Absorbed Dose in OH Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
120
103
17
38
69
63
57
98.4
98.1
100.0
97.4
98.6
98.6
98.2
91.7
91.3
94.1
97.4
88.4
87.3
96.5
0.292
0.307
0.201
0.311
0.268
0.411
0.145
0.022
0.024
0.009
0.025
0.020
0.028
0.015
0.880
0.940
0.296
0.847
0.937
1.16
0.229
0.055
0.059
0.014
0.061
0.053
0.068
0.035
0.096
0.097
0.091
0.104
0.087
0.106
0.084
0.006
0.006
0.004
0.007
0.006
0.007
0.005
1.19
1.19
1.20
1.19
1.17
1.37
0.921
1.44
1.44
1.36
1.44
1.39
1.49
1.36
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                     O-22

-------
Table O-10b.   qa/n/na-Chlordane (5103-74-2): Range of Potential Exposure and Potential
                 Absorbed Dose in OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
120
103
17
38
69
63
57

-------
TableO-11a.   Chlorpyrifos (2921-88-2):  Estimates of Potential Exposure and Potential Absorbed
                 Dose in OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
110
93
17
33
66
60
50
120
103
17
38
69
63
57
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
44.3
48.2
23.0
48.7
32.4
49.7
37.8
20.5
23.5
2.28
49.2
3.08
9.20
33.0
86.1
92.9
16.7
72.6
37.9
111
38.3
120
129
5.59
204
5.57
46.7
167
23.7
24.8
18.3
27.3
20.5
21.3
26.9
1.66
1.84
0.864
3.02
1.32
1.49
1.86
0.991
1.03
0.701
1.02
0.920
1.13
0.788
1.63
1.68
1.14
2.00
1.22
1.46
1.81
Potential Exposure in OH Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
110
93
17
33
66
60
50
120
103
17
38
69
63
57
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
126
138
65.5
139
92.5
142
108
58.5
67.1
6.52
140
8.77
26.3
94.2
246
265
47.7
207
108
318
109
342
369
15.9
580
15.9
133
476
67.5
70.8
52.2
77.8
58.6
60.7
76.8
4.72
5.26
2.46
8.62
3.77
4.25
5.30
0.991
1.03
0.701
1.02
0.920
1.13
0.788
1.63
1.68
1.14
2.00
1.22
1.46
1.81
Potential Absorbed Dose in OH Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
110
93
17
33
66
60
50
120
103
17
38
69
63
57
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.318
0.348
0.157
0.339
0.234
0.364
0.263
0.136
0.156
0.016
0.309
0.023
0.070
0.209
0.656
0.708
0.120
0.488
0.291
0.857
0.257
0.794
0.856
0.042
1.32
0.041
0.367
1.09
0.159
0.167
0.122
0.180
0.139
0.148
0.173
0.011
0.013
0.006
0.020
0.009
0.010
0.012
1.05
1.10
0.724
1.10
0.978
1.15
0.918
1.67
1.72
1.15
1.99
1.29
1.48
1.87
Potential Absorbed Dose in OH Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
110
93
17
33
66
60
50
120
103
17
38
69
63
57
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.908
0.992
0.448
0.966
0.667
1.04
0.751
0.388
0.444
0.046
0.880
0.066
0.200
0.596
1.87
2.02
0.343
1.39
0.830
2.45
0.734
2.26
2.44
0.119
3.78
0.118
1.05
3.10
0.454
0.476
0.348
0.514
0.397
0.422
0.495
0.032
0.036
0.016
0.057
0.026
0.030
0.035
1.05
1.10
0.724
1.10
0.978
1.15
0.918
1.67
1.72
1.15
1.99
1.29
1.48
1.87
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                     O-24

-------
Table O-11b.   Chlorpyrifos (2921-88-2):  Range of Potential Exposure and Potential Absorbed
                 Dose in OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
110
93
17
33
66
60
50
120
103
17
38
69
63
57
1.86
1.86
5.03
5.74
1.86
1.86
6.71
0.090
0.090
0.218
0.090
0.159
0.169
0.090
12.2
12.2
12.4
12.3
11.6
9.95
14.8
0.553
0.562
0.438
0.604
0.562
0.528
0.554
19.8
19.8
16.5
24.3
18.2
16.5
23.8
1.18
1.22
0.663
2.58
1.10
1.18
1.22
42.4
48.6
31.4
55.8
35.2
37.3
48.3
3.67
4.02
1.60
5.84
3.23
3.55
3.70
131
170
67.5
212
111
179
122
32.9
32.9
23.8
433
14.5
20.2
39.5
768
768
67.5
383
187
768
212
1,200
1,200
23.8
1,200
33.7
371
1,200
Potential Exposure in OH Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
110
93
17
33
66
60
50
120
103
17
38
69
63
57
5.32
5.32
14.4
16.4
5.32
5.32
19.1
0.258
0.258
0.622
0.258
0.452
0.482
0.258
34.7
34.7
35.3
35.1
33.2
28.4
42.2
1.58
1.60
1.25
1.72
1.60
1.51
1.58
56.4
56.4
47.1
69.4
51.8
47.1
67.8
3.35
3.48
1.89
7.37
3.14
3.35
3.48
121
139
89.6
159
100
106
138
10.5
11.5
4.56
16.7
9.22
10.1
10.5
373
486
193
605
316
509
347
93.9
94.0
67.8
1,240
41.3
57.5
113
2,190
2,190
193
1,090
533
2,190
605
3,410
3,410
67.8
3,410
96.1
1,060
3,410
Potential Absorbed Dose in OH Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
110
93
17
33
66
60
50
120
103
17
38
69
63
57
0.018
0.018
0.038
0.025
0.018
0.018
0.025
0.001
0.001
0.001
0.001
0.001
0.001
0.001
0.077
0.079
0.069
0.080
0.069
0.068
0.095
0.004
0.004
0.003
0.004
0.004
0.004
0.004
0.128
0.129
0.107
0.138
0.119
0.118
0.136
0.008
0.009
0.005
0.017
0.007
0.008
0.007
0.300
0.323
0.198
0.430
0.264
0.273
0.351
0.025
0.027
0.009
0.043
0.023
0.024
0.026
0.965
1.00
0.422
0.965
0.842
1.36
0.832
0.198
0.218
0.177
1.91
0.127
0.137
0.435
6.04
6.04
0.422
2.60
1.42
6.04
0.965
8.03
8.03
0.177
8.03
0.218
2.92
8.03
Potential Absorbed Dose in OH Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
110
93
17
33
66
60
50
120
103
17
38
69
63
57
0.051
0.051
0.109
0.070
0.051
0.051
0.070
0.002
0.002
0.004
0.002
0.002
0.003
0.002
0.219
0.225
0.198
0.227
0.198
0.194
0.270
0.010
0.011
0.008
0.011
0.012
0.011
0.010
0.365
0.368
0.304
0.393
0.340
0.337
0.387
0.023
0.025
0.014
0.047
0.020
0.024
0.021
0.855
0.921
0.564
1.23
0.753
0.778
1.00
0.072
0.078
0.026
0.124
0.065
0.069
0.075
2.75
2.86
1.20
2.75
2.40
3.87
2.37
0.564
0.623
0.504
5.44
0.364
0.391
1.24
17.2
17.2
1.20
7.42
4.05
17.2
2.75
22.9
22.9
0.504
22.9
0.623
8.32
22.9
a  Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries."Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into
the body), divided by the subject's body weight.
                                                    O-25

-------
Table O-12a.   Chrysene (218-01-9):  Estimates of Potential Exposure and Potential Absorbed
                 Dose in OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
108
92
16
35
62
58
50
119
102
17
38
68
62
57
59.3
65.2
25.0
74.3
51.6
53.4
66.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
1.52
1.63
-
2.38
1.12
1.15
1.95
53.7
59.6
18.0
35.2
70.2
42.8
65.5
2.32
2.49
-
3.79
0.880
1.10
3.16
132
141
40.1
63.6
166
84.3
169
1.08
1.13
-
1.37
0.964
0.955
1.25
19.1
22.6
7.02
17.0
21.1
17.0
21.8
0.649
0.685
-
0.902
0.464
0.493
0.774
1.26
1.20
1.18
1.12
1.38
1.25
1.26
Potential Exposure in OH Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
108
92
16
35
62
58
50
119
102
17
38
68
62
57
59.3
65.2
25.0
74.3
51.6
53.4
66.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
6.64
7.16
-
10.4
4.89
5.02
8.52
235
261
78.8
154
308
187
287
10.2
10.9
-
16.6
3.86
4.81
13.8
577
616
176
279
728
369
740
4.73
4.97
-
6.00
4.22
4.18
5.46
83.8
99.0
30.8
74.5
92.6
74.4
95.3
0.649
0.685
-
0.902
0.464
0.493
0.774
1.26
1.20
1.18
1.12
1.38
1.25
1.26
Potential Absorbed Dose in OH Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
108
92
16
35
62
58
50
119
102
17
38
68
62
57
59.3
65.2
25.0
74.3
51.6
53.4
66.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.011
0.012
-
0.018
0.008
0.008
0.014
0.374
0.418
0.113
0.232
0.498
0.327
0.426
0.018
0.020
-
0.030
0.006
0.008
0.025
0.934
0.998
0.245
0.418
1.18
0.697
1.14
0.007
0.008
-
0.009
0.007
0.007
0.008
0.130
0.154
0.047
0.113
0.147
0.119
0.143
0.711
0.754
-
0.991
0.526
0.522
0.875
1.28
1.22
1.14
1.10
1.42
1.30
1.26
Potential Absorbed Dose in OH Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
108
92
16
35
62
58
50
119
102
17
38
68
62
57
59.3
65.2
25.0
74.3
51.6
53.4
66.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.048
0.051
-
0.077
0.034
0.035
0.062
1.64
1.83
0.494
1.02
2.18
1.43
1.87
0.080
0.086
-
0.131
0.028
0.035
0.109
4.09
4.37
1.07
1.83
5.18
3.05
5.00
0.032
0.033
-
0.040
0.029
0.029
0.036
0.571
0.677
0.205
0.494
0.643
0.523
0.628
0.711
0.754
-
0.991
0.526
0.522
0.875
1.28
1.22
1.14
1.10
1.42
1.30
1.26
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                     O-26

-------
Table O-12b.   Chrysene (218-01-9):  Range of Potential Exposure and Potential Absorbed Dose in
                 OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
108
92
16
35
62
58
50
119
102
17
38
68
62
57

-------
Table O-13a.   Cyfluthrin (68359-37-5): Estimates of Potential Exposure and Potential Absorbed
                 Dose in OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
123
106
17
39
71
67
56
119
103
16
38
69
63
56
1.6
1.9
0.0
2.6
1.4
0.0
3.6
79.8
82.5
62.5
86.8
79.7
82.5
76.8
-
-
-
-
-
-
-
7.63
8.47
2.26
7.53
8.11
7.67
7.59
-
-
-
-
-
-
-
11.3
11.9
2.96
7.59
13.6
11.1
11.6
-
-
-
-
-
-
-
3.47
4.05
1.28
4.27
3.26
3.65
3.28
-
-
-
-
-
-
-
1.34
1.31
1.06
1.23
1.38
1.28
1.41
Potential Exposure in OH Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
123
106
17
39
71
67
56
119
103
16
38
69
63
56
1.6
1.9
0.0
2.6
1.4
0.0
3.6
79.8
82.5
62.5
86.8
79.7
82.5
76.8
-
-
-
-
-
-
-
17.6
19.5
5.20
17.3
18.7
17.7
17.5
-
-
-
-
-
-
-
26.0
27.3
6.81
17.5
31.2
25.6
26.6
-
-
-
-
-
-
-
7.99
9.33
2.96
9.82
7.51
8.40
7.56
-
-
-
-
-
-
-
1.34
1.31
1.06
1.23
1.38
1.28
1.41
Potential Absorbed Dose in OH Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
123
106
17
39
71
67
56
119
103
16
38
69
63
56
1.6
1.9
0.0
2.6
1.4
0.0
3.6
79.8
82.5
62.5
86.8
79.7
82.5
76.8
-
-
-
-
-
-
-
0.051
0.056
0.016
0.049
0.054
0.055
0.046
-
-
-
-
-
-
-
0.078
0.082
0.020
0.052
0.094
0.090
0.061
-
-
-
-
-
-
-
0.024
0.028
0.008
0.028
0.023
0.026
0.022
-
-
-
-
-
-
-
1.32
1.28
1.14
1.22
1.35
1.30
1.36
Potential Absorbed Dose in OH Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
123
106
17
39
71
67
56
119
103
16
38
69
63
56
1.6
1.9
0.0
2.6
1.4
0.0
3.6
79.8
82.5
62.5
86.8
79.7
82.5
76.8
-
-
-
-
-
-
-
0.117
0.130
0.036
0.113
0.125
0.127
0.106
-
-
-
-
-
-
-
0.179
0.188
0.045
0.119
0.215
0.207
0.141
-
-
-
-
-
-
-
0.054
0.064
0.019
0.065
0.052
0.059
0.050
-
-
-
-
-
-
-
1.32
1.28
1.14
1.22
1.35
1.30
1.36
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected.  Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      O-28

-------
Table O-13b.   Cyfluthrin (68359-37-5): Range of Potential Exposure and Potential Absorbed Dose
                 in OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
123
106
17
39
71
67
56
119
103
16
38
69
63
56

-------
Table O-14a.   Diazinon (333-41-5): Estimates of Potential Exposure and Potential Absorbed Dose
                 in OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
120
103
17
38
69
63
57
99.2
99.1
100.0
100.0
98.6
98.6
100.0
97.5
97.1
100.0
97.4
98.6
98.4
96.5
78.0
88.2
13.1
93.6
42.0
82.3
72.7
31.5
36.7
0.437
17.0
19.4
48.9
12.4
274
294
5.75
228
183
326
195
192
207
0.412
80.8
136
257
66.2
15.4
16.1
11.6
20.9
11.3
13.8
17.7
0.806
0.946
0.307
1.14
0.643
0.769
0.850
1.33
1.41
0.565
1.45
1.09
1.36
1.30
1.97
2.06
0.859
1.90
1.78
2.08
1.86
Potential Exposure in OH Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
120
103
17
38
69
63
57
99.2
99.1
100.0
100.0
98.6
98.6
100.0
97.5
97.1
100.0
97.4
98.6
98.4
96.5
256
290
43.1
308
138
271
239
104
120
1.44
55.8
63.6
161
40.6
901
965
18.9
749
601
1,070
642
631
680
1.35
266
447
845
217
50.7
53.0
38.2
68.5
37.2
45.4
58.1
2.65
3.11
1.01
3.75
2.11
2.53
2.79
1.33
1.41
0.565
1.45
1.09
1.36
1.30
1.97
2.06
0.859
1.90
1.78
2.08
1.86
Potential Absorbed Dose in OH Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
120
103
17
38
69
63
57
99.2
99.1
100.0
100.0
98.6
98.6
100.0
97.5
97.1
100.0
97.4
98.6
98.4
96.5
0.544
0.616
0.089
0.629
0.278
0.577
0.503
0.224
0.260
0.003
0.087
0.136
0.366
0.067
1.97
2.11
0.046
1.51
1.12
2.38
1.32
1.44
1.55
0.003
0.360
0.960
1.96
0.296
0.105
0.110
0.078
0.140
0.078
0.097
0.116
0.005
0.006
0.002
0.008
0.004
0.005
0.006
1.36
1.44
0.573
1.50
1.10
1.35
1.37
1.98
2.07
0.822
1.88
1.80
2.06
1.90
Potential Absorbed Dose in OH Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
120
103
17
38
69
63
57
99.2
99.1
100.0
100.0
98.6
98.6
100.0
97.5
97.1
100.0
97.4
98.6
98.4
96.5
1.79
2.02
0.292
2.07
0.914
1.90
1.65
0.735
0.855
0.009
0.284
0.448
1.20
0.219
6.48
6.95
0.150
4.97
3.67
7.83
4.34
4.73
5.10
0.008
1.18
3.16
6.45
0.974
0.345
0.362
0.255
0.461
0.256
0.318
0.382
0.018
0.021
0.007
0.025
0.015
0.018
0.018
1.36
1.44
0.573
1.50
1.10
1.35
1.37
1.98
2.07
0.822
1.88
1.80
2.06
1.90
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      O-30

-------
Table O-14b.   Diazinon (333-41-5): Range of Potential Exposure and Potential Absorbed Dose in
                 OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
120
103
17
38
69
63
57

-------
Table O-15a.   Dibenzora./ilanthracene (53-70-3):  Estimates of Potential Exposure and Potential
                 Absorbed Dose in OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
119
102
17
38
68
62
57
0.8
0.9
0.0
2.6
0.0
0.0
1.8
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
-
-
-
-
9.82
10.7
4.47
6.71
12.6
8.09
11.7
-
-
-
-
-
-
-
21.4
22.6
10.4
9.38
27.1
15.1
26.6
-
-
-
-
-
-
-
3.93
4.60
1.55
3.55
4.27
3.44
4.56
-
-
-
-
-
-
-
1.24
1.16
1.30
1.11
1.37
1.24
1.22
Potential Exposure in OH Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
119
102
17
38
68
62
57
0.8
0.9
0.0
2.6
0.0
0.0
1.8
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
-
-
-
-
35.3
38.5
16.1
24.1
45.2
29.1
42.0
-
-
-
-
-
-
-
76.8
81.2
37.4
33.7
97.4
54.2
95.5
-
-
-
-
-
-
-
14.1
16.5
5.57
12.8
15.3
12.3
16.4
-
-
-
-
-
-
-
1.24
1.16
1.30
1.11
1.37
1.24
1.22
Potential Absorbed Dose in OH Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
119
102
17
38
68
62
57
0.8
0.9
0.0
2.6
0.0
0.0
1.8
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
-
-
-
-
0.069
0.076
0.028
0.045
0.090
0.062
0.077
-
-
-
-
-
-
-
0.157
0.167
0.063
0.063
0.200
0.126
0.186
-
-
-
-
-
-
-
0.027
0.031
0.010
0.024
0.030
0.024
0.030
-
-
-
-
-
-
-
1.26
1.19
1.26
1.10
1.40
1.28
1.23
Potential Absorbed Dose in OH Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
119
102
17
38
68
62
57
0.8
0.9
0.0
2.6
0.0
0.0
1.8
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
-
-
-
-
0.248
0.272
0.101
0.161
0.323
0.222
0.276
-
-
-
-
-
-
-
0.564
0.599
0.228
0.227
0.719
0.454
0.667
-
-
-
-
-
-
-
0.096
0.113
0.037
0.085
0.106
0.087
0.108
-
-
-
-
-
-
-
1.26
1.19
1.26
1.10
1.40
1.28
1.23
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                     O-32

-------
Table O-15b.   Dibenzora./ilanthracene (53-70-3):  Range of Potential Exposure and Potential
                 Absorbed Dose in OH Adults. Summarized  by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
119
102
17
38
68
62
57

-------
Table O-16a.   Di-n-butylphthalate (84-74-2):  Estimates of Potential Exposure and Potential
                 Absorbed Dose in OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
107
17
38
73
69
55
116
100
16
38
66
61
55
97.6
97.2
100.0
92.1
100.0
100.0
94.5
100.0
100.0
100.0
100.0
100.0
100.0
100.0
2,890
2,800
3,500
2,950
2,750
2,750
3,070
165
173
109
176
155
169
160
1,370
1,350
1,390
1,580
1,170
1,310
1,440
136
140
85.4
126
145
129
144
2,570
2,480
3,260
2,570
2,480
2,420
2,790
127
136
86.4
137
120
130
125
0.508
0.517
0.380
0.546
0.484
0.550
0.442
0.716
0.703
0.698
0.751
0.689
0.750
0.683
Potential Exposure in OH Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
107
17
38
73
69
55
116
100
16
38
66
61
55
97.6
97.2
100.0
92.1
100.0
100.0
94.5
100.0
100.0
100.0
100.0
100.0
100.0
100.0
10,400
10,000
12,600
10,600
9,890
9,890
1 1 ,000
591
623
393
633
558
606
575
4,930
4,850
4,990
5,670
4,220
4,690
5,190
488
504
307
454
520
462
518
9,250
8,900
11,700
9,230
8,920
8,680
10,000
458
487
310
493
431
466
450
0.508
0.517
0.380
0.546
0.484
0.550
0.442
0.716
0.703
0.698
0.751
0.689
0.750
0.683
Potential Absorbed Dose in OH Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
107
17
38
73
69
55
116
100
16
38
66
61
55
97.6
97.2
100.0
92.1
100.0
100.0
94.5
100.0
100.0
100.0
100.0
100.0
100.0
100.0
20.4
19.8
23.9
21.3
19.4
19.5
21.5
1.17
1.24
0.734
1.24
1.12
1.22
1.12
11.5
11.6
10.6
15.3
9.20
9.50
13.6
1.03
1.07
0.641
1.06
1.04
1.04
1.02
17.5
16.9
21.8
17.3
17.1
16.9
18.3
0.872
0.933
0.569
0.910
0.843
0.914
0.827
0.575
0.588
0.443
0.677
0.534
0.578
0.573
0.764
0.753
0.711
0.805
0.728
0.762
0.769
Potential Absorbed Dose in OH Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
107
17
38
73
69
55
116
100
16
38
66
61
55
97.6
97.2
100.0
92.1
100.0
100.0
94.5
100.0
100.0
100.0
100.0
100.0
100.0
100.0
73.2
71.2
85.8
76.4
69.7
70.1
77.1
4.20
4.45
2.64
4.45
4.01
4.38
4.01
41.2
41.5
38.1
54.9
33.1
34.1
48.8
3.71
3.83
2.30
3.82
3.75
3.75
3.68
63.0
60.9
78.3
62.1
61.4
60.8
65.9
3.13
3.35
2.04
3.27
3.03
3.29
2.97
0.575
0.588
0.443
0.677
0.534
0.578
0.573
0.764
0.753
0.711
0.805
0.728
0.762
0.769
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected.  Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      O-34

-------
Table O-16b.   Di-n-butylphthalate (84-74-2):  Range of Potential Exposure and Potential Absorbed
                 Dose in OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
124
107
17
38
73
69
55
116
100
16
38
66
61
55

-------
Table O-17a.   p.p'-DDE (72-55-9):  Estimates of Potential Exposure and Potential Absorbed Dose
                 in OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
120
103
17
38
69
63
57
36.0
36.1
35.3
41.0
37.0
36.2
35.7
63.3
62.1
70.6
68.4
63.8
63.5
63.2
-
-
-
-
-
-
-
0.340
0.370
0.153
0.378
0.269
0.379
0.295
-
-
-
-
-
-
-
0.542
0.577
0.141
0.412
0.309
0.660
0.374
-
-
-
-
-
-
-
0.165
0.178
0.104
0.198
0.157
0.181
0.149
-
-
-
-
-
-
-
1.19
1.22
0.918
1.25
1.05
1.19
1.20
Potential Exposure in OH Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
120
103
17
38
69
63
57
36.0
36.1
35.3
41.0
37.0
36.2
35.7
63.3
62.1
70.6
68.4
63.8
63.5
63.2
-
-
-
-
-
-
-
1.07
1.16
0.480
1.19
0.846
1.19
0.929
-
-
-
-
-
-
-
1.71
1.82
0.442
1.30
0.971
2.07
1.18
-
-
-
-
-
-
-
0.519
0.560
0.326
0.621
0.494
0.570
0.467
-
-
-
-
-
-
-
1.19
1.22
0.918
1.25
1.05
1.19
1.20
Potential Absorbed Dose in OH Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
120
103
17
38
69
63
57
36.0
36.1
35.3
41.0
37.0
36.2
35.7
63.3
62.1
70.6
68.4
63.8
63.5
63.2
-
-
-
-
-
-
-
0.002
0.002
0.001
0.002
0.002
0.003
0.002
-
-
-
-
-
-
-
0.003
0.004
0.001
0.002
0.002
0.004
0.002
-
-
-
-
-
-
-
0.001
0.001
0.001
0.001
0.001
0.001
0.001
-
-
-
-
-
-
-
1.19
1.21
0.980
1.19
1.09
1.16
1.22
Potential Absorbed Dose in OH Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
120
103
17
38
69
63
57
36.0
36.1
35.3
41.0
37.0
36.2
35.7
63.3
62.1
70.6
68.4
63.8
63.5
63.2
-
-
-
-
-
-
-
0.007
0.008
0.003
0.007
0.006
0.008
0.006
-
-
-
-
-
-
-
0.011
0.011
0.003
0.007
0.008
0.013
0.007
-
-
-
-
-
-
-
0.004
0.004
0.002
0.004
0.003
0.004
0.003
-
-
-
-
-
-
-
1.19
1.21
0.980
1.19
1.09
1.16
1.22
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected.  Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      O-36

-------
Table O-17b.   p.p'-DDE (72-55-9): Range of Potential Exposure and Potential Absorbed Dose in
                 OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
120
103
17
38
69
63
57

-------
Table O-18a.   2.4-D (2.4-dichlorophenoxyacetic acid) (94-75-7):  Estimates of Potential Exposure
                 in OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Potential Exposure
-Aggregated
(ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
112
99
13
36
67
63
49
127
110
17
41
73
69
58
119
103
16
38
68
62
57
106
94
12
34
63
58
48
65.2
64.6
69.2
52.8
68.7
66.7
63.3
48.0
48.2
47.1
48.8
45.2
49.3
46.6
95.8
95.1
100.0
89.5
98.5
98.4
93.0
99.1
98.9
100.0
97.1
100.0
98.3
100.0
4.01
3.82
5.45
2.79
4.55
5.08
2.63
-
-
-
-
-
-
-
13.7
14.9
5.69
2.67
19.9
17.1
10.0
278
288
201
185
331
370
167
4.07
3.94
4.92
2.52
4.38
4.65
2.65
-
-
-
-
-
-
-
50.4
54.0
10.3
4.16
65.7
67.2
20.3
393
413
167
217
476
487
187
2.79
2.69
3.66
2.18
3.13
3.49
2.09
-
-
-
-
-
-
-
3.16
3.39
2.03
1.26
4.89
3.82
2.58
166
167
153
122
189
225
115
0.791
0.766
0.949
0.635
0.831
0.862
0.580
-
-
-
-
-
-
-
1.65
1.68
1.42
1.41
1.59
1.60
1.70
0.935
0.958
0.759
0.890
0.951
0.908
0.835
Potential Exposure in OH Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Potential Exposure
-Aggregated
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
112
99
13
36
67
63
49
127
110
17
41
73
69
58
119
103
16
38
68
62
57
106
94
12
34
63
58
48
65.2
64.6
69.2
52.8
68.7
66.7
63.3
48.0
48.2
47.1
48.8
45.2
49.3
46.6
95.8
95.1
100.0
89.5
98.5
98.4
93.0
99.1
98.9
100.0
97.1
100.0
98.3
100.0
18.1
17.3
24.6
12.6
20.6
23.0
11.9
-
-
-
-
-
-
-
61.9
67.5
25.7
12.1
90.1
77.1
45.3
1,260
1,300
910
838
1,500
1,670
756
18.4
17.8
22.2
11.4
19.8
21.0
12.0
-
-
-
-
-
-
-
228
244
46.8
18.8
297
304
91.9
1,780
1,870
757
981
2,150
2,200
844
12.6
12.2
16.6
9.87
14.2
15.8
9.44
-
-
-
-
-
-
-
14.3
15.3
9.18
5.72
22.1
17.3
11.7
750
757
693
550
857
1,020
518
0.791
0.766
0.949
0.635
0.831
0.862
0.580
-
-
-
-
-
-
-
1.65
1.68
1.42
1.41
1.59
1.60
1.70
0.935
0.958
0.759
0.890
0.951
0.908
0.835
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                    O-38

-------
Table O-18b.   2.4-D (2.4-dichlorophenoxyacetic acid) (94-75-7):  Range of Potential Exposure in
                OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Potential Exposure
- Aggregated
(ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
112
99
13
36
67
63
49
127
110
17
41
73
69
58
119
103
16
38
68
62
57
106
94
12
34
63
58
48

-------
Table O-18c.   2.4-D (2.4-dichlorophenoxyacetic acid) (94-75-7):  Estimates of Potential Absorbed
                 Dose in OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in OH Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Potential Absorbed
Dose - Aggregated
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
112
99
13
36
67
63
49
127
110
17
41
73
69
58
119
103
16
38
68
62
57
106
94
12
34
63
58
48
65.2
64.6
69.2
52.8
68.7
66.7
63.3
48.0
48.2
47.1
48.8
45.2
49.3
46.6
95.8
95.1
100.0
89.5
98.5
98.4
93.0
99.1
98.9
100.0
97.1
100.0
98.3
100.0
0.028
0.027
0.036
0.019
0.033
0.036
0.018
-
-
-
-
-
-
-
0.098
0.107
0.037
0.018
0.145
0.122
0.072
1.97
2.04
1.42
1.25
2.41
2.69
1.10
0.031
0.030
0.035
0.023
0.034
0.035
0.021
-
-
-
-
-
-
-
0.368
0.394
0.065
0.028
0.479
0.486
0.160
2.96
3.11
1.27
1.60
3.58
3.65
1.40
0.019
0.018
0.025
0.014
0.021
0.024
0.013
-
-
-
-
-
-
-
0.022
0.023
0.014
0.008
0.034
0.027
0.017
1.12
1.13
1.03
0.793
1.31
1.59
0.732
0.848
0.838
0.912
0.661
0.905
0.887
0.661
-
-
-
-
-
-
-
1.68
1.71
1.42
1.42
1.62
1.62
1.73
0.975
0.997
0.813
0.915
1.00
0.942
0.844
Potential Absorbed Dose in OH Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose - Aggregated
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
112
99
13
36
67
63
49
127
110
17
41
73
69
58
119
103
16
38
68
62
57
106
94
12
34
63
58
48
65.2
64.6
69.2
52.8
68.7
66.7
63.3
48.0
48.2
47.1
48.8
45.2
49.3
46.6
95.8
95.1
100.0
89.5
98.5
98.4
93.0
99.1
98.9
100.0
97.1
100.0
98.3
100.0
0.128
0.123
0.164
0.087
0.149
0.164
0.081
-
-
-
-
-
-
-
0.443
0.486
0.167
0.084
0.656
0.551
0.325
8.93
9.25
6.40
5.67
10.9
12.2
4.98
0.140
0.138
0.158
0.102
0.153
0.159
0.093
-
-
-
-
-
-
-
1.66
1.78
0.292
0.128
2.17
2.20
0.723
13.4
14.1
5.73
7.25
16.2
16.5
6.33
0.085
0.082
0.111
0.064
0.097
0.110
0.060
-
-
-
-
-
-
-
0.098
0.105
0.061
0.038
0.154
0.122
0.077
5.06
5.11
4.68
3.59
5.93
7.18
3.31
0.848
0.838
0.912
0.661
0.905
0.887
0.661
-
-
-
-
-
-
-
1.68
1.71
1.42
1.42
1.62
1.62
1.73
0.975
0.997
0.813
0.915
1.00
0.942
0.844
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      O-40

-------
Table O-18d.   2.4-D (2.4-dichlorophenoxyacetic acid) (94-75-7): Range of Potential Absorbed
                 Dose in OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in OH Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Potential Absorbed
Dose - Aggregated
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
112
99
13
36
67
63
49
127
110
17
41
73
69
58
119
103
16
38
68
62
57
106
94
12
34
63
58
48

-------
Table O-19a.   lndenori.2.3-cc/|pvrene (193-39-5): Estimates of Potential Exposure and Potential
                 Absorbed Dose in OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
119
102
17
38
68
62
57
26.4
29.6
5.9
43.6
20.5
20.3
33.9
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
-
-
-
-
48.8
53.7
19.6
33.0
62.8
39.8
58.6
-
-
-
-
-
-
-
114
121
43.8
54.5
144
78.8
142
-
-
-
-
-
-
-
18.2
21.2
7.47
16.0
20.1
16.3
20.7
-
-
-
-
-
-
-
1.25
1.20
1.20
1.15
1.37
1.23
1.27
Potential Exposure in OH Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
119
102
17
38
68
62
57
26.4
29.6
5.9
43.6
20.5
20.3
33.9
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
-
-
-
-
177
194
70.8
119
227
144
212
-
-
-
-
-
-
-
411
438
159
197
520
285
516
-
-
-
-
-
-
-
66.0
76.6
27.0
57.7
72.6
58.9
74.8
-
-
-
-
-
-
-
1.25
1.20
1.20
1.15
1.37
1.23
1.27
Potential Absorbed Dose in OH Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
119
102
17
38
68
62
57
26.4
29.6
5.9
43.6
20.5
20.3
33.9
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
-
-
-
-
0.344
0.381
0.123
0.220
0.452
0.305
0.387
-
-
-
-
-
-
-
0.840
0.897
0.267
0.363
1.07
0.660
1.01
-
-
-
-
-
-
-
0.124
0.145
0.050
0.106
0.139
0.114
0.136
-
-
-
-
-
-
-
1.28
1.24
1.17
1.14
1.40
1.28
1.28
Potential Absorbed Dose in OH Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
119
102
17
38
68
62
57
26.4
29.6
5.9
43.6
20.5
20.3
33.9
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
-
-
-
-
1.25
1.38
0.444
0.796
1.64
1.10
1.40
-
-
-
-
-
-
-
3.04
3.24
0.966
1.31
3.87
2.39
3.64
-
-
-
-
-
-
-
0.450
0.524
0.180
0.383
0.504
0.414
0.492
-
-
-
-
-
-
-
1.28
1.24
1.17
1.14
1.40
1.28
1.28
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                     O-42

-------
Table O-19b.   lndenori.2.3-cc/|pvrene (193-39-5):  Range of Potential Exposure and Potential
                 Absorbed Dose in OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
119
102
17
38
68
62
57

-------
Table O-20a.   Pentachlorophenol (87-86-5):  Estimates of Potential Exposure in OH Adults.
                 Summarized by Exposure Pathway and  Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
102
87
15
32
62
54
48
127
110
17
41
73
69
58
119
103
16
38
68
62
57
92.2
92.0
93.3
90.6
91.9
96.3
87.5
29.1
32.7
5.9
26.8
27.4
24.6
34.5
95.8
95.1
100.0
97.4
95.6
96.8
94.7
50.0
48.5
58.7
28.8
59.0
69.3
28.3
-
-
-
-
-
-
-
2.59
2.69
1.96
2.36
2.12
2.98
2.16
86.8
85.0
99.6
26.7
106
114
25.2
-
-
-
-
-
-
-
4.78
5.10
1.62
2.64
1.93
6.33
2.03
27.4
26.3
35.0
21.9
29.1
33.4
22.0
-
-
-
-
-
-
-
1.40
1.40
1.42
1.43
1.37
1.49
1.31
0.988
1.01
0.861
0.685
1.11
1.18
0.660
-
-
-
-
-
-
-
1.09
1.13
0.842
1.06
0.991
1.07
1.12
Potential Exposure in OH Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
102
87
15
32
62
54
48
127
110
17
41
73
69
58
119
103
16
38
68
62
57
92.2
92.0
93.3
90.6
91.9
96.3
87.5
29.1
32.7
5.9
26.8
27.4
24.6
34.5
95.8
95.1
100.0
97.4
95.6
96.8
94.7
188
182
220
108
222
260
106
-
-
-
-
-
-
-
9.72
10.1
7.35
8.85
7.97
11.2
8.11
326
319
374
100
398
428
94.6
-
-
-
-
-
-
-
18.0
19.1
6.07
9.91
7.25
23.8
7.61
103
98.7
131
82.3
109
125
82.4
-
-
-
-
-
-
-
5.26
5.25
5.35
5.36
5.16
5.60
4.91
0.988
1.01
0.861
0.685
1.11
1.18
0.660
-
-
-
-
-
-
-
1.09
1.13
0.842
1.06
0.991
1.07
1.12
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                    O-44

-------
Table O-20b.   Pentachlorophenol (87-86-5):  Range of Potential Exposure in OH Adults.
                Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
102
87
15
32
62
54
48
127
110
17
41
73
69
58
119
103
16
38
68
62
57

-------
Table O-20c.   Pentachlorophenol (87-86-5):  Estimates of Potential Absorbed Dose in OH Adults.
                 Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in OH Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
102
87
15
32
62
54
48
127
110
17
41
73
69
58
119
103
16
38
68
62
57
92.2
92.0
93.3
90.6
91.9
96.3
87.5
29.1
32.7
5.9
26.8
27.4
24.6
34.5
95.8
95.1
100.0
97.4
95.6
96.8
94.7
0.374
0.366
0.419
0.209
0.453
0.531
0.198
-
-
-
-
-
-
-
0.019
0.020
0.014
0.018
0.015
0.022
0.015
Potential Absorbed Dose in OH Adults (pmo
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
102
87
15
32
62
54
48
127
110
17
41
73
69
58
119
103
16
38
68
62
57
92.2
92.0
93.3
90.6
91.9
96.3
87.5
29.1
32.7
5.9
26.8
27.4
24.6
34.5
95.8
95.1
100.0
97.4
95.6
96.8
94.7
1.40
1.38
1.57
0.785
1.70
1.99
0.744
-
-
-
-
-
-
-
0.071
0.074
0.053
0.066
0.057
0.084
0.058
0.807
0.823
0.736
0.240
1.00
1.07
0.201
-
-
-
-
-
-
-
0.038
0.041
0.013
0.025
0.014
0.050
0.017
0.184
0.176
0.235
0.140
0.201
0.233
0.141
-
-
-
-
-
-
-
0.010
0.010
0.010
0.009
0.010
0.011
0.009
1.06
1.08
0.929
0.843
1.16
1.21
0.786
-
-
-
-
-
-
-
1.15
1.19
0.917
1.13
1.04
1.10
1.21
es/kg/day)
3.03
3.09
2.76
0.901
3.77
4.03
0.753
-
-
-
-
-
-
-
0.143
0.153
0.049
0.094
0.054
0.189
0.063
0.691
0.663
0.884
0.524
0.753
0.876
0.530
-
-
-
-
-
-
-
0.036
0.036
0.036
0.036
0.036
0.039
0.032
1.06
1.08
0.929
0.843
1.16
1.21
0.786
-
-
-
-
-
-
-
1.15
1.19
0.917
1.13
1.04
1.10
1.21
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      O-46

-------
Table O-20d.   Pentachlorophenol (87-86-5):  Range of Potential Absorbed Dose in OH Adults.
                 Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in OH Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
F
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
102
87
15
32
62
54
48
127
110
17
41
73
69
58
119
103
16
38
68
62
57
otentia
102
87
15
32
62
54
48
127
110
17
41
73
69
58
119
103
16
38
68
62
57

-------
Table O-21a.   c/s-Permethrin (61949-76-6):  Estimates of Potential Exposure and Potential
                 Absorbed Dose in OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
120
103
17
38
69
63
57
36.0
31.5
64.7
41.0
31.5
31.9
41.1
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
4.83
-
-
-
-
54.4
39.0
148
59.3
29.7
30.7
80.7
-
-
3.39
-
-
-
-
190
93.8
450
126
68.0
71.0
265
-
-
4.19
-
-
-
-
13.4
12.2
23.9
15.8
11.4
11.9
15.3
-
-
0.481
-
-
-
-
1.47
1.42
1.66
1.64
1.27
1.24
1.68
Potential Exposure in OH Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
120
103
17
38
69
63
57
36.0
31.5
64.7
41.0
31.5
31.9
41.1
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
12.3
-
-
-
-
139
99.7
378
152
75.8
78.5
206
-
-
8.67
-
-
-
-
486
240
1,150
321
174
182
676
-
-
10.7
-
-
-
-
34.2
31.1
61.0
40.3
29.1
30.3
39.1
-
-
0.481
-
-
-
-
1.47
1.42
1.66
1.64
1.27
1.24
1.68
Potential Absorbed Dose in OH Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
120
103
17
38
69
63
57
36.0
31.5
64.7
41.0
31.5
31.9
41.1
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
0.032
-
-
-
-
0.426
0.303
1.17
0.466
0.226
0.232
0.641
-
-
0.021
-
-
-
-
1.62
0.873
3.73
1.19
0.606
0.628
2.24
-
-
0.028
-
-
-
-
0.091
0.083
0.159
0.104
0.079
0.083
0.101
-
-
0.491
-
-
-
-
1.49
1.44
1.72
1.68
1.28
1.25
1.73
Potential Absorbed Dose in OH Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
120
103
17
38
69
63
57
36.0
31.5
64.7
41.0
31.5
31.9
41.1
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
0.082
-
-
-
-
1.09
0.774
3.00
1.19
0.577
0.592
1.64
-
-
0.052
-
-
-
-
4.13
2.23
9.54
3.05
1.55
1.60
5.73
-
-
0.071
-
-
-
-
0.233
0.212
0.407
0.267
0.202
0.213
0.257
-
-
0.491
-
-
-
-
1.49
1.44
1.72
1.68
1.28
1.25
1.73
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                     O-48

-------
Table O-21b.   c/s-Permethrin (61949-76-6): Range of Potential Exposure and Potential Absorbed
                 Dose in OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
120
103
17
38
69
63
57

-------
Table O-22a.   frans-Permethrin (61949-77-7):  Estimates of Potential Exposure and Potential
                 Absorbed Dose in OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
115
98
17
37
65
60
55
31.2
28.7
47.1
38.5
27.4
24.6
39.3
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
-
-
-
-
55.8
40.3
145
58.2
31.7
32.3
81.3
-
-
-
-
-
-
-
199
109
447
130
92.7
96.2
268
-
-
-
-
-
-
-
10.6
9.57
18.5
12.7
8.82
9.33
12.1
-
-
-
-
-
-
-
1.61
1.57
1.80
1.73
1.45
1.38
1.84
Potential Exposure in OH Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
115
98
17
37
65
60
55
31.2
28.7
47.1
38.5
27.4
24.6
39.3
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
-
-
-
-
143
103
371
149
80.9
82.6
208
-
-
-
-
-
-
-
508
278
1,140
333
237
246
685
-
-
-
-
-
-
-
27.0
24.5
47.4
32.4
22.5
23.8
30.9
-
-
-
-
-
-
-
1.61
1.57
1.80
1.73
1.45
1.38
1.84
Potential Absorbed Dose in OH Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
115
98
17
37
65
60
55
31.2
28.7
47.1
38.5
27.4
24.6
39.3
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
-
-
-
-
0.437
0.313
1.15
0.454
0.244
0.248
0.643
-
-
-
-
-
-
-
1.69
1.000
3.70
1.21
0.835
0.865
2.27
-
-
-
-
-
-
-
0.072
0.066
0.124
0.083
0.062
0.066
0.080
-
-
-
-
-
-
-
1.63
1.57
1.87
1.76
1.44
1.37
1.88
Potential Absorbed Dose in OH Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
115
98
17
37
65
60
55
31.2
28.7
47.1
38.5
27.4
24.6
39.3
100.0
100.0
100.0
100.0
100.0
100.0
100.0
-
-
-
-
-
-
-
1.12
0.799
2.95
1.16
0.624
0.635
1.64
-
-
-
-
-
-
-
4.32
2.56
9.46
3.10
2.13
2.21
5.80
-
-
-
-
-
-
-
0.184
0.168
0.316
0.213
0.158
0.168
0.203
-
-
-
-
-
-
-
1.63
1.57
1.87
1.76
1.44
1.37
1.88
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                     O-50

-------
Table O-22b.   frans-Permethrin (61949-77-7):  Range of Potential Exposure and Potential
                 Absorbed Dose in OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
115
98
17
37
65
60
55

-------
Table O-23a.   PCB 52 (35693-99-3): Estimates of Potential Exposure and Potential Absorbed
                 Dose in OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
123
106
17
37
73
69
54
119
102
17
38
68
63
56
95.9
95.3
100.0
97.3
94.5
94.2
98.1
55.5
52.0
76.5
65.8
51.5
55.6
55.4
6.33
5.78
9.71
5.85
6.39
6.76
5.78
0.235
0.233
0.248
0.217
0.246
0.257
0.210
6.48
5.60
10.0
6.31
6.81
7.93
3.94
0.347
0.358
0.278
0.296
0.385
0.402
0.274
4.54
4.30
6.39
4.28
4.46
4.26
4.93
0.131
0.129
0.141
0.119
0.141
0.141
0.120
0.801
0.770
0.929
0.749
0.852
0.958
0.537
1.03
1.02
1.09
1.05
0.995
1.04
1.02
Potential Exposure in OH Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
123
106
17
37
73
69
54
119
102
17
38
68
63
56
95.9
95.3
100.0
97.3
94.5
94.2
98.1
55.5
52.0
76.5
65.8
51.5
55.6
55.4
21.7
19.8
33.2
20.0
21.9
23.1
19.8
0.804
0.797
0.851
0.743
0.843
0.881
0.718
22.2
19.2
34.3
21.6
23.3
27.2
13.5
1.19
1.23
0.953
1.01
1.32
1.38
0.940
15.6
14.7
21.9
14.7
15.3
14.6
16.9
0.447
0.442
0.483
0.406
0.482
0.483
0.410
0.801
0.770
0.929
0.749
0.852
0.958
0.537
1.03
1.02
1.09
1.05
0.995
1.04
1.02
Potential Absorbed Dose in OH Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
123
106
17
37
73
69
54
119
102
17
38
68
63
56
95.9
95.3
100.0
97.3
94.5
94.2
98.1
55.5
52.0
76.5
65.8
51.5
55.6
55.4
0.044
0.040
0.066
0.042
0.043
0.046
0.040
0.002
0.002
0.002
0.001
0.002
0.002
0.001
0.043
0.036
0.069
0.044
0.043
0.051
0.029
0.002
0.002
0.002
0.002
0.002
0.002
0.002
0.031
0.029
0.043
0.029
0.031
0.030
0.032
0.001
0.001
0.001
0.001
0.001
0.001
0.001
0.834
0.806
0.955
0.848
0.851
0.958
0.646
1.04
1.03
1.11
1.05
0.997
1.02
1.06
Potential Absorbed Dose in OH Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
123
106
17
37
73
69
54
119
102
17
38
68
63
56
95.9
95.3
100.0
97.3
94.5
94.2
98.1
55.5
52.0
76.5
65.8
51.5
55.6
55.4
0.149
0.137
0.227
0.142
0.149
0.159
0.136
0.005
0.005
0.006
0.005
0.006
0.006
0.005
0.146
0.123
0.238
0.150
0.147
0.175
0.099
0.008
0.008
0.007
0.007
0.008
0.008
0.007
0.106
0.101
0.146
0.099
0.105
0.102
0.111
0.003
0.003
0.003
0.003
0.003
0.003
0.003
0.834
0.806
0.955
0.848
0.851
0.958
0.646
1.04
1.03
1.11
1.05
0.997
1.02
1.06
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                     O-52

-------
Table O-23b.   PCB 52 (35693-99-3): Range of Potential Exposure and Potential Absorbed Dose in
                 OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
123
106
17
37
73
69
54
119
102
17
38
68
63
56

-------
Table O-24a.   PCB 95 (38379-99-6): Estimates of Potential Exposure and Potential Absorbed
                 Dose in OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
119
102
17
38
68
63
56
69.6
68.5
76.5
66.7
69.9
71.0
67.9
52.1
49.0
70.6
60.5
50.0
49.2
55.4
2.13
2.02
2.87
2.54
1.91
2.11
2.16
0.212
-
0.230
0.186
0.222
-
0.188
3.69
3.72
3.48
5.32
2.72
3.45
4.00
0.430
-
0.359
0.268
0.507
-
0.328
1.23
1.18
1.64
1.20
1.19
1.15
1.34
0.107
-
0.110
0.097
0.114
-
0.098
0.897
0.870
1.04
0.987
0.880
0.981
0.783
1.02
-
1.16
1.06
0.955
-
0.997
Potential Exposure in OH Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
119
102
17
38
68
63
56
69.6
68.5
76.5
66.7
69.9
71.0
67.9
52.1
49.0
70.6
60.5
50.0
49.2
55.4
6.53
6.18
8.78
7.77
5.85
6.46
6.62
0.650
-
0.706
0.568
0.680
-
0.575
11.3
11.4
10.7
16.3
8.34
10.6
12.3
1.32
-
1.10
0.822
1.55
-
1.01
3.77
3.61
5.01
3.68
3.65
3.53
4.09
0.327
-
0.336
0.297
0.348
-
0.302
0.897
0.870
1.04
0.987
0.880
0.981
0.783
1.02
-
1.16
1.06
0.955
-
0.997
Potential Absorbed Dose in OH Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
119
102
17
38
68
63
56
69.6
68.5
76.5
66.7
69.9
71.0
67.9
52.1
49.0
70.6
60.5
50.0
49.2
55.4
0.015
0.014
0.020
0.018
0.013
0.014
0.015
0.001
-
0.002
0.001
0.001
-
0.001
0.025
0.025
0.026
0.038
0.016
0.022
0.029
0.003
-
0.003
0.002
0.003
-
0.002
0.008
0.008
0.011
0.008
0.008
0.008
0.009
0.001
-
0.001
0.001
0.001
-
0.001
0.912
0.885
1.06
1.04
0.870
0.964
0.849
1.03
-
1.22
1.08
0.945
-
1.04
Potential Absorbed Dose in OH Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
119
102
17
38
68
63
56
69.6
68.5
76.5
66.7
69.9
71.0
67.9
52.1
49.0
70.6
60.5
50.0
49.2
55.4
0.045
0.042
0.062
0.054
0.039
0.044
0.046
0.004
-
0.005
0.004
0.004
-
0.004
0.077
0.077
0.080
0.115
0.051
0.068
0.088
0.008
-
0.009
0.006
0.009
-
0.006
0.026
0.025
0.033
0.025
0.025
0.025
0.027
0.002
-
0.002
0.002
0.002
-
0.002
0.912
0.885
1.06
1.04
0.870
0.964
0.849
1.03
-
1.22
1.08
0.945
-
1.04
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                     O-54

-------
Table O-24b.   PCB 95 (38379-99-6): Range of Potential Exposure and Potential Absorbed Dose in
                 OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
119
102
17
38
68
63
56

-------
Table O-25a.   PCB 101  (37680-73-2):  Estimates of Potential Exposure and Potential Absorbed
                 Dose in OH Adults. Summarized  by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
119
102
17
38
68
63
56
60.8
58.3
76.5
56.4
63.0
58.0
64.3
54.6
51.0
76.5
63.2
52.9
54.0
55.4
2.07
1.97
2.73
2.67
1.81
1.91
2.27
0.281
0.286
0.250
0.245
0.295
0.311
0.247
4.48
4.65
3.31
7.13
2.61
3.36
5.60
0.627
0.657
0.417
0.351
0.760
0.771
0.413
1.07
1.01
1.58
1.04
1.08
0.950
1.25
0.128
0.129
0.121
0.120
0.135
0.135
0.120
0.960
0.940
1.03
1.05
0.935
1.04
0.837
1.10
1.11
1.13
1.14
1.04
1.11
1.11
Potential Exposure in OH Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
119
102
17
38
68
63
56
60.8
58.3
76.5
56.4
63.0
58.0
64.3
54.6
51.0
76.5
63.2
52.9
54.0
55.4
6.35
6.03
8.36
8.17
5.55
5.85
6.96
0.861
0.877
0.765
0.751
0.904
0.952
0.758
13.7
14.2
10.1
21.8
7.99
10.3
17.1
1.92
2.01
1.28
1.08
2.33
2.36
1.27
3.29
3.09
4.83
3.19
3.31
2.91
3.82
0.391
0.394
0.372
0.368
0.412
0.414
0.366
0.960
0.940
1.03
1.05
0.935
1.04
0.837
1.10
1.11
1.13
1.14
1.04
1.11
1.11
Potential Absorbed Dose in OH Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
119
102
17
38
68
63
56
60.8
58.3
76.5
56.4
63.0
58.0
64.3
54.6
51.0
76.5
63.2
52.9
54.0
55.4
0.014
0.013
0.019
0.019
0.012
0.013
0.016
0.002
0.002
0.002
0.002
0.002
0.002
0.002
0.031
0.032
0.024
0.051
0.016
0.022
0.041
0.004
0.004
0.003
0.002
0.004
0.005
0.003
0.007
0.007
0.011
0.007
0.007
0.007
0.008
0.001
0.001
0.001
0.001
0.001
0.001
0.001
0.977
0.953
1.07
1.08
0.940
1.02
0.920
1.12
1.11
1.18
1.15
1.04
1.08
1.16
Potential Absorbed Dose in OH Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
119
102
17
38
68
63
56
60.8
58.3
76.5
56.4
63.0
58.0
64.3
54.6
51.0
76.5
63.2
52.9
54.0
55.4
0.044
0.041
0.059
0.057
0.037
0.039
0.049
0.006
0.006
0.006
0.005
0.006
0.006
0.005
0.096
0.099
0.074
0.156
0.050
0.066
0.124
0.012
0.012
0.010
0.007
0.013
0.014
0.008
0.022
0.021
0.032
0.021
0.023
0.020
0.025
0.003
0.003
0.002
0.002
0.003
0.003
0.002
0.977
0.953
1.07
1.08
0.940
1.02
0.920
1.12
1.11
1.18
1.15
1.04
1.08
1.16
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                     O-56

-------
Table O-25b.   PCB 101 (37680-73-2):  Range of Potential Exposure and Potential Absorbed Dose
                 in OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
125
108
17
39
73
69
56
119
102
17
38
68
63
56

-------
Table O-26a.   3.5.6-TCP (3.5.6-trichloro-2-pyridinol) (6515-38-4): Estimates of Potential Exposure
                 in OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Potential Exposure
-Aggregated
(ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
115
99
16
36
66
64
51
127
110
17
41
73
69
58
120
103
17
38
69
63
57
108
92
16
33
62
58
50
100.0
100.0
100.0
100.0
100.0
100.0
100.0
99.2
99.1
100.0
100.0
98.6
100.0
98.3
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
18.4
20.2
7.33
26.1
10.2
23.9
11.5
1,900
1,930
1,720
1,250
2,020
2,740
914
3.57
4.02
0.863
5.99
2.53
2.92
4.30
2,010
2,060
1,770
1,140
2,190
2,980
891
44.9
48.2
3.15
48.0
9.76
58.9
11.4
3,020
3,110
2,440
1,510
3,470
3,750
1,280
8.11
8.68
0.896
11.8
5.58
6.12
9.87
3,210
3,320
2,520
1,190
3,730
4,020
1,130
8.96
9.38
6.72
11.4
7.55
9.05
8.84
983
990
938
734
1,090
1,690
515
1.19
1.34
0.565
1.71
1.04
1.05
1.35
1,050
1,070
942
761
1,170
1,860
543
0.939
0.989
0.450
1.13
0.737
1.13
0.642
1.16
1.18
1.12
1.03
1.13
0.934
1.08
1.32
1.33
0.992
1.53
1.18
1.30
1.33
1.14
1.15
1.15
0.922
1.13
0.914
1.03
Potential Exposure in OH Adults (pmoles/day)
Potential Exposure
via Inhalation
(pmoles/day)
Potential Exposure
via Dietary
Ingestion
(pmoles/day)
Potential Exposure
via Indirect
Ingestion
(pmoles/day)
Potential Exposure
-Aggregated
(pmoles/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
115
99
16
36
66
64
51
127
110
17
41
73
69
58
120
103
17
38
69
63
57
108
92
16
33
62
58
50
100.0
100.0
100.0
100.0
100.0
100.0
100.0
99.2
99.1
100.0
100.0
98.6
100.0
98.3
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
92.6
102
36.9
132
51.5
120
57.8
9,590
9,740
8,670
6,280
10,200
13,800
4,600
18.0
20.3
4.35
30.2
12.7
14.7
21.7
10,100
10,400
8,910
5,750
11,100
15,000
4,490
226
243
15.9
242
49.2
297
57.5
15,200
15,700
12,300
7,590
17,500
18,900
6,450
40.9
43.7
4.52
59.6
28.1
30.8
49.8
16,200
16,700
12,700
6,000
18,800
20,300
5,710
45.1
47.3
33.8
57.3
38.0
45.6
44.6
4,950
4,990
4,730
3,700
5,490
8,540
2,590
5.98
6.76
2.85
8.60
5.23
5.31
6.82
5,310
5,410
4,750
3,830
5,920
9,390
2,740
0.939
0.989
0.450
1.13
0.737
1.13
0.642
1.16
1.18
1.12
1.03
1.13
0.934
1.08
1.32
1.33
0.992
1.53
1.18
1.30
1.33
1.14
1.15
1.15
0.922
1.13
0.914
1.03
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
                                                    O-58

-------
Table O-26b.   3.5.6-TCP (3.5.6-trichloro-2-pyridinol) (6515-38-4): Range of Potential Exposure in
                OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Exposure in OH Adults (ng/day)
Potential Exposure
via Inhalation
(ng/day)
Potential Exposure
via Dietary
Ingestion (ng/day)
Potential Exposure
via Indirect
Ingestion (ng/day)
Potential Exposure
- Aggregated
(ng/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
115
99
16
36
66
64
51
127
110
17
41
73
69
58
120
103
17
38
69
63
57
108
92
16
33
62
58
50
1.72
1.72
2.25
2.99
1.72
1.72
3.77

-------
Table O-26c.   3.5.6-TCP (3.5.6-trichloro-2-pyridinol) (6515-38-4): Estimates of Potential Absorbed
                 Dose in OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
% Detected
Arithmetic Mean
Std. Dev.
Geometric
Mean
Log Std. Dev.
Potential Absorbed Dose in OH Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Potential Absorbed
Dose - Aggregated
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
115
99
16
36
66
64
51
127
110
17
41
73
69
58
120
103
17
38
69
63
57
108
92
16
33
62
58
50
100.0
100.0
100.0
100.0
100.0
100.0
100.0
99.2
99.1
100.0
100.0
98.6
100.0
98.3
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.131
0.144
0.049
0.178
0.075
0.171
0.081
13.7
14.2
11.1
9.23
14.6
20.0
6.34
0.025
0.029
0.006
0.042
0.018
0.021
0.031
14.5
15.0
11.4
8.06
16.0
21.6
6.16
0.333
0.357
0.022
0.314
0.077
0.437
0.090
22.3
23.2
15.1
12.2
25.5
27.7
8.88
0.061
0.065
0.007
0.090
0.041
0.045
0.075
23.4
24.6
15.6
8.70
27.4
29.5
7.68
0.061
0.064
0.045
0.075
0.053
0.063
0.059
6.68
6.75
6.26
4.91
7.50
11.9
3.38
0.008
0.009
0.004
0.011
0.007
0.007
0.009
7.22
7.40
6.24
4.99
8.30
13.1
3.62
0.972
1.02
0.444
1.16
0.781
1.13
0.731
1.23
1.25
1.12
1.11
1.20
0.987
1.14
1.34
1.36
0.918
1.55
1.21
1.29
1.39
1.19
1.21
1.14
1.00
1.17
0.964
1.06
Potential Absorbed Dose in OH Adults (pmoles/kg/day)
Potential Absorbed
Dose via Inhalation
(pmoles/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(pmoles/kg/day)
Potential Absorbed
Dose - Aggregated
(pmoles/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
115
99
16
36
66
64
51
127
110
17
41
73
69
58
120
103
17
38
69
63
57
108
92
16
33
62
58
50
100.0
100.0
100.0
100.0
100.0
100.0
100.0
99.2
99.1
100.0
100.0
98.6
100.0
98.3
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
0.661
0.728
0.245
0.895
0.377
0.861
0.410
69.3
71.3
56.0
46.5
73.8
101
31.9
0.128
0.144
0.029
0.210
0.092
0.104
0.154
72.9
75.6
57.2
40.6
80.7
109
31.1
1.68
1.80
0.108
1.58
0.389
2.20
0.454
112
117
76.1
61.5
128
140
44.7
0.307
0.328
0.033
0.451
0.208
0.226
0.377
118
124
78.6
43.9
138
148
38.7
0.309
0.325
0.224
0.380
0.266
0.319
0.296
33.7
34.0
31.5
24.8
37.8
59.8
17.0
0.041
0.046
0.019
0.057
0.036
0.037
0.045
36.4
37.3
31.4
25.1
41.8
65.9
18.2
0.972
1.02
0.444
1.16
0.781
1.13
0.731
1.23
1.25
1.12
1.11
1.20
0.987
1.14
1.34
1.36
0.918
1.55
1.21
1.29
1.39
1.19
1.21
1.14
1.00
1.17
0.964
1.06
a Estimates are labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected estimates is below 50%.
"Potential Absorbed Dose" was calculated as the Potential Exposure times 50% (the assumed absorption factor into the body), divided by the subject's
body weight.
                                                      O-60

-------
Table O-26d.   3.5.6-TCP (3.5.6-trichloro-2-pyridinol) (6515-38-4):  Range of Potential Absorbed
                 Dose in OH Adults. Summarized by Exposure Pathway and Strata3
Exposure/Dose
Parameter and
Pathway 	
Strata
N
Minimum
25th
Percentile
50th
Percentile
75th
Percentile
95th
Percentile
Maximum
Potential Absorbed Dose in OH Adults (ng/kg/day)
Potential Absorbed
Dose via Inhalation
(ng/kg/day)
Potential Absorbed
Dose via Dietary
Ingestion
(ng/kg/day)
Potential Absorbed
Dose via Indirect
Ingestion
(ng/kg/day)
Potential Absorbed
Dose - Aggregated
(ng/kg/day)
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
115
99
16
36
66
64
51
127
110
17
41
73
69
58
120
103
17
38
69
63
57
108
92
16
33
62
58
50
0.015
0.015
0.017
0.018
0.015
0.015
0.018

-------

-------
                      Appendix P
Descriptive Statistics of Urinary Biomarker Concentrations
      for Target Pollutants in NC Study Participants
                           P-l

-------
P-2

-------
This appendix contains tables of descriptive statistics of urine biomarker data (unadjusted, adjusted for
specific gravity, and adjusted for creatinine levels, with  units expressed in both ng and pmoles) in NC
children and adults for the following pollutants and metabolites:
Pollutant/Metabolite
2,4-D (2,4-dichlorophenoxyacetic acid)
1 -hydroxybenz[a]anthracene
3-hydroxychrysene
Pentachlorophenol
3,5,6-TCP (3,5,6-trichloro-2-pyridinol)
Table Numbers
(Children)
Tables P-1 a, P-1b
Tables P-2a, P-2b
Tables P-3a, P-3b
Tables P-4a, P-4b
Tables P-5a, P-5b
Table Numbers
(Adults)
Tables P-1c, P-1d
Tables P-2c, P-2d
Tables P-3c, P-3d
Tables P-4c, P-4d
Tables P-5c, P-5d
Descriptive statistics are presented separately for the following groups of participants:
        All participants
        Participants from urban areas
        Participants from rural  areas
        Participants from low-income areas
        Participants from middle/upper-income areas
        Stay-at-home children  (or their caregivers)
        Day care children (or their caregivers)
                                                   P-3

-------
Table P-1a.    2.4-D (2.4-dichlorophenoxyacetic acid) (94-75-7): Estimated Urinary
                 Biomarker Concentrations in NC Preschool Children, Summarized by
                 Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration,
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
128
107
21
59
65
65
63
128
107
21
59
65
65
63
110
93
17
49
57
55
55
128
107
21
59
65
65
63
128
107
21
59
65
65
63
110
93
17
49
57
55
55
% Detected
93.8
93.5
95.2
96.6
90.8
87.7
100.0
93.8
93.5
95.2
96.6
90.8
87.7
100.0
93.6
93.5
94.1
98.0
89.5
87.3
100.0
93.8
93.5
95.2
96.6
90.8
87.7
100.0
93.8
93.5
95.2
96.6
90.8
87.7
100.0
93.6
93.5
94.1
98.0
89.5
87.3
100.0
Arithmetic Mean
0.775
0.812
0.583
0.836
0.707
0.715
0.836
0.758
0.795
0.571
0.819
0.692
0.700
0.819
1.16
1.19
1.00
1.23
1.08
1.16
1.15
3.50
3.67
2.64
3.78
3.20
3.23
3.78
3.43
3.60
2.59
3.70
3.13
3.17
3.70
0.592
0.606
0.513
0.627
0.555
0.594
0.590
Std. Dev.
0.561
0.575
0.453
0.558
0.573
0.556
0.565
0.549
0.562
0.442
0.546
0.561
0.545
0.552
0.761
0.795
0.536
0.733
0.792
0.873
0.639
2.54
2.60
2.05
2.52
2.59
2.52
2.55
2.48
2.54
2.00
2.47
2.54
2.46
2.50
0.389
0.406
0.274
0.375
0.405
0.446
0.326
Geometric
Mean
0.594
0.624
0.465
0.665
0.522
0.519
0.684
0.582
0.611
0.456
0.652
0.511
0.508
0.670
0.933
0.947
0.862
1.04
0.835
0.869
1.00
2.69
2.82
2.10
3.01
2.36
2.35
3.09
2.63
2.76
2.06
2.95
2.31
2.30
3.03
0.477
0.484
0.441
0.532
0.427
0.444
0.512
Log Std. Dev.
0.759
0.768
0.670
0.710
0.799
0.841
0.640
0.758
0.768
0.669
0.710
0.799
0.841
0.638
0.687
0.703
0.610
0.584
0.764
0.809
0.537
0.759
0.768
0.670
0.710
0.799
0.841
0.640
0.758
0.768
0.669
0.710
0.799
0.841
0.638
0.687
0.703
0.610
0.584
0.764
0.809
0.537
a Not detected results are replaced by the method detection limit (MDL) divided by the square root of 2. Multiple sample results for a given
study subject have been log-transformed, averaged, and exponentiated back to regular units prior to summarizing the data within a stratum. This
result is labeled as "detected" if any measurement entering into the calculation was detected.  Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     P-4

-------
Table P-1b.    2.4-D (2.4-dichlorophenoxyacetic acid) (94-75-7): Range of Estimated
                 Urinary Biomarker Concentrations in NC Preschool Children, Summarized
                 by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
128
107
21
59
65
65
63
128
107
21
59
65
65
63
110
93
17
49
57
55
55
128
107
21
59
65
65
63
128
107
21
59
65
65
63
110
93
17
49
57
55
55
Minimum

-------
Table P-1c.   2.4-D (2.4-dichlorophenoxyacetic acid) (94-75-7): Estimated Urinary
                 Biomarker Concentrations in NC Adults, Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration,
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
128
107
21
59
65
65
63
128
107
21
59
65
65
63
112
95
17
50
58
55
57
128
107
21
59
65
65
63
128
107
21
59
65
65
63
112
95
17
50
58
55
57
% Detected
86.7
86.0
90.5
86.4
89.2
87.7
85.7
86.7
86.0
90.5
86.4
89.2
87.7
85.7
84.8
84.2
88.2
84.0
87.9
85.5
84.2
86.7
86.0
90.5
86.4
89.2
87.7
85.7
86.7
86.0
90.5
86.4
89.2
87.7
85.7
84.8
84.2
88.2
84.0
87.9
85.5
84.2
Arithmetic Mean
0.935
0.978
0.717
0.995
0.920
0.927
0.943
0.914
0.956
0.699
0.971
0.899
0.906
0.922
0.705
0.726
0.586
0.656
0.774
0.811
0.602
4.23
4.43
3.24
4.50
4.16
4.20
4.27
4.13
4.32
3.16
4.40
4.07
4.10
4.17
0.360
0.371
0.300
0.335
0.396
0.415
0.308
Std. Dev.
1.05
1.11
0.584
1.28
0.808
0.978
1.12
1.02
1.08
0.568
1.25
0.788
0.953
1.09
0.682
0.726
0.324
0.722
0.659
0.771
0.571
4.73
5.03
2.64
5.80
3.66
4.42
5.07
4.62
4.90
2.57
5.65
3.57
4.31
4.95
0.348
0.371
0.165
0.369
0.337
0.394
0.292
Geometric
Mean
0.593
0.610
0.516
0.573
0.645
0.603
0.584
0.580
0.596
0.504
0.560
0.631
0.589
0.570
0.476
0.473
0.491
0.425
0.556
0.558
0.408
2.68
2.76
2.34
2.59
2.92
2.73
2.64
2.62
2.70
2.28
2.53
2.85
2.67
2.58
0.243
0.242
0.251
0.217
0.284
0.285
0.209
Log Std. Dev.
0.956
0.975
0.862
1.02
0.891
0.941
0.978
0.956
0.975
0.861
1.02
0.891
0.940
0.979
0.925
0.965
0.683
0.957
0.853
0.912
0.919
0.956
0.975
0.862
1.02
0.891
0.941
0.978
0.956
0.975
0.861
1.02
0.891
0.940
0.979
0.925
0.965
0.683
0.957
0.853
0.912
0.919
a Not detected results are replaced by the method detection limit (MDL) divided by the square root of 2. Multiple sample results for a given
study subject have been log-transformed, averaged, and exponentiated back to regular units prior to summarizing the data within a stratum.  This
result is labeled as "detected" if any measurement entering into the calculation was detected.  Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                      P-6

-------
Table P-1d.    2.4-D (2.4-dichlorophenoxyacetic acid) (94-75-7): Range of Estimated
                 Urinary Biomarker Concentrations in NC Adults, Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
128
107
21
59
65
65
63
128
107
21
59
65
65
63
112
95
17
50
58
55
57
128
107
21
59
65
65
63
128
107
21
59
65
65
63
112
95
17
50
58
55
57
Minimum

-------
Table P-2a.    1-hydroxybenzralanthracene (69847-26-3): Estimated Urinary Biomarker
                 Concentrations in NC Preschool Children, Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration,
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
128
107
21
59
65
65
63
128
107
21
59
65
65
63
110
93
17
49
57
55
55
128
107
21
59
65
65
63
128
107
21
59
65
65
63
110
93
17
49
57
55
55
% Detected
1.6
1.9
0.0
3.4
0.0
1.5
1.6
1.6
1.9
0.0
3.4
0.0
1.5
1.6
1.8
2.2
0.0
4.1
0.0
1.8
1.8
1.6
1.9
0.0
3.4
0.0
1.5
1.6
1.6
1.9
0.0
3.4
0.0
1.5
1.6
1.8
2.2
0.0
4.1
0.0
1.8
1.8
Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
a Not detected results are replaced by the method detection limit (MDL) divided by the square root of 2. Multiple sample results for a given
study subject have been log-transformed, averaged, and exponentiated back to regular units prior to summarizing the data within a stratum. This
result is labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     P-8

-------
Table P-2b.    1-hydroxybenzralanthracene (69847-26-3): Range of Estimated Urinary
                 Biomarker Concentrations in NC Preschool Children, Summarized by
                 Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
128
107
21
59
65
65
63
128
107
21
59
65
65
63
110
93
17
49
57
55
55
128
107
21
59
65
65
63
128
107
21
59
65
65
63
110
93
17
49
57
55
55
Minimum

-------
Table P-2c.   1-hydroxybenzralanthracene (69847-26-3): Estimated Urinary Biomarker
                 Concentrations in NC Adults, Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration,
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
128
107
21
59
65
65
63
128
107
21
59
65
65
63
112
95
17
50
58
55
57
128
107
21
59
65
65
63
128
107
21
59
65
65
63
112
95
17
50
58
55
57
% Detected
31.3
31.8
28.6
27.1
33.8
35.4
27.0
31.3
31.8
28.6
27.1
33.8
35.4
27.0
32.1
31.6
35.3
28.0
34.5
36.4
28.1
31.3
31.8
28.6
27.1
33.8
35.4
27.0
31.3
31.8
28.6
27.1
33.8
35.4
27.0
32.1
31.6
35.3
28.0
34.5
36.4
28.1
Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
a Not detected results are replaced by the method detection limit (MDL) divided by the square root of 2. Multiple sample results for a given
study subject have been log-transformed, averaged, and exponentiated back to regular units prior to summarizing the data within a stratum. This
result is labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     P-10

-------
Table P-2d.    1-hydroxybenzralanthracene (69847-26-3): Range of Estimated Urinary
                 Biomarker Concentrations in NC Adults, Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
128
107
21
59
65
65
63
128
107
21
59
65
65
63
112
95
17
50
58
55
57
128
107
21
59
65
65
63
128
107
21
59
65
65
63
112
95
17
50
58
55
57
Minimum

-------
Table P-3a.    3-hydroxychrysene (63019-39-6): Estimated Urinary Biomarker
                 Concentrations in NC Preschool Children, Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration,
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
128
107
21
59
65
65
63
128
107
21
59
65
65
63
110
93
17
49
57
55
55
128
107
21
59
65
65
63
128
107
21
59
65
65
63
110
93
17
49
57
55
55
% Detected
2.3
2.8
0.0
3.4
1.5
0.0
4.8
2.3
2.8
0.0
3.4
1.5
0.0
4.8
2.7
3.2
0.0
4.1
1.8
0.0
5.5
2.3
2.8
0.0
3.4
1.5
0.0
4.8
2.3
2.8
0.0
3.4
1.5
0.0
4.8
2.7
3.2
0.0
4.1
1.8
0.0
5.5
Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
a Not detected results are replaced by the method detection limit (MDL) divided by the square root of 2.  Multiple sample results for a given
study subject have been log-transformed, averaged, and exponentiated back to regular units prior to summarizing the data within a stratum. This
result is labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     P-12

-------
Table P-3b.    3-hydroxychrysene (63019-39-6):  Range of Estimated Urinary Biomarker
                 Concentrations in NC Preschool Children, Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
128
107
21
59
65
65
63
128
107
21
59
65
65
63
110
93
17
49
57
55
55
128
107
21
59
65
65
63
128
107
21
59
65
65
63
110
93
17
49
57
55
55
Minimum

-------
Table P-3c.   3-hydroxychrysene (63019-39-6): Estimated Urinary Biomarker
                 Concentrations in NC Adults, Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration,
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
128
107
21
59
65
65
63
128
107
21
59
65
65
63
112
95
17
50
58
55
57
128
107
21
59
65
65
63
128
107
21
59
65
65
63
112
95
17
50
58
55
57
% Detected
7.8
6.5
14.3
13.6
3.1
7.7
7.9
7.8
6.5
14.3
13.6
3.1
7.7
7.9
8.9
7.4
17.6
16.0
3.4
9.1
8.8
7.8
6.5
14.3
13.6
3.1
7.7
7.9
7.8
6.5
14.3
13.6
3.1
7.7
7.9
8.9
7.4
17.6
16.0
3.4
9.1
8.8
Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
a Not detected results are replaced by the method detection limit (MDL) divided by the square root of 2.  Multiple sample results for a given
study subject have been log-transformed, averaged, and exponentiated back to regular units prior to summarizing the data within a stratum. This
result is labeled as "detected" if any measurement entering into the calculation was detected.  Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                      P-14

-------
Table P-3d.    3-hydroxychrysene (63019-39-6): Range of Estimated Urinary Biomarker
                 Concentrations in NC Adults, Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
128
107
21
59
65
65
63
128
107
21
59
65
65
63
112
95
17
50
58
55
57
128
107
21
59
65
65
63
128
107
21
59
65
65
63
112
95
17
50
58
55
57
Minimum

-------
Table P-4a.   Pentachlorophenol (87-86-5): Estimated Urinary Biomarker Concentrations
                 in NC Preschool Children, Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration,
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
128
107
21
59
65
65
63
128
107
21
59
65
65
63
110
93
17
49
57
55
55
128
107
21
59
65
65
63
128
107
21
59
65
65
63
110
93
17
49
57
55
55
% Detected
89.1
88.8
90.5
94.9
84.6
80.0
98.4
89.1
88.8
90.5
94.9
84.6
80.0
98.4
88.2
88.2
88.2
93.9
84.2
78.2
98.2
89.1
88.8
90.5
94.9
84.6
80.0
98.4
89.1
88.8
90.5
94.9
84.6
80.0
98.4
88.2
88.2
88.2
93.9
84.2
78.2
98.2
Arithmetic Mean
0.605
0.639
0.433
0.659
0.571
0.642
0.567
0.592
0.625
0.425
0.645
0.559
0.629
0.555
0.898
0.940
0.665
0.913
0.915
0.991
0.804
2.27
2.40
1.63
2.47
2.14
2.41
2.13
2.22
2.35
1.60
2.42
2.10
2.36
2.08
0.381
0.399
0.282
0.387
0.388
0.421
0.341
Std. Dev.
0.629
0.672
0.280
0.625
0.649
0.734
0.500
0.615
0.658
0.273
0.611
0.636
0.720
0.488
0.946
1.01
0.323
0.752
1.11
1.11
0.741
2.36
2.52
1.05
2.35
2.44
2.76
1.88
2.31
2.47
1.03
2.30
2.39
2.70
1.83
0.401
0.430
0.137
0.319
0.472
0.472
0.315
Geometric
Mean
0.433
0.447
0.369
0.498
0.388
0.419
0.448
0.424
0.437
0.363
0.488
0.380
0.410
0.439
0.643
0.653
0.593
0.710
0.610
0.665
0.622
1.63
1.68
1.39
1.87
1.46
1.57
1.68
1.59
1.64
1.36
1.83
1.43
1.54
1.65
0.273
0.277
0.252
0.301
0.259
0.282
0.264
Log Std. Dev.
0.766
0.798
0.564
0.705
0.810
0.876
0.637
0.765
0.797
0.564
0.705
0.810
0.877
0.636
0.763
0.802
0.506
0.696
0.821
0.853
0.667
0.766
0.798
0.564
0.705
0.810
0.876
0.637
0.765
0.797
0.564
0.705
0.810
0.877
0.636
0.763
0.802
0.506
0.696
0.821
0.853
0.667
a Not detected results are replaced by the method detection limit (MDL) divided by the square root of 2. Multiple sample results for a given
study subject have been log-transformed, averaged, and exponentiated back to regular units prior to summarizing the data within a stratum. This
result is labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     P-16

-------
Table P-4b.    Pentachlorophenol (87-86-5): Range of Estimated  Urinary Biomarker
                 Concentrations in NC Preschool Children, Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
128
107
21
59
65
65
63
128
107
21
59
65
65
63
110
93
17
49
57
55
55
128
107
21
59
65
65
63
128
107
21
59
65
65
63
110
93
17
49
57
55
55
Minimum

-------
Table P-4c.   Pentachlorophenol (87-86-5):  Estimated Urinary Biomarker Concentrations
                 in NC Adults, Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration,
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
128
107
21
59
65
65
63
128
107
21
59
65
65
63
112
95
17
50
58
55
57
128
107
21
59
65
65
63
128
107
21
59
65
65
63
112
95
17
50
58
55
57
% Detected
69.5
70.1
66.7
69.5
69.2
72.3
66.7
69.5
70.1
66.7
69.5
69.2
72.3
66.7
66.1
67.4
58.8
64.0
67.2
69.1
63.2
69.5
70.1
66.7
69.5
69.2
72.3
66.7
69.5
70.1
66.7
69.5
69.2
72.3
66.7
66.1
67.4
58.8
64.0
67.2
69.1
63.2
Arithmetic Mean
0.478
0.514
0.296
0.500
0.470
0.461
0.496
0.467
0.502
0.289
0.488
0.458
0.450
0.484
0.336
0.356
0.227
0.312
0.363
0.368
0.306
1.80
1.93
1.11
1.88
1.76
1.73
1.86
1.75
1.88
1.08
1.83
1.72
1.69
1.82
0.143
0.151
0.096
0.132
0.154
0.156
0.130
Std. Dev.
0.595
0.641
0.168
0.696
0.509
0.494
0.687
0.579
0.623
0.163
0.677
0.496
0.482
0.668
0.363
0.387
0.138
0.383
0.357
0.347
0.378
2.23
2.41
0.629
2.61
1.91
1.85
2.58
2.17
2.34
0.611
2.54
1.86
1.81
2.51
0.154
0.164
0.058
0.163
0.151
0.147
0.160
Geometric
Mean
0.327
0.343
0.257
0.330
0.328
0.331
0.323
0.320
0.335
0.251
0.322
0.321
0.324
0.316
0.242
0.252
0.193
0.219
0.264
0.279
0.210
1.23
1.29
0.966
1.24
1.23
1.24
1.21
1.20
1.26
0.944
1.21
1.21
1.22
1.18
0.102
0.107
0.082
0.093
0.112
0.118
0.089
Log Std. Dev.
0.789
0.824
0.533
0.806
0.796
0.759
0.825
0.788
0.822
0.531
0.805
0.795
0.758
0.823
0.766
0.789
0.593
0.777
0.772
0.706
0.802
0.789
0.824
0.533
0.806
0.796
0.759
0.825
0.788
0.822
0.531
0.805
0.795
0.758
0.823
0.766
0.789
0.593
0.777
0.772
0.706
0.802
a Not detected results are replaced by the method detection limit (MDL) divided by the square root of 2. Multiple sample results for a given
study subject have been log-transformed, averaged, and exponentiated back to regular units prior to summarizing the data within a stratum.  This
result is labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected results is below  50%.
                                                      P-18

-------
Table P-4d.    Pentachlorophenol (87-86-5): Range of Estimated  Urinary Biomarker
                 Concentrations in  NC Adults, Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
128
107
21
59
65
65
63
128
107
21
59
65
65
63
112
95
17
50
58
55
57
128
107
21
59
65
65
63
128
107
21
59
65
65
63
112
95
17
50
58
55
57
Minimum

-------
Table P-5a.    3.5.6-TCP (3.5.6-trichloro-2-pyridinol) (6515-38-4):  Estimated Urinary
                 Biomarker Concentrations in NC Preschool Children, Summarized by
                 Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration,
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
128
107
21
59
65
65
63
128
107
21
59
65
65
63
110
93
17
49
57
55
55
128
107
21
59
65
65
63
128
107
21
59
65
65
63
110
93
17
49
57
55
55
% Detected
98.4
98.1
100.0
98.3
98.5
96.9
100.0
98.4
98.1
100.0
98.3
98.5
96.9
100.0
98.2
97.8
100.0
98.0
98.2
96.4
100.0
98.4
98.1
100.0
98.3
98.5
96.9
100.0
98.4
98.1
100.0
98.3
98.5
96.9
100.0
98.2
97.8
100.0
98.0
98.2
96.4
100.0
Arithmetic Mean
7.28
7.28
7.28
6.55
8.02
8.12
6.42
7.13
7.13
7.14
6.41
7.85
7.95
6.28
10.5
10.2
12.1
9.45
11.5
11.9
9.10
36.7
36.7
36.7
33.0
40.4
40.9
32.3
35.9
35.9
36.0
32.3
39.6
40.1
31.6
5.98
5.82
6.87
5.38
6.57
6.77
5.18
Std. Dev.
10.3
10.9
6.93
7.36
12.7
13.7
4.76
10.1
10.7
6.77
7.18
12.5
13.4
4.65
12.4
12.7
10.6
10.2
14.4
16.0
7.24
52.0
54.9
34.9
37.1
64.0
69.1
24.0
51.0
53.8
34.1
36.2
62.8
67.7
23.4
7.07
7.26
6.06
5.81
8.22
9.09
4.12
Geometric
Mean
5.22
5.18
5.46
4.90
5.48
5.15
5.31
5.12
5.07
5.36
4.80
5.37
5.04
5.20
7.96
7.70
9.55
7.13
8.75
8.43
7.52
26.3
26.1
27.5
24.7
27.6
25.9
26.7
25.8
25.6
27.0
24.2
27.1
25.4
26.2
4.53
4.39
5.44
4.06
4.98
4.80
4.28
Log Std. Dev.
0.741
0.744
0.742
0.691
0.805
0.862
0.597
0.739
0.742
0.741
0.689
0.804
0.861
0.595
0.663
0.664
0.650
0.664
0.674
0.741
0.576
0.741
0.744
0.742
0.691
0.805
0.862
0.597
0.739
0.742
0.741
0.689
0.804
0.861
0.595
0.663
0.664
0.650
0.664
0.674
0.741
0.576
a Not detected results are replaced by the method detection limit (MDL) divided by the square root of 2.  Multiple sample results for a given
study subject have been log-transformed, averaged, and exponentiated back to regular units prior to summarizing the data within a stratum. This
result is labeled as "detected" if any measurement entering into the calculation was detected.  Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     P-20

-------
Table P-5b.    3.5.6-TCP (3.5.6-trichloro-2-pyridinol) (6515-38-4): Range of Estimated
                 Urinary Biomarker Concentrations  in NC Preschool Children, Summarized
                 by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
128
107
21
59
65
65
63
128
107
21
59
65
65
63
110
93
17
49
57
55
55
128
107
21
59
65
65
63
128
107
21
59
65
65
63
110
93
17
49
57
55
55
Minimum

-------
Table P-5c.   3.5.6-TCP (3.5.6-trichloro-2-pyridinol) (6515-38-4): Estimated Urinary
                 Biomarker Concentrations in NC Adults, Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration,
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
128
107
21
59
65
65
63
128
107
21
59
65
65
63
112
95
17
50
58
55
57
128
107
21
59
65
65
63
128
107
21
59
65
65
63
112
95
17
50
58
55
57
% Detected
98.4
99.1
95.2
96.6
100.0
98.5
98.4
98.4
99.1
95.2
96.6
100.0
98.5
98.4
98.2
98.9
94.1
96.0
100.0
98.2
98.2
98.4
99.1
95.2
96.6
100.0
98.5
98.4
98.4
99.1
95.2
96.6
100.0
98.5
98.4
98.2
98.9
94.1
96.0
100.0
98.2
98.2
Arithmetic Mean
5.42
5.49
5.06
4.93
5.77
5.67
5.16
5.29
5.36
4.93
4.81
5.64
5.53
5.04
4.07
4.11
3.88
3.41
4.63
4.79
3.38
27.3
27.7
25.5
24.9
29.1
28.6
26.0
26.7
27.0
24.9
24.3
28.4
27.9
25.4
2.32
2.34
2.21
1.94
2.64
2.73
1.93
Std. Dev.
4.09
3.97
4.73
4.01
3.96
4.32
3.86
3.98
3.87
4.59
3.91
3.86
4.20
3.75
2.84
2.90
2.56
2.62
2.99
3.40
1.96
20.6
20.0
23.8
20.2
20.0
21.8
19.4
20.1
19.5
23.1
19.7
19.5
21.2
18.9
1.62
1.65
1.46
1.49
1.71
1.93
1.12
Geometric
Mean
4.28
4.40
3.74
3.76
4.78
4.47
4.10
4.18
4.30
3.65
3.68
4.67
4.37
4.00
3.31
3.34
3.18
2.66
3.95
3.95
2.80
21.6
22.2
18.8
19.0
24.1
22.5
20.7
21.1
21.7
18.4
18.5
23.5
22.0
20.2
1.89
1.90
1.81
1.52
2.25
2.25
1.59
Log Std. Dev.
0.682
0.666
0.761
0.736
0.604
0.683
0.684
0.680
0.664
0.758
0.734
0.602
0.680
0.683
0.654
0.656
0.657
0.721
0.548
0.602
0.661
0.682
0.666
0.761
0.736
0.604
0.683
0.684
0.680
0.664
0.758
0.734
0.602
0.680
0.683
0.654
0.656
0.657
0.721
0.548
0.602
0.661
a Not detected results are replaced by the method detection limit (MDL) divided by the square root of 2.  Multiple sample results for a given
study subject have been log-transformed, averaged, and exponentiated back to regular units prior to summarizing the data within a stratum. This
result is labeled as "detected" if any measurement entering into the calculation was detected.  Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                      P-22

-------
Table P-5d.    3.5.6-TCP (3.5.6-trichloro-2-pyridinol) (6515-38-4): Range of Estimated
                 Urinary Biomarker Concentrations in NC Adults, Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
128
107
21
59
65
65
63
128
107
21
59
65
65
63
112
95
17
50
58
55
57
128
107
21
59
65
65
63
128
107
21
59
65
65
63
112
95
17
50
58
55
57
Minimum

-------

-------
                      Appendix Q
Descriptive Statistics of Urinary Biomarker Concentrations
      for Target Pollutants in OH Study Participants
                          Q-l

-------
Q-2

-------
This appendix contains tables of descriptive statistics of urine biomarker data (unadjusted, adjusted for
specific gravity, and adjusted for creatinine levels, with  units expressed in both ng and pmoles) in OH
children and adults for the following pollutants and metabolites:
Pollutant/Metabolite
2,4-D (2,4-dichlorophenoxyacetic acid)
1 -hydroxybenz[a]anthracene
3-hydroxybenz[a]anthracene
3-hydroxybenz[a]pyrene
3-hydroxychrysene
6-hydroxychrysene
6-hydroxyindeno[1 ,2,3-cc/]pyrene
1-hydroxypyrene
Pentachlorophenol
3-phenoxybenzoic acid
3,5,6-TCP (3,5,6-trichloro-2-pyridinol)
Table Numbers
(Children)
Tables Q-1a, Q-1b
Tables Q-2a, Q-2b
Tables Q-3a, Q-3b
Tables Q-4a, Q-4b
Tables Q-5a, Q-5b
Tables Q-6a, Q-6b
Tables Q-7a, Q-7b
Tables Q-8a, Q-8b
Tables Q-9a, Q-9b
Tables Q-10a, Q-1 Ob
Tables Q-11 a, Q-11b
Table Numbers
(Adults)
Tables Q-1 c, Q-1d
Tables Q-2c, Q-2d
Tables Q-3c, Q-3d
Tables Q-4c, Q-4d
Tables Q-5c, Q-5d
Tables Q-6c, Q-6d
Tables Q-7c, Q-7d
Tables Q-8c, Q-8d
Tables Q-9c, Q-9d
Tables Q-1 Oc, Q-1 Od
Tables Q-1 1c, Q-11 d
Descriptive statistics are presented separately for the following groups of participants:
        All participants
        Participants from urban areas
        Participants from rural areas
        Participants from low-income areas
        Participants from middle/upper-income areas
        Stay-at-home children (or their caregivers)
        Day care children (or their caregivers)
                                                  Q-3

-------
Table Q-1a.   2.4-D (2.4-dichlorophenoxyacetic acid) (94-75-7): Estimated Urinary
                 Biomarker Concentrations in OH Preschool Children, Summarized by
                 Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration,
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
126
109
17
40
73
69
57
126
109
17
40
73
69
57
111
96
15
38
63
59
52
126
109
17
40
73
69
57
126
109
17
40
73
69
57
111
96
15
38
63
59
52
% Detected
98.4
98.2
100.0
100.0
97.3
97.1
100.0
98.4
98.2
100.0
100.0
97.3
97.1
100.0
98.2
97.9
100.0
100.0
96.8
96.6
100.0
98.4
98.2
100.0
100.0
97.3
97.1
100.0
98.4
98.2
100.0
100.0
97.3
97.1
100.0
98.2
97.9
100.0
100.0
96.8
96.6
100.0
Arithmetic Mean
1.32
1.32
1.30
1.36
1.37
1.50
1.10
1.29
1.29
1.27
1.33
1.35
1.47
1.08
1.75
1.71
1.98
1.77
1.77
1.91
1.56
5.97
5.98
5.89
6.16
6.22
6.80
4.96
5.84
5.85
5.76
6.03
6.09
6.65
4.86
0.892
0.873
1.01
0.904
0.905
0.975
0.798
Std. Dev.
1.59
1.68
0.904
1.14
1.90
1.84
1.21
1.56
1.64
0.877
1.12
1.86
1.80
1.19
1.97
2.08
0.988
1.35
2.39
2.03
1.89
7.21
7.59
4.09
5.18
8.61
8.33
5.46
7.05
7.43
3.97
5.06
8.43
8.13
5.36
1.01
1.06
0.505
0.692
1.22
1.04
0.968
Geometric
Mean
0.927
0.902
1.11
1.03
0.908
1.03
0.816
0.909
0.884
1.08
1.00
0.890
1.01
0.800
1.31
1.24
1.82
1.37
1.26
1.46
1.16
4.20
4.08
5.00
4.64
4.11
4.66
3.69
4.11
4.00
4.90
4.55
4.03
4.57
3.62
0.668
0.634
0.932
0.700
0.643
0.744
0.591
Log Std. Dev.
0.794
0.822
0.571
0.765
0.842
0.853
0.703
0.793
0.822
0.568
0.763
0.842
0.852
0.703
0.726
0.753
0.404
0.731
0.767
0.738
0.700
0.794
0.822
0.571
0.765
0.842
0.853
0.703
0.793
0.822
0.568
0.763
0.842
0.852
0.703
0.726
0.753
0.404
0.731
0.767
0.738
0.700
a Not detected results are replaced by the method detection limit (MDL) divided by the square root of 2. Multiple sample results for a given
study subject have been log-transformed, averaged, and exponentiated back to regular units prior to summarizing the data within a stratum. This
result is labeled as "detected" if any measurement entering into the calculation was detected.  Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     Q-4

-------
Table Q-1b.    2.4-D (2.4-dichlorophenoxyacetic acid) (94-75-7): Range of Estimated
                 Urinary Biomarker Concentrations in OH Preschool Children, Summarized
                 by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
126
109
17
40
73
69
57
126
109
17
40
73
69
57
111
96
15
38
63
59
52
126
109
17
40
73
69
57
126
109
17
40
73
69
57
111
96
15
38
63
59
52
Minimum

-------
Table Q-1c.   2.4-D (2.4-dichlorophenoxyacetic acid) (94-75-7): Estimated Urinary
                 Biomarker Concentrations in OH Adults, Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration,
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
126
109
17
41
72
69
57
125
108
17
41
72
68
57
109
94
15
38
62
58
51
126
109
17
41
72
69
57
125
108
17
41
72
68
57
109
94
15
38
62
58
51
% Detected
89.7
89.0
94.1
90.2
90.3
87.0
93.0
90.4
89.8
94.1
90.2
90.3
88.2
93.0
89.0
88.3
93.3
89.5
88.7
86.2
92.2
89.7
89.0
94.1
90.2
90.3
87.0
93.0
90.4
89.8
94.1
90.2
90.3
88.2
93.0
89.0
88.3
93.3
89.5
88.7
86.2
92.2
Arithmetic Mean
1.02
1.000
1.15
1.05
1.02
0.999
1.04
1.00
0.984
1.12
1.03
0.998
0.989
1.02
0.771
0.766
0.800
0.817
0.771
0.811
0.725
4.61
4.52
5.19
4.75
4.62
4.52
4.72
4.54
4.45
5.08
4.65
4.52
4.47
4.62
0.394
0.392
0.409
0.418
0.394
0.414
0.371
Std. Dev.
1.03
1.04
1.05
1.02
1.10
1.16
0.866
1.01
1.01
1.03
0.997
1.07
1.14
0.850
0.841
0.856
0.765
1.11
0.689
0.827
0.863
4.68
4.69
4.75
4.60
4.96
5.26
3.92
4.59
4.59
4.66
4.51
4.85
5.15
3.85
0.430
0.438
0.391
0.569
0.352
0.423
0.441
Geometric
Mean
0.701
0.685
0.810
0.733
0.689
0.647
0.773
0.694
0.679
0.793
0.716
0.674
0.646
0.755
0.536
0.527
0.601
0.509
0.568
0.540
0.532
3.17
3.10
3.67
3.32
3.12
2.93
3.50
3.14
3.07
3.59
3.24
3.05
2.92
3.42
0.274
0.269
0.307
0.260
0.290
0.276
0.272
Log Std. Dev.
0.876
0.877
0.883
0.866
0.895
0.928
0.806
0.868
0.868
0.882
0.868
0.894
0.916
0.806
0.856
0.873
0.751
0.950
0.808
0.937
0.762
0.876
0.877
0.883
0.866
0.895
0.928
0.806
0.868
0.868
0.882
0.868
0.894
0.916
0.806
0.856
0.873
0.751
0.950
0.808
0.937
0.762
a Not detected results are replaced by the method detection limit (MDL) divided by the square root of 2. Multiple sample results for a given
study subject have been log-transformed, averaged, and exponentiated back to regular units prior to summarizing the data within a stratum.  This
result is labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                      Q-6

-------
Table Q-1d.   2.4-D (2.4-dichlorophenoxyacetic acid) (94-75-7): Range of Estimated
                 Urinary Biomarker Concentrations in OH Adults, Summarized  by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
126
109
17
41
72
69
57
125
108
17
41
72
68
57
109
94
15
38
62
58
51
126
109
17
41
72
69
57
125
108
17
41
72
68
57
109
94
15
38
62
58
51
Minimum

-------
Table Q-2a.   1-hydroxybenzralanthracene (69847-26-3): Estimated Urinary Biomarker
                 Concentrations in OH Preschool Children, Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration,
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
126
109
17
40
73
69
57
126
109
17
40
73
69
57
111
96
15
38
63
59
52
126
109
17
40
73
69
57
126
109
17
40
73
69
57
111
96
15
38
63
59
52
% Detected
4.8
4.6
5.9
5.0
4.1
1.4
8.8
4.8
4.6
5.9
5.0
4.1
1.4
8.8
3.6
4.2
0.0
5.3
3.2
0.0
7.7
4.8
4.6
5.9
5.0
4.1
1.4
8.8
4.8
4.6
5.9
5.0
4.1
1.4
8.8
3.6
4.2
0.0
5.3
3.2
0.0
7.7
Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
a Not detected results are replaced by the method detection limit (MDL) divided by the square root of 2. Multiple sample results for a given
study subject have been log-transformed, averaged, and exponentiated back to regular units prior to summarizing the data within a stratum. This
result is labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected results is below 50%.

-------
Table Q-2b.    1-hydroxybenzralanthracene (69847-26-3): Range of Estimated Urinary
                 Biomarker Concentrations in OH Preschool Children, Summarized by
                 Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
126
109
17
40
73
69
57
126
109
17
40
73
69
57
111
96
15
38
63
59
52
126
109
17
40
73
69
57
126
109
17
40
73
69
57
111
96
15
38
63
59
52
Minimum

-------
Table Q-2c.   1-hydroxybenzralanthracene (69847-26-3): Estimated Urinary Biomarker
                 Concentrations in OH Adults, Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration,
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
126
109
17
41
72
69
57
125
108
17
41
72
68
57
109
94
15
38
62
58
51
126
109
17
41
72
69
57
125
108
17
41
72
68
57
109
94
15
38
62
58
51
% Detected
27.8
27.5
29.4
29.3
23.6
26.1
29.8
27.2
26.9
29.4
29.3
23.6
25.0
29.8
22.9
23.4
20.0
28.9
19.4
19.0
27.5
27.8
27.5
29.4
29.3
23.6
26.1
29.8
27.2
26.9
29.4
29.3
23.6
25.0
29.8
22.9
23.4
20.0
28.9
19.4
19.0
27.5
Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
a Not detected results are replaced by the method detection limit (MDL) divided by the square root of 2. Multiple sample results for a given
study subject have been log-transformed, averaged, and exponentiated back to regular units prior to summarizing the data within a stratum. This
result is labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     Q-10

-------
Table Q-2d.   1-hydroxybenzralanthracene (69847-26-3): Range of Estimated Urinary
                 Biomarker Concentrations in OH Adults, Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
126
109
17
41
72
69
57
125
108
17
41
72
68
57
109
94
15
38
62
58
51
126
109
17
41
72
69
57
125
108
17
41
72
68
57
109
94
15
38
62
58
51
Minimum

-------
 Table Q-3a.   3-hydroxybenzralanthracene (4834-35-9): Estimated Urinary Biomarker
                 Concentrations in OH Preschool Children, Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration,
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
126
109
17
40
73
69
57
126
109
17
40
73
69
57
111
96
15
38
63
59
52
126
109
17
40
73
69
57
126
109
17
40
73
69
57
111
96
15
38
63
59
52
% Detected
0.8
0.9
0.0
2.5
0.0
0.0
1.8
0.8
0.9
0.0
2.5
0.0
0.0
1.8
0.9
1.0
0.0
2.6
0.0
0.0
1.9
0.8
0.9
0.0
2.5
0.0
0.0
1.8
0.8
0.9
0.0
2.5
0.0
0.0
1.8
0.9
1.0
0.0
2.6
0.0
0.0
1.9
Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
a Not detected results are replaced by the method detection limit (MDL) divided by the square root of 2. Multiple sample results for a given
study subject have been log-transformed, averaged, and exponentiated back to regular units prior to summarizing the data within a stratum. This
result is labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                    Q-12

-------
Table Q-3b.   3-hydroxybenzralanthracene (4834-35-9): Range of Estimated Urinary
                Biomarker Concentrations in OH Preschool Children, Summarized by
                Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
126
109
17
40
73
69
57
126
109
17
40
73
69
57
111
96
15
38
63
59
52
126
109
17
40
73
69
57
126
109
17
40
73
69
57
111
96
15
38
63
59
52
Minimum

-------
Table Q-3c.   3-hydroxybenzralanthracene (4834-35-9):  Estimated Urinary Biomarker
                 Concentrations in OH Adults, Summarized  by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration,
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
126
109
17
41
72
69
57
125
108
17
41
72
68
57
109
94
15
38
62
58
51
126
109
17
41
72
69
57
125
108
17
41
72
68
57
109
94
15
38
62
58
51
% Detected
2.4
2.8
0.0
2.4
2.8
2.9
1.8
2.4
2.8
0.0
2.4
2.8
2.9
1.8
0.9
1.1
0.0
0.0
1.6
0.0
2.0
2.4
2.8
0.0
2.4
2.8
2.9
1.8
2.4
2.8
0.0
2.4
2.8
2.9
1.8
0.9
1.1
0.0
0.0
1.6
0.0
2.0
Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
a Not detected results are replaced by the method detection limit (MDL) divided by the square root of 2. Multiple sample results for a given
study subject have been log-transformed, averaged, and exponentiated back to regular units prior to summarizing the data within a stratum. This
result is labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     Q-14

-------
Table Q-3d.   3-hydroxybenzralanthracene (4834-35-9):  Range of Estimated Urinary
                 Biomarker Concentrations in OH Adults, Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
126
109
17
41
72
69
57
125
108
17
41
72
68
57
109
94
15
38
62
58
51
126
109
17
41
72
69
57
125
108
17
41
72
68
57
109
94
15
38
62
58
51
Minimum

-------
Table Q-4a.   S-hydroxybenzfalpyrene (13345-21 -6): Estimated Urinary Biomarker
                 Concentrations in OH Preschool Children, Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration,
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
126
109
17
40
73
69
57
126
109
17
40
73
69
57
111
96
15
38
63
59
52
126
109
17
40
73
69
57
126
109
17
40
73
69
57
111
96
15
38
63
59
52
% Detected
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
a Not detected results are replaced by the method detection limit (MDL) divided by the square root of 2. Multiple sample results for a given
study subject have been log-transformed, averaged, and exponentiated back to regular units prior to summarizing the data within a stratum.  This
result is labeled as "detected" if any measurement entering into the calculation was detected.  Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     Q-16

-------
Table Q-4b.    S-hydroxybenzfalpyrene (13345-21 -6): Range of Estimated Urinary
                 Biomarker Concentrations in OH Preschool Children, Summarized by
                 Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
126
109
17
40
73
69
57
126
109
17
40
73
69
57
111
96
15
38
63
59
52
126
109
17
40
73
69
57
126
109
17
40
73
69
57
111
96
15
38
63
59
52
Minimum

-------
Table Q-4c.   S-hydroxybenzfalpyrene (13345-21 -6): Estimated Urinary Biomarker
                 Concentrations in OH Adults,  Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration,
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
126
109
17
41
72
69
57
125
108
17
41
72
68
57
109
94
15
38
62
58
51
126
109
17
41
72
69
57
125
108
17
41
72
68
57
109
94
15
38
62
58
51
% Detected
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
a Not detected results are replaced by the method detection limit (MDL) divided by the square root of 2. Multiple sample results for a given
study subject have been log-transformed, averaged, and exponentiated back to regular units prior to summarizing the data within a stratum. This
result is labeled as "detected" if any measurement entering into the calculation was detected.  Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     Q-18

-------
Table Q-4d.   S-hydroxybenzfalpyrene (13345-21 -6): Range of Estimated Urinary
                 Biomarker Concentrations in OH Adults, Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
126
109
17
41
72
69
57
125
108
17
41
72
68
57
109
94
15
38
62
58
51
126
109
17
41
72
69
57
125
108
17
41
72
68
57
109
94
15
38
62
58
51
Minimum

-------
Table Q-5a.   3-hydroxychrysene (63019-39-6): Estimated Urinary Biomarker
                 Concentrations in OH  Preschool Children, Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration,
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
126
109
17
40
73
69
57
126
109
17
40
73
69
57
111
96
15
38
63
59
52
126
109
17
40
73
69
57
126
109
17
40
73
69
57
111
96
15
38
63
59
52
% Detected
1.6
0.9
5.9
0.0
1.4
1.4
1.8
1.6
0.9
5.9
0.0
1.4
1.4
1.8
0.9
1.0
0.0
0.0
1.6
1.7
0.0
1.6
0.9
5.9
0.0
1.4
1.4
1.8
1.6
0.9
5.9
0.0
1.4
1.4
1.8
0.9
1.0
0.0
0.0
1.6
1.7
0.0
Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
a Not detected results are replaced by the method detection limit (MDL) divided by the square root of 2.  Multiple sample results for a given
study subject have been log-transformed, averaged, and exponentiated back to regular units prior to summarizing the data within a stratum. This
result is labeled as "detected" if any measurement entering into the calculation was detected.  Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     Q-20

-------
Table Q-5b.    3-hydroxychrysene (63019-39-6): Range of Estimated Urinary Biomarker
                 Concentrations in OH Preschool Children, Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
126
109
17
40
73
69
57
126
109
17
40
73
69
57
111
96
15
38
63
59
52
126
109
17
40
73
69
57
126
109
17
40
73
69
57
111
96
15
38
63
59
52
Minimum

-------
Table Q-5c.   3-hydroxychrysene (63019-39-6): Estimated Urinary Biomarker
                 Concentrations in OH Adults, Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration,
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
126
109
17
41
72
69
57
125
108
17
41
72
68
57
109
94
15
38
62
58
51
126
109
17
41
72
69
57
125
108
17
41
72
68
57
109
94
15
38
62
58
51
% Detected
0.8
0.9
0.0
0.0
1.4
0.0
1.8
0.8
0.9
0.0
0.0
1.4
0.0
1.8
0.9
1.1
0.0
0.0
1.6
0.0
2.0
0.8
0.9
0.0
0.0
1.4
0.0
1.8
0.8
0.9
0.0
0.0
1.4
0.0
1.8
0.9
1.1
0.0
0.0
1.6
0.0
2.0
Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
a Not detected results are replaced by the method detection limit (MDL) divided by the square root of 2.  Multiple sample results for a given
study subject have been log-transformed, averaged, and exponentiated back to regular units prior to summarizing the data within a stratum. This
result is labeled as "detected" if any measurement entering into the calculation was detected.  Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                      Q-22

-------
Table Q-5d.   3-hydroxychrysene (63019-39-6): Range of Estimated Urinary Biomarker
                 Concentrations in OH Adults, Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
126
109
17
41
72
69
57
125
108
17
41
72
68
57
109
94
15
38
62
58
51
126
109
17
41
72
69
57
125
108
17
41
72
68
57
109
94
15
38
62
58
51
Minimum

-------
Table Q-6a.   6-hydroxychrysene (NA8): Estimated Urinary Biomarker Concentrations in
                 OH Preschool Children, Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration,
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
126
109
17
40
73
69
57
126
109
17
40
73
69
57
111
96
15
38
63
59
52
126
109
17
40
73
69
57
126
109
17
40
73
69
57
111
96
15
38
63
59
52
% Detected
2.4
1.8
5.9
2.5
1.4
0.0
5.3
2.4
1.8
5.9
2.5
1.4
0.0
5.3
1.8
2.1
0.0
2.6
1.6
0.0
3.8
2.4
1.8
5.9
2.5
1.4
0.0
5.3
2.4
1.8
5.9
2.5
1.4
0.0
5.3
1.8
2.1
0.0
2.6
1.6
0.0
3.8
Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
a Not detected results are replaced by the method detection limit (MDL) divided by the square root of 2.  Multiple sample results for a given
study subject have been log-transformed, averaged, and exponentiated back to regular units prior to summarizing the data within a stratum. This
result is labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     Q-24

-------
Table Q-6b.    6-hydroxychrysene (NA8): Range of Estimated Urinary Biomarker
                 Concentrations in OH Preschool Children, Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
126
109
17
40
73
69
57
126
109
17
40
73
69
57
111
96
15
38
63
59
52
126
109
17
40
73
69
57
126
109
17
40
73
69
57
111
96
15
38
63
59
52
Minimum

-------
Table Q-6c.   6-hydroxychrysene (NA8): Estimated Urinary Biomarker Concentrations in
                 OH Adults, Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration,
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
126
109
17
41
72
69
57
125
108
17
41
72
68
57
109
94
15
38
62
58
51
126
109
17
41
72
69
57
125
108
17
41
72
68
57
109
94
15
38
62
58
51
% Detected
0.8
0.9
0.0
0.0
1.4
0.0
1.8
0.8
0.9
0.0
0.0
1.4
0.0
1.8
0.9
1.1
0.0
0.0
1.6
0.0
2.0
0.8
0.9
0.0
0.0
1.4
0.0
1.8
0.8
0.9
0.0
0.0
1.4
0.0
1.8
0.9
1.1
0.0
0.0
1.6
0.0
2.0
Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
a Not detected results are replaced by the method detection limit (MDL) divided by the square root of 2.  Multiple sample results for a given
study subject have been log-transformed, averaged, and exponentiated back to regular units prior to summarizing the data within a stratum. This
result is labeled as "detected" if any measurement entering into the calculation was detected.  Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                      Q-26

-------
Table Q-6d.   6-hydroxychrysene (NA8): Range of Estimated Urinary Biomarker
                 Concentrations in OH Adults, Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
126
109
17
41
72
69
57
125
108
17
41
72
68
57
109
94
15
38
62
58
51
126
109
17
41
72
69
57
125
108
17
41
72
68
57
109
94
15
38
62
58
51
Minimum

-------
Table Q-7a.   6-hydroxy indenori.2.3-cc/lpvrene (NA9): Estimated Urinary Biomarker
                 Concentrations in OH Preschool Children, Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration,
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
126
109
17
40
73
69
57
126
109
17
40
73
69
57
111
96
15
38
63
59
52
126
109
17
40
73
69
57
126
109
17
40
73
69
57
111
96
15
38
63
59
52
% Detected
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
a Not detected results are replaced by the method detection limit (MDL) divided by the square root of 2. Multiple sample results for a given
study subject have been log-transformed, averaged, and exponentiated back to regular units prior to summarizing the data within a stratum. This
result is labeled as "detected" if any measurement entering into the calculation was detected.  Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     Q-28

-------
Table Q-7b.   6-hydroxy indenori.2.3-cc/lpvrene (NA9): Range of Estimated Urinary
                Biomarker Concentrations in OH Preschool Children, Summarized by
                Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
126
109
17
40
73
69
57
126
109
17
40
73
69
57
111
96
15
38
63
59
52
126
109
17
40
73
69
57
126
109
17
40
73
69
57
111
96
15
38
63
59
52
Minimum

-------
Table Q-7c.   6-hydroxy indenori.2.3-cc/lpvrene (NA9): Estimated Urinary Biomarker
                 Concentrations in OH Adults, Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration,
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
125
108
17
41
71
68
57
124
107
17
41
71
67
57
108
93
15
38
61
57
51
125
108
17
41
71
68
57
124
107
17
41
71
67
57
108
93
15
38
61
57
51
% Detected
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
Arithmetic Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Geometric
Mean
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Log Std. Dev.
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
a Not detected results are replaced by the method detection limit (MDL) divided by the square root of 2. Multiple sample results for a given
study subject have been log-transformed, averaged, and exponentiated back to regular units prior to summarizing the data within a stratum.  This
result is labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     Q-30

-------
Table Q-7d.   6-hydroxy indenori.2.3-cc/lpvrene (NA9): Range of Estimated Urinary
                 Biomarker Concentrations in OH Adults, Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
125
108
17
41
71
68
57
124
107
17
41
71
67
57
108
93
15
38
61
57
51
125
108
17
41
71
68
57
124
107
17
41
71
67
57
108
93
15
38
61
57
51
Minimum

-------
Table Q-8a.   1-hydroxypyrene (5315-79-7): Estimated Urinary Biomarker Concentrations
                 in OH Preschool Children, Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration,
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
126
109
17
40
73
69
57
126
109
17
40
73
69
57
111
96
15
38
63
59
52
126
109
17
40
73
69
57
126
109
17
40
73
69
57
111
96
15
38
63
59
52
% Detected
79.4
79.8
76.5
82.5
80.8
73.9
86.0
79.4
79.8
76.5
82.5
80.8
73.9
86.0
77.5
78.1
73.3
81.6
77.8
71.2
84.6
79.4
79.8
76.5
82.5
80.8
73.9
86.0
79.4
79.8
76.5
82.5
80.8
73.9
86.0
77.5
78.1
73.3
81.6
77.8
71.2
84.6
Arithmetic Mean
0.382
0.360
0.519
0.404
0.392
0.409
0.348
0.374
0.353
0.508
0.395
0.384
0.400
0.342
0.542
0.503
0.790
0.532
0.556
0.586
0.493
1.75
1.65
2.38
1.85
1.79
1.87
1.60
1.71
1.62
2.33
1.81
1.76
1.83
1.57
0.281
0.261
0.409
0.275
0.288
0.303
0.255
Std. Dev.
0.316
0.240
0.608
0.273
0.355
0.368
0.238
0.308
0.234
0.592
0.266
0.346
0.359
0.232
0.447
0.286
0.969
0.325
0.529
0.540
0.309
1.45
1.10
2.78
1.25
1.63
1.69
1.09
1.41
1.07
2.71
1.22
1.58
1.65
1.06
0.232
0.148
0.502
0.168
0.274
0.280
0.160
Geometric
Mean
0.305
0.297
0.358
0.333
0.307
0.315
0.293
0.299
0.292
0.351
0.327
0.302
0.309
0.289
0.443
0.431
0.526
0.451
0.444
0.467
0.417
1.40
1.36
1.64
1.53
1.41
1.45
1.34
1.37
1.34
1.61
1.50
1.39
1.41
1.32
0.229
0.223
0.273
0.234
0.230
0.242
0.216
Log Std. Dev.
0.644
0.614
0.816
0.622
0.662
0.702
0.569
0.642
0.612
0.814
0.621
0.659
0.700
0.566
0.618
0.572
0.864
0.578
0.637
0.654
0.574
0.644
0.614
0.816
0.622
0.662
0.702
0.569
0.642
0.612
0.814
0.621
0.659
0.700
0.566
0.618
0.572
0.864
0.578
0.637
0.654
0.574
a Not detected results are replaced by the method detection limit (MDL) divided by the square root of 2. Multiple sample results for a given
study subject have been log-transformed, averaged, and exponentiated back to regular units prior to summarizing the data within a stratum. This
result is labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     Q-32

-------
Table Q-8b.   1-hydroxypyrene (5315-79-7): Range of Estimated Urinary Biomarker
                 Concentrations in OH Preschool Children, Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
126
109
17
40
73
69
57
126
109
17
40
73
69
57
111
96
15
38
63
59
52
126
109
17
40
73
69
57
126
109
17
40
73
69
57
111
96
15
38
63
59
52
Minimum

-------
Table Q-8c.   1-hydroxypyrene (5315-79-7): Estimated Urinary Biomarker Concentrations
                 in OH Adults, Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration,
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
126
109
17
41
72
69
57
125
108
17
41
72
68
57
109
94
15
38
62
58
51
126
109
17
41
72
69
57
125
108
17
41
72
68
57
109
94
15
38
62
58
51
% Detected
69.0
68.8
70.6
78.0
62.5
69.6
68.4
68.8
68.5
70.6
78.0
62.5
69.1
68.4
67.0
67.0
66.7
76.3
61.3
67.2
66.7
69.0
68.8
70.6
78.0
62.5
69.6
68.4
68.8
68.5
70.6
78.0
62.5
69.1
68.4
67.0
67.0
66.7
76.3
61.3
67.2
66.7
Arithmetic Mean
0.322
0.308
0.412
0.343
0.315
0.331
0.312
0.313
0.299
0.404
0.335
0.307
0.320
0.304
0.253
0.246
0.299
0.241
0.272
0.289
0.212
1.48
1.41
1.89
1.57
1.44
1.52
1.43
1.43
1.37
1.85
1.54
1.41
1.47
1.39
0.131
0.127
0.155
0.125
0.141
0.150
0.110
Std. Dev.
0.218
0.199
0.305
0.219
0.230
0.214
0.223
0.213
0.194
0.299
0.215
0.225
0.210
0.218
0.181
0.180
0.187
0.160
0.198
0.197
0.154
0.998
0.913
1.40
1.00
1.05
0.982
1.02
0.976
0.889
1.37
0.983
1.03
0.963
0.999
0.094
0.093
0.097
0.083
0.103
0.102
0.080
Geometric
Mean
0.267
0.260
0.318
0.289
0.255
0.277
0.255
0.259
0.252
0.312
0.282
0.249
0.268
0.249
0.203
0.198
0.235
0.197
0.219
0.240
0.168
1.22
1.19
1.46
1.33
1.17
1.27
1.17
1.19
1.15
1.43
1.29
1.14
1.23
1.14
0.105
0.103
0.121
0.102
0.113
0.124
0.087
Log Std. Dev.
0.601
0.571
0.766
0.590
0.631
0.586
0.621
0.600
0.568
0.767
0.590
0.630
0.584
0.621
0.679
0.661
0.797
0.661
0.682
0.613
0.705
0.601
0.571
0.766
0.590
0.631
0.586
0.621
0.600
0.568
0.767
0.590
0.630
0.584
0.621
0.679
0.661
0.797
0.661
0.682
0.613
0.705
a Not detected results are replaced by the method detection limit (MDL) divided by the square root of 2. Multiple sample results for a given
study subject have been log-transformed, averaged, and exponentiated back to regular units prior to summarizing the data within a stratum. This
result is labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                      Q-34

-------
Table Q-8d.   1-hydroxypyrene (5315-79-7): Range of Estimated Urinary Biomarker
                 Concentrations in OH Adults, Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
126
109
17
41
72
69
57
125
108
17
41
72
68
57
109
94
15
38
62
58
51
126
109
17
41
72
69
57
125
108
17
41
72
68
57
109
94
15
38
62
58
51
Minimum

-------
Table Q-9a.   Pentachlorophenol (87-86-5): Estimated Urinary Biomarker Concentrations
                 in OH Preschool Children, Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration,
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
126
109
17
40
73
69
57
126
109
17
40
73
69
57
111
96
15
38
63
59
52
126
109
17
40
73
69
57
126
109
17
40
73
69
57
111
96
15
38
63
59
52
% Detected
99.2
99.1
100.0
100.0
98.6
98.6
100.0
99.2
99.1
100.0
100.0
98.6
98.6
100.0
99.1
99.0
100.0
100.0
98.4
98.3
100.0
99.2
99.1
100.0
100.0
98.6
98.6
100.0
99.2
99.1
100.0
100.0
98.6
98.6
100.0
99.1
99.0
100.0
100.0
98.4
98.3
100.0
Arithmetic Mean
1.27
1.23
1.52
1.05
1.47
1.54
0.946
1.24
1.20
1.49
1.03
1.44
1.50
0.926
1.73
1.65
2.25
1.37
2.01
2.10
1.31
4.77
4.62
5.72
3.94
5.53
5.78
3.55
4.67
4.52
5.59
3.86
5.41
5.65
3.48
0.734
0.700
0.954
0.581
0.852
0.893
0.555
Std. Dev.
2.20
2.32
1.19
0.884
2.80
2.89
0.638
2.14
2.26
1.16
0.863
2.73
2.82
0.624
2.19
2.26
1.65
1.05
2.76
2.87
0.823
8.25
8.70
4.46
3.32
10.5
10.9
2.40
8.05
8.48
4.35
3.24
10.2
10.6
2.34
0.931
0.960
0.701
0.444
1.17
1.22
0.349
Geometric
Mean
0.876
0.830
1.25
0.797
0.959
0.993
0.753
0.859
0.813
1.22
0.781
0.939
0.972
0.739
1.27
1.19
1.86
1.07
1.43
1.48
1.07
3.29
3.12
4.68
2.99
3.60
3.73
2.83
3.22
3.05
4.59
2.93
3.53
3.65
2.77
0.538
0.507
0.789
0.452
0.608
0.627
0.452
Log Std. Dev.
0.765
0.773
0.618
0.750
0.797
0.800
0.698
0.764
0.772
0.615
0.749
0.795
0.798
0.697
0.749
0.755
0.604
0.731
0.761
0.785
0.672
0.765
0.773
0.618
0.750
0.797
0.800
0.698
0.764
0.772
0.615
0.749
0.795
0.798
0.697
0.749
0.755
0.604
0.731
0.761
0.785
0.672
a Not detected results are replaced by the method detection limit (MDL) divided by the square root of 2. Multiple sample results for a given
study subject have been log-transformed, averaged, and exponentiated back to regular units prior to summarizing the data within a stratum. This
result is labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     Q-36

-------
Table Q-9b.   Pentachlorophenol (87-86-5): Range of Estimated Urinary Biomarker
                 Concentrations in OH Preschool Children, Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
126
109
17
40
73
69
57
126
109
17
40
73
69
57
111
96
15
38
63
59
52
126
109
17
40
73
69
57
126
109
17
40
73
69
57
111
96
15
38
63
59
52
Minimum

-------
Table Q-9c.   Pentachlorophenol (87-86-5): Estimated Urinary Biomarker Concentrations
                 in OH Adults, Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration,
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
126
109
17
41
72
69
57
125
108
17
41
72
68
57
109
94
15
38
62
58
51
126
109
17
41
72
69
57
125
108
17
41
72
68
57
109
94
15
38
62
58
51
% Detected
96.0
95.4
100.0
97.6
94.4
95.7
96.5
96.0
95.4
100.0
97.6
94.4
95.6
96.5
95.4
94.7
100.0
97.4
93.5
94.8
96.1
96.0
95.4
100.0
97.6
94.4
95.7
96.5
96.0
95.4
100.0
97.6
94.4
95.6
96.5
95.4
94.7
100.0
97.4
93.5
94.8
96.1
Arithmetic Mean
0.776
0.742
0.990
0.740
0.764
0.712
0.853
0.757
0.723
0.970
0.723
0.747
0.693
0.833
0.650
0.628
0.789
0.508
0.748
0.638
0.664
2.91
2.79
3.72
2.78
2.87
2.67
3.20
2.84
2.72
3.64
2.71
2.80
2.60
3.13
0.276
0.267
0.335
0.216
0.317
0.271
0.282
Std. Dev.
0.715
0.700
0.795
0.619
0.763
0.608
0.825
0.701
0.686
0.779
0.603
0.746
0.596
0.807
0.879
0.905
0.707
0.446
1.07
0.766
1.00
2.68
2.63
2.98
2.32
2.87
2.28
3.10
2.63
2.57
2.93
2.27
2.80
2.24
3.03
0.373
0.384
0.300
0.189
0.456
0.325
0.425
Geometric
Mean
0.575
0.550
0.769
0.569
0.550
0.551
0.606
0.560
0.534
0.752
0.556
0.538
0.534
0.592
0.433
0.415
0.569
0.388
0.471
0.465
0.400
2.16
2.06
2.89
2.14
2.07
2.07
2.27
2.10
2.01
2.82
2.09
2.02
2.01
2.22
0.184
0.176
0.241
0.164
0.200
0.197
0.169
Log Std. Dev.
0.746
0.742
0.722
0.709
0.772
0.704
0.797
0.747
0.743
0.723
0.708
0.772
0.705
0.797
0.806
0.800
0.815
0.724
0.851
0.704
0.909
0.746
0.742
0.722
0.709
0.772
0.704
0.797
0.747
0.743
0.723
0.708
0.772
0.705
0.797
0.806
0.800
0.815
0.724
0.851
0.704
0.909
a Not detected results are replaced by the method detection limit (MDL) divided by the square root of 2. Multiple sample results for a given
study subject have been log-transformed, averaged, and exponentiated back to regular units prior to summarizing the data within a stratum.  This
result is labeled as "detected" if any measurement entering into the calculation was detected. Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                      Q-38

-------
Table Q-9d.   Pentachlorophenol (87-86-5): Range of Estimated Urinary Biomarker
                 Concentrations in OH Adults, Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
126
109
17
41
72
69
57
125
108
17
41
72
68
57
109
94
15
38
62
58
51
126
109
17
41
72
69
57
125
108
17
41
72
68
57
109
94
15
38
62
58
51
Minimum

-------
Table Q-10a.  3-phenoxybenzoic acid (3739-38-6): Estimated Urinary Biomarker
                 Concentrations in OH Preschool  Children, Summarized  by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration,
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
126
109
17
40
73
69
57
126
109
17
40
73
69
57
111
96
15
38
63
59
52
126
109
17
40
73
69
57
126
109
17
40
73
69
57
111
96
15
38
63
59
52
% Detected
73.0
73.4
70.6
82.5
67.1
65.2
82.5
73.0
73.4
70.6
82.5
67.1
65.2
82.5
70.3
70.8
66.7
81.6
63.5
61.0
80.8
73.0
73.4
70.6
82.5
67.1
65.2
82.5
73.0
73.4
70.6
82.5
67.1
65.2
82.5
70.3
70.8
66.7
81.6
63.5
61.0
80.8
Arithmetic Mean
0.689
0.743
0.343
0.565
0.806
0.478
0.944
0.674
0.726
0.336
0.554
0.787
0.468
0.922
1.40
1.53
0.584
0.884
1.79
0.812
2.07
3.21
3.47
1.60
2.64
3.76
2.23
4.40
3.14
3.39
1.57
2.59
3.68
2.19
4.30
0.739
0.806
0.308
0.466
0.944
0.428
1.09
Std. Dev.
2.49
2.68
0.248
0.615
3.25
0.529
3.66
2.44
2.62
0.242
0.605
3.18
0.519
3.59
6.38
6.85
0.564
1.67
8.37
1.00
9.26
11.6
12.5
1.16
2.87
15.1
2.47
17.1
11.4
12.2
1.13
2.82
14.9
2.42
16.8
3.37
3.61
0.297
0.883
4.42
0.528
4.89
Geometric
Mean
0.310
0.316
0.273
0.367
0.287
0.292
0.334
0.301
0.306
0.268
0.360
0.277
0.286
0.321
0.456
0.463
0.410
0.474
0.428
0.443
0.471
1.45
1.48
1.28
1.72
1.34
1.36
1.56
1.41
1.43
1.25
1.68
1.29
1.33
1.50
0.240
0.244
0.216
0.250
0.226
0.233
0.249
Log Std. Dev.
1.01
1.05
0.697
0.907
1.07
0.983
1.05
1.02
1.06
0.697
0.906
1.09
0.983
1.07
1.15
1.20
0.862
1.01
1.26
1.11
1.22
1.01
1.05
0.697
0.907
1.07
0.983
1.05
1.02
1.06
0.697
0.906
1.09
0.983
1.07
1.15
1.20
0.862
1.01
1.26
1.11
1.22
a Not detected results are replaced by the method detection limit (MDL) divided by the square root of 2. Multiple sample results for a given
study subject have been log-transformed, averaged, and exponentiated back to regular units prior to summarizing the data within a stratum. This
result is labeled as "detected" if any measurement entering into the calculation was detected.  Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     Q-40

-------
Table Q-10b.  3-phenoxybenzoic acid (3739-38-6): Range of Estimated Urinary Biomarker
                 Concentrations in OH Preschool Children, Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
126
109
17
40
73
69
57
126
109
17
40
73
69
57
111
96
15
38
63
59
52
126
109
17
40
73
69
57
126
109
17
40
73
69
57
111
96
15
38
63
59
52
Minimum

-------
Table Q-10c.  3-phenoxybenzoic acid (3739-38-6): Estimated Urinary Biomarker
                 Concentrations in OH Adults,  Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration,
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
124
107
17
40
71
68
56
123
106
17
40
71
67
56
107
92
15
37
61
57
50
124
107
17
40
71
68
56
123
106
17
40
71
67
56
107
92
15
37
61
57
50
% Detected
66.1
68.2
52.9
60.0
64.8
61.8
71.4
65.9
67.9
52.9
60.0
64.8
61.2
71.4
62.6
65.2
46.7
56.8
62.3
57.9
68.0
66.1
68.2
52.9
60.0
64.8
61.8
71.4
65.9
67.9
52.9
60.0
64.8
61.2
71.4
62.6
65.2
46.7
56.8
62.3
57.9
68.0
Arithmetic Mean
0.580
0.619
0.334
0.612
0.548
0.438
0.752
0.569
0.608
0.327
0.597
0.537
0.431
0.735
0.487
0.526
-
0.462
0.514
0.447
0.533
2.71
2.89
1.56
2.86
2.56
2.04
3.51
2.66
2.84
1.53
2.79
2.51
2.01
3.43
0.257
0.277
-
0.244
0.271
0.236
0.281
Std. Dev.
0.802
0.848
0.331
0.865
0.817
0.630
0.948
0.788
0.834
0.324
0.841
0.804
0.624
0.928
0.723
0.765
-
0.708
0.778
0.741
0.706
3.74
3.96
1.54
4.04
3.81
2.94
4.43
3.68
3.89
1.51
3.93
3.75
2.91
4.33
0.381
0.403
-
0.373
0.411
0.391
0.373
Geometric
Mean
0.322
0.338
0.238
0.337
0.291
0.261
0.414
0.315
0.331
0.233
0.329
0.284
0.256
0.404
0.244
0.262
-
0.221
0.252
0.230
0.262
1.50
1.58
1.11
1.57
1.36
1.22
1.93
1.47
1.54
1.09
1.54
1.33
1.19
1.89
0.129
0.138
-
0.116
0.133
0.121
0.138
Log Std. Dev.
1.05
1.07
0.818
1.05
1.07
0.961
1.10
1.05
1.08
0.818
1.05
1.07
0.969
1.10
1.16
1.18
-
1.18
1.20
1.11
1.22
1.05
1.07
0.818
1.05
1.07
0.961
1.10
1.05
1.08
0.818
1.05
1.07
0.969
1.10
1.16
1.18
-
1.18
1.20
1.11
1.22
a Not detected results are replaced by the method detection limit (MDL) divided by the square root of 2. Multiple sample results for a given
study subject have been log-transformed, averaged, and exponentiated back to regular units prior to summarizing the data within a stratum. This
result is labeled as "detected" if any measurement entering into the calculation was detected.  Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     Q-42

-------
Table Q-10d.  3-phenoxybenzoic acid (3739-38-6): Range of Estimated Urinary Biomarker
                 Concentrations in OH Adults, Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
124
107
17
40
71
68
56
123
106
17
40
71
67
56
107
92
15
37
61
57
50
124
107
17
40
71
68
56
123
106
17
40
71
67
56
107
92
15
37
61
57
50
Minimum

-------
Table Q-11a.  3.5.6-TCP (3.5.6-trichloro-2-pyridinol) (6515-38-4): Estimated Urinary
                 Biomarker Concentrations in OH Preschool Children, Summarized by
                 Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration,
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
122
107
15
40
70
67
55
122
107
15
40
70
67
55
106
93
13
37
60
57
49
122
107
15
40
70
67
55
122
107
15
40
70
67
55
106
93
13
37
60
57
49
% Detected
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
Arithmetic Mean
5.61
5.68
5.08
5.68
5.69
6.05
5.06
5.50
5.58
4.97
5.56
5.60
5.92
5.00
7.69
7.74
7.35
7.16
8.18
8.46
6.80
28.2
28.6
25.6
28.6
28.7
30.5
25.5
27.7
28.1
25.1
28.0
28.2
29.8
25.2
4.38
4.41
4.19
4.08
4.66
4.81
3.87
Std. Dev.
3.38
3.43
3.07
3.11
3.59
3.73
2.84
3.34
3.39
3.01
3.04
3.56
3.65
2.87
4.29
4.36
3.91
3.88
4.73
4.50
3.90
17.1
17.3
15.5
15.7
18.1
18.8
14.3
16.8
17.1
15.2
15.3
17.9
18.4
14.5
2.44
2.48
2.23
2.21
2.69
2.56
2.22
Geometric
Mean
4.64
4.71
4.21
4.89
4.60
4.90
4.34
4.56
4.62
4.13
4.79
4.52
4.80
4.27
6.52
6.57
6.20
6.32
6.68
7.13
5.88
23.4
23.7
21.2
24.6
23.2
24.7
21.9
23.0
23.3
20.8
24.1
22.8
24.2
21.5
3.71
3.74
3.53
3.60
3.80
4.06
3.35
Log Std. Dev.
0.636
0.634
0.658
0.570
0.683
0.687
0.565
0.637
0.636
0.657
0.568
0.686
0.686
0.571
0.604
0.599
0.661
0.504
0.692
0.637
0.551
0.636
0.634
0.658
0.570
0.683
0.687
0.565
0.637
0.636
0.657
0.568
0.686
0.686
0.571
0.604
0.599
0.661
0.504
0.692
0.637
0.551
a Not detected results are replaced by the method detection limit (MDL) divided by the square root of 2. Multiple sample results for a given
study subject have been log-transformed, averaged, and exponentiated back to regular units prior to summarizing the data within a stratum.  This
result is labeled as "detected" if any measurement entering into the calculation was detected.  Thus, N specifies the number of subjects having
data entering into the summaries. Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     Q-44

-------
Table Q-11b.  3.5.6-TCP (3.5.6-trichloro-2-pyridinol) (6515-38-4): Range of Estimated
                 Urinary Biomarker Concentrations in OH Preschool Children, Summarized
                 by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
122
107
15
40
70
67
55
122
107
15
40
70
67
55
106
93
13
37
60
57
49
122
107
15
40
70
67
55
122
107
15
40
70
67
55
106
93
13
37
60
57
49
Minimum
1.18
1.18
1.38
1.23
1.18
1.18
1.38
1.15
1.15
1.35
1.21
1.15
1.15
1.35
1.31
1.31
1.79
1.76
1.31
1.31
1.72
5.95
5.95
6.95
6.20
5.95
5.95
6.95
5.80
5.80
6.82
6.11
5.80
5.80
6.82
0.747
0.747
1.02
1.00
0.747
0.747
0.981
25th
Percentile
2.87
2.90
2.08
3.38
2.73
3.01
2.68
2.82
2.84
2.03
3.30
2.66
2.97
2.62
4.25
4.25
5.25
4.25
4.02
5.21
4.04
14.4
14.6
10.5
17.0
13.8
15.2
13.5
14.2
14.3
10.3
16.6
13.4
14.9
13.2
2.42
2.42
2.99
2.42
2.29
2.97
2.30
50th
Percentile
5.07
4.79
5.28
5.15
5.12
5.28
4.43
4.96
4.68
5.18
5.04
5.03
5.18
4.32
6.74
6.49
7.04
6.10
7.49
7.65
5.80
25.6
24.1
26.6
26.0
25.8
26.6
22.3
25.0
23.6
26.1
25.4
25.3
26.1
21.8
3.84
3.70
4.01
3.47
4.27
4.36
3.30
75th
Percentile
7.33
7.50
6.12
7.42
7.78
9.08
6.88
7.17
7.32
6.00
7.24
7.63
8.82
6.78
10.4
10.3
10.4
8.27
11.7
11.7
8.21
37.0
37.8
30.9
37.4
39.2
45.8
34.7
36.1
36.9
30.3
36.5
38.4
44.4
34.2
5.95
5.85
5.95
4.71
6.67
6.67
4.67
95th
Percentile
12.3
12.8
12.3
12.0
12.3
12.9
11.2
12.1
12.6
12.1
11.8
12.1
12.6
11.6
16.1
17.8
14.1
17.8
17.0
17.8
14.1
62.2
64.5
62.2
60.4
62.2
65.1
56.3
61.1
63.4
61.1
59.3
61.1
63.7
58.6
9.20
10.1
8.04
10.2
9.66
10.1
8.04
Maximum
15.3
15.3
12.3
14.1
15.3
15.3
12.8
14.9
14.9
12.1
13.8
14.9
14.9
12.6
20.1
20.1
14.1
19.2
20.1
19.2
20.1
77.2
77.2
62.2
71.2
77.2
77.2
64.5
75.3
75.3
61.1
69.5
75.3
75.3
63.6
11.4
11.4
8.04
10.9
11.4
10.9
11.4
a For a given study subject, multiple sample results have been log-transformed (after replacing not detected results by the method detection limit
(MDL) divided by the square root of 2), averaged, and exponentiated back to regular units prior to summarizing the data within a stratum. This
result is labeled as "detected" if any measurement entering into the calculation was detected.  Thus, N specifies the number of subjects having
data entering into the summaries.
                                                   Q-45

-------
Table Q-11c.  3.5.6-TCP (3.5.6-trichloro-2-pyridinol) (6515-38-4): Estimated  Urinary
                 Biomarker Concentrations in OH Adults, Summarized  by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration,
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
126
109
17
41
72
69
57
125
108
17
41
72
68
57
109
94
15
38
62
58
51
126
109
17
41
72
69
57
125
108
17
41
72
68
57
109
94
15
38
62
58
51
% Detected
97.6
99.1
88.2
100.0
97.2
98.6
96.5
97.6
99.1
88.2
100.0
97.2
98.5
96.5
97.2
98.9
86.7
100.0
96.8
98.3
96.1
97.6
99.1
88.2
100.0
97.2
98.6
96.5
97.6
99.1
88.2
100.0
97.2
98.5
96.5
97.2
98.9
86.7
100.0
96.8
98.3
96.1
Arithmetic Mean
4.75
5.01
3.06
4.57
4.33
5.12
4.29
4.65
4.92
3.00
4.46
4.23
5.05
4.19
3.55
3.79
2.02
2.84
3.92
4.44
2.54
23.9
25.2
15.4
23.0
21.8
25.8
21.6
23.5
24.8
15.1
22.5
21.3
25.4
21.1
2.02
2.16
1.15
1.62
2.23
2.53
1.45
Std. Dev.
4.47
4.65
2.66
4.53
3.46
4.89
3.91
4.38
4.55
2.59
4.46
3.37
4.78
3.84
3.92
4.15
1.25
2.55
4.44
4.99
1.72
22.5
23.4
13.4
22.8
17.5
24.6
19.7
22.1
22.9
13.1
22.5
17.0
24.1
19.3
2.23
2.36
0.709
1.45
2.53
2.84
0.981
Geometric
Mean
3.51
3.73
2.37
3.38
3.36
3.69
3.30
3.44
3.67
2.32
3.30
3.29
3.64
3.23
2.53
2.69
1.69
2.16
2.78
3.02
2.06
17.7
18.8
11.9
17.0
17.0
18.6
16.6
17.4
18.5
11.7
16.6
16.6
18.3
16.3
1.44
1.53
0.963
1.23
1.58
1.72
1.18
Log Std. Dev.
0.756
0.746
0.718
0.745
0.708
0.793
0.710
0.756
0.746
0.718
0.745
0.706
0.794
0.709
0.783
0.786
0.645
0.727
0.772
0.834
0.672
0.756
0.746
0.718
0.745
0.708
0.793
0.710
0.756
0.746
0.718
0.745
0.706
0.794
0.709
0.783
0.786
0.645
0.727
0.772
0.834
0.672
a Not detected results are replaced by the method detection limit (MDL) divided by the square root of 2. Multiple sample results for a given
study subject have been log-transformed, averaged, and exponentiated back to regular units prior to summarizing the data within a stratum. This
result is labeled as "detected" if any measurement entering into the calculation was detected.  Thus, N specifies the number of subjects having
data entering into the summaries.  Means and standard deviations are not reported when the percentage of detected results is below 50%.
                                                     Q-46

-------
Table Q-11d.  3.5.6-TCP (3.5.6-trichloro-2-pyridinol) (6515-38-4): Range of Estimated
                 Urinary Biomarker Concentrations in OH Adults, Summarized by Strata3
Biomarker
Concentration
Parameter
Urinary
concentration
(ng/mL)
Urinary
concentration,
adjusted for
specific gravity
(ng/mL)
Urinary
concentration
adjusted for
creatinine
(ng/mg)
Urinary
concentration
(pmoles/mL)
Urinary
concentration,
adjusted for
specific gravity
(pmoles/mL)
Urinary
concentration,
adjusted for
creatinine
(umoles/mole)
Strata
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
Overall
Urban
Rural
Low Income
Mid/High Income
Home Children
Day Care Children
N
126
109
17
41
72
69
57
125
108
17
41
72
68
57
109
94
15
38
62
58
51
126
109
17
41
72
69
57
125
108
17
41
72
68
57
109
94
15
38
62
58
51
Minimum

-------

-------
                                 Appendix R
 Detailed Results of Statistical Analyses Performed on Potential Exposure Level and
Potential Absorbed Dose Estimates and on Urinary Biomarker Concentrations for the
                              Study Participants
                                     R-l

-------
R-2

-------
Table R-l.    Estimated Ratio Between Selected Strata of Geometric Mean Potential
             Exposure and Potential Absorbed Dose Estimates in Participating NC
             Children, and 95% Confidence Intervals on This Ratio
Exposure/Dose/Biomarker Parameter
and Pathway
Estimated Ratio of Geometric Means (95% CI)
Urban vs. Rural
Low Income vs.
Mid/High Income
Day Care vs.
Home Children
Benz[a] anthracene
Potential Exposure via Inhalation
Potential Exposure via Dietary Ingestiona
Potential Exposure via Indirect Ingestion
Potential Absorbed Dose via Inhalation
Potential Absorbed Dose via Dietary Ingestion a
Potential Absorbed Dose via Indirect Ingestion
1.50 (0.88,2.54)
~
0.88 (0.42,1.84)
1.66 (0.94,2.91)
~
0.95 (0.44,2.04)
1.38(0.99,1.92)
~
0.66(0.39,1.14)
1.34(0.94,1.91)
~
0.61 (0.35,1.07)
0.85 (0.52,1.40)
~
1.72(0.93,3.19)
0.74 (0.44,1.25)
~
1.53 (0.80,2.91)
Benzo [AJfluoranthene
Potential Exposure via Inhalation
Potential Exposure via Dietary Ingestion a
Potential Exposure via Indirect Ingestion
Potential Absorbed Dose via Inhalation
Potential Absorbed Dose via Dietary Ingestion a
Potential Absorbed Dose via Indirect Ingestion
1.44 (0.85,2.45)
-
0.93 (0.45,1.89)
1.59(0.91,2.78)
-
0.99 (0.47,2.09)
1.58* (1.12,2.24)
-
0.74(0.44,1.27)
1.52* (1.04,2.21)
-
0.68(0.39,1.19)
1.08 (0.66,1.76)
-
1.81* (1.01,3.23)
0.94(0.57,1.57)
-
1.60 (0.87,2.95)
Benzo [AJfluoranthene
Potential Exposure via Inhalation
Potential Exposure via Dietary Ingestion a
Potential Exposure via Indirect Ingestion
Potential Absorbed Dose via Inhalation
Potential Absorbed Dose via Dietary Ingestion a
Potential Absorbed Dose via Indirect Ingestion
1.14(0.84,1.56)
-
0.83 (0.40,1.72)
1.26(0.88,1.80)
-
0.89(0.42,1.91)
1.25* (1.02,1. 53)
-
0.70(0.41,1.19)
1.20(0.95,1.53)
-
0.64(0.36,1.12)
1.01 (0.76,1.35)
-
1.72(0.94,3.15)
0.88 (0.64,1.22)
-
1.53 (0.81,2.88)
Benzo |#/»']perylene
Potential Exposure via Inhalation
Potential Exposure via Dietary Ingestion a
Potential Exposure via Indirect Ingestion
Potential Absorbed Dose via Inhalation
Potential Absorbed Dose via Dietary Ingestion a
Potential Absorbed Dose via Indirect Ingestion
1.31(0.78,2.21)
~
0.96 (0.48,1.90)
1.45 (0.83,2.54)
~
1.03(0.50,2.11)
1.33 (0.96,1.83)
~
0.72(0.43,1.19)
1.30(0.91,1.84)
~
0.66(0.38,1.12)
0.96(0.59,1.58)
~
1.60 (0.92,2.80)
0.84 (0.50,1.42)
~
1.42 (0.79,2.56)
Benzo [a]pyrene
Potential Exposure via Inhalation
Potential Exposure via Dietary Ingestion a
Potential Exposure via Indirect Ingestion
Potential Absorbed Dose via Inhalation
Potential Absorbed Dose via Dietary Ingestion a
Potential Absorbed Dose via Indirect Ingestion
1.18(0.74,1.87)
~
0.97(0.48,1.99)
1.29(0.79,2.11)
~
1.04 (0.49,2.21)
1.57** (1.13,2.19)
~
0.68(0.40,1.15)
1.51* (1.06,2.15)
~
0.62(0.36,1.08)
1.03 (0.69,1.54)
~
1.65 (0.91,3.00)
0.90(0.59,1.37)
~
1.46 (0.78,2.74)
                                        R-3

-------
Table R-l.    Estimated Ratio Between Selected Strata of Geometric Mean Potential
             Exposure and Potential Absorbed Dose Estimates in Participating NC
             Children, and 95% Confidence Intervals on This Ratio (cont.)
Exposure/Dose/Biomarker Parameter
and Pathway
Estimated Ratio of Geometric Means (95% CI)
Urban vs. Rural
Low Income vs.
Mid/High Income
Day Care vs.
Home Children
Benzo[e]pyrene
Potential Exposure via Inhalation
Potential Exposure via Dietary Ingestion3
Potential Exposure via Indirect Ingestion
Potential Absorbed Dose via Inhalation
Potential Absorbed Dose via Dietary Ingestion a
Potential Absorbed Dose via Indirect Ingestion
1.15(0.81,1.65)
~
0.89 (0.44,1.79)
1.27 (0.86,1.87)
-
0.95 (0.46,1.99)
1.36* (1.07,1.74)
~
0.74(0.44,1.24)
1.31* (1.00,1.72)
-
0.68(0.39,1.17)
1.05 (0.76,1.45)
~
1.67 (0.94,2.96)
0.92(0.65,1.29)
-
1.48(0.81,2.71)
Benzylbutylphthalate
Potential Exposure via Inhalation3
Potential Exposure via Dietary Ingestion a
Potential Exposure via Indirect Ingestion
Potential Absorbed Dose via Inhalation3
Potential Absorbed Dose via Dietary Ingestion3
Potential Absorbed Dose via Indirect Ingestion
-
~
0.54(0.25,1.19)
-
~
0.57(0.25,1.30)
-
~
1.55 (0.88,2.75)
-
~
1.35 (0.74,2.45)
-
~
1.49 (0.80,2.79)
-
~
1.33 (0.68,2.63)
Bisphenol-A
Potential Exposure via Inhalation
Potential Exposure via Dietary Ingestion
Potential Exposure via Indirect Ingestion b
Potential Absorbed Dose via Inhalation
Potential Absorbed Dose via Dietary Ingestion
Potential Absorbed Dose via Indirect Ingestionb
Aggregated Potential Exposure
Aggregated Potential Absorbed Dose
1.03 (0.57,1.86)
0.68(0.38,1.20)
0.83 (0.41,1.66)
1.14(0.61,2.12)
0.73 (0.41,1.32)
0.84(0.41,1.73)
0.68(0.41,1.12)
0.73 (0.44,1.22)
1.33 (0.91,1.93)
0.90(0.60,1.35)
0.76(0.45,1.28)
1.28(0.85,1.91)
0.84(0.56,1.28)
0.65 (0.38,1.12)
0.87(0.58,1.31)
0.82(0.54,1.25)
0.81 (0.47,1.41)
2.47** (1.54,3.96)
1.16(0.70,1.92)
0.71 (0.40,1.27)
2.19** (1.36,3. 53)
1.05(0.57,1.91)
2.12** (1.42,3. 17)
1.85** (1.23,2.79)
a^oAa-Chlordane
Potential Exposure via Inhalation
Potential Exposure via Dietary Ingestion 3
Potential Exposure via Indirect Ingestion
Potential Absorbed Dose via Inhalation
Potential Absorbed Dose via Dietary Ingestion3
Potential Absorbed Dose via Indirect Ingestion
0.77(0.35,1.68)
~
0.66 (0.27,1.63)
0.84(0.38,1.88)
-
0.72(0.28,1.85)
1.36 (0.78,2.38)
~
0.84(0.44,1.57)
1.30(0.73,2.31)
-
0.76(0.39,1.46)
1.33 (0.67,2.61)
~
1.79 (0.80,3.98)
1.16(0.58,2.32)
-
1.58(0.68,3.65)
gamma-Chlordaae
Potential Exposure via Inhalation
Potential Exposure via Dietary Ingestion3
0.78(0.34,1.78)
~
1.43 (0.80,2.56)
~
1.36 (0.66,2.80)
~
                                        R-4

-------
Table R-l.    Estimated Ratio Between Selected Strata of Geometric Mean Potential
             Exposure and Potential Absorbed Dose Estimates in Participating NC
             Children, and 95% Confidence Intervals on This Ratio (cont.)
Exposure/Dose/Biomarker Parameter
and Pathway
Potential Exposure via Indirect Ingestion
Potential Absorbed Dose via Inhalation
Potential Absorbed Dose via Dietary Ingestion a
Potential Absorbed Dose via Indirect Ingestion
Estimated Ratio of Geometric Means (95% CI)
Urban vs. Rural
0.68 (0.27,1.75)
0.85 (0.37,1.97)
~
0.74 (0.28,1.96)
Low Income vs.
Mid/High Income
0.83 (0.43,1.58)
1.36 (0.75,2.47)
~
0.75 (0.38,1.46)
Day Care vs.
Home Children
1.81 (0.78,4.18)
1.19(0.57,2.47)
~
1.60(0.67,3.81)
Chlorpyrifos
Potential Exposure via Inhalation
Potential Exposure via Dietary Ingestion
Potential Exposure via Indirect Ingestion
Potential Absorbed Dose via Inhalation
Potential Absorbed Dose via Dietary Ingestion
Potential Absorbed Dose via Indirect Ingestion
Aggregated Potential Exposure
Aggregated Potential Absorbed Dose
0.87 (0.42,1.78)
1.13(0.54,2.39)
0.88(0.41,1.90)
0.95 (0.47,1.93)
1.24 (0.60,2.55)
0.96 (0.44,2.07)
1.04(0.51,2.08)
1.11(0.57,2.17)
1.02(0.61,1.71)
1.14(0.70,1.85)
0.99(0.56,1.75)
0.98(0.59,1.64)
1.08(0.66,1.75)
0.90(0.51,1.61)
1.27(0.75,2.14)
1.17(0.70,1.95)
1.51 (0.83,2.77)
1.29(0.66,2.51)
1.40 (0.77,2.57)
1.32(0.73,2.39)
1.13(0.60,2.12)
1.24 (0.67,2.28)
1.21 (0.65,2.27)
1.05 (0.59,1.87)
Chrysene
Potential Exposure via Inhalation
Potential Exposure via Dietary Ingestion a
Potential Exposure via Indirect Ingestion
Potential Absorbed Dose via Inhalation
Potential Absorbed Dose via Dietary Ingestion a
Potential Absorbed Dose via Indirect Ingestion
1.46 (0.90,2.37)
~
0.91(0.43,1.91)
1.61 (0.96,2.70)
-
0.98(0.45,2.10)
1.57** (1.14,2.17)
~
0.69(0.40,1.19)
1.52* (1.07,2.15)
-
0.63 (0.36,1.11)
0.93 (0.60,1.44)
~
1.83 (0.99,3.39)
0.81(0.51,1.29)
-
1.62 (0.86,3.07)
Cyfluthrin
Potential Exposure via Inhalation3
Potential Exposure via Dietary Ingestion a
Potential Exposure via Indirect Ingestion °
Potential Absorbed Dose via Inhalation a
Potential Absorbed Dose via Dietary Ingestion a
Potential Absorbed Dose via Indirect Ingestion °
-
~
0.62 (0.22,1.74)
-
~
0.67(0.23,1.95)
-
~
0.70(0.33,1.49)
-
~
0.64(0.30,1.39)
-
~
1.07 (0.43,2.66)
-
~
0.95 (0.37,2.40)
Diazinon
Potential Exposure via Inhalation
Potential Exposure via Dietary Ingestion b
Potential Exposure via Indirect Ingestion
Potential Absorbed Dose via Inhalation
Potential Absorbed Dose via Dietary Ingestionb
0.93 (0.36,2.39)
0.86(0.52,1.42)
0.74 (0.23,2.38)
1.02 (0.40,2.62)
0.94(0.58,1.52)
2.24* (1.15,4.38)
1.07(0.76,1.50)
1.60 (0.71,3.63)
2.14* (1.09,4.18)
1.04(0.74,1.46)
1.38(0.62,3.11)
1.37(0.87,2.14)
1.53 (0.53,4.42)
1.21 (0.54,2.73)
1.20(0.79,1.82)
                                        R-5

-------
Table R-l.    Estimated Ratio Between Selected Strata of Geometric Mean Potential
             Exposure and Potential Absorbed Dose Estimates in Participating NC
             Children, and 95% Confidence Intervals on This Ratio (cont.)
Exposure/Dose/Biomarker Parameter
and Pathway
Potential Absorbed Dose via Indirect Ingestion
Aggregated Potential Exposure
Aggregated Potential Absorbed Dose
Estimated Ratio of Geometric Means (95% CI)
Urban vs. Rural
0.80 (0.24,2.61)
0.93 (0.44,1.94)
1.00 (0.48,2.08)
Low Income vs.
Mid/High Income
1.43 (0.62,3.27)
1.42 (0.81,2.49)
1.32 (0.76,2.30)
Day Care vs.
Home Children
1.35 (0.46,3.99)
1.44 (0.74,2.83)
1.26 (0.65,2.44)
Dibenzo [a,h ] anthracene
Potential Exposure via Inhalation3
Potential Exposure via Dietary Ingestion a
Potential Exposure via Indirect Ingestion
Potential Absorbed Dose via Inhalation8
Potential Absorbed Dose via Dietary Ingestion a
Potential Absorbed Dose via Indirect Ingestion
~
-
0.81 (0.39,1.65)
~
-
0.87(0.41,1.84)
~
-
0.72(0.43,1.23)
~
-
0.66(0.38,1.16)
~
-
1.66(0.92,3.01)
~
-
1.47 (0.79,2.76)
Di-w-butylphthalate
Potential Exposure via Inhalation
Potential Exposure via Dietary Ingestion b
Potential Exposure via Indirect Ingestion
Potential Absorbed Dose via Inhalation
Potential Absorbed Dose via Dietary Ingestionb
Potential Absorbed Dose via Indirect Ingestion
Aggregated Potential Exposure
Aggregated Potential Absorbed Dose
1.16(0.85,1.58)
0.88(0.46,1.67)
1.12(0.69,1.83)
1.28(0.91,1.80)
0.90 (0.47,1.72)
1.19(0.69,2.06)
0.90(0.49,1.65)
0.92 (0.50,1.67)
1.10(0.90,1.35)
0.66(0.40,1.08)
1.02(0.70,1.50)
1.07(0.85,1.35)
0.58* (0.35,0.95)
0.88(0.58,1.34)
0.73 (0.45,1.19)
0.64(0.39,1.04)
1.77** (1.33,2.37)
1.56 (0.84,2.89)
1.30(0.91,1.86)
1.54** (1.14,2.10)
1.41 (0.76,2.61)
1.15(0.75,1.75)
1.66 (0.93,2.96)
1.48 (0.83,2.62)
#/>'-DDE
Potential Exposure via Inhalation3
Potential Exposure via Dietary Ingestion
Potential Exposure via Indirect Ingestion8
Potential Absorbed Dose via Inhalation"
Potential Absorbed Dose via Dietary Ingestion
Potential Absorbed Dose via Indirect Ingestion a
~
0.97(0.55,1.71)
~
-
1.06(0.59,1.92)
~
~
1.06(0.74,1.50)
~
-
0.99(0.69,1.44)
~
~
1.57 (0.94,2.62)
~
-
1.38(0.81,2.36)
~
2,4-D (2,4-dichlorophenoxyacetic acid)
Potential Exposure via Inhalation0
Potential Exposure via Dietary Ingestion
Potential Exposure via Indirect Ingestion
Potential Absorbed Dose via Inhalation0
Potential Absorbed Dose via Dietary Ingestion
Potential Absorbed Dose via Indirect Ingestion
1.21 (0.65,2.24)
1.22 (0.72,2.09)
3.39** (1.64,7.02)
1.33 (0.71,2.48)
1.30 (0.76,2.24)
3.68** (1.74,7.77)
1.46 (0.96,2.22)
1.01 (0.69,1.48)
0.27** (0.15,0.47)
1.41 (0.92,2.16)
0.93 (0.63,1.36)
0.25** (0.14,0.45)
2.23** (1.28,3. 89)
1.59* (1.04,2.42)
0.54* (0.31,0.94)
1.94* (1.12,3.39)
1.43(0.94,2.17)
0.47* (0.27,0.84)
                                        R-6

-------
Table R-l.    Estimated Ratio Between Selected Strata of Geometric Mean Potential
             Exposure and Potential Absorbed Dose Estimates in Participating NC
             Children, and 95% Confidence Intervals on This Ratio (cont.)
Exposure/Dose/Biomarker Parameter
and Pathway
Aggregated Potential Exposure
Aggregated Potential Absorbed Dose
Estimated Ratio of Geometric Means (95% CI)
Urban vs. Rural
1.27 (0.70,2.29)
1.35 (0.73,2.50)
Low Income vs.
Mid/High Income
1.08(0.70,1.66)
0.99(0.63,1.54)
Day Care vs.
Home Children
1.46 (0.95,2.23)
1.27(0.82,1.95)
Heptachlor
Potential Exposure via Inhalation
Potential Exposure via Dietary Ingestiona
Potential Exposure via Indirect Ingestiona
Potential Absorbed Dose via Inhalation
Potential Absorbed Dose via Dietary Ingestion a
Potential Absorbed Dose via Indirect Ingestion3
1.11(0.47,2.65)
~
-
1.21 (0.50,2.93)
~
-
1.30 (0.74,2.29)
~
-
1.23 (0.69,2.22)
~
-
1.82 (0.82,4.07)
~
-
1.60(0.71,3.59)
~
-
Indeno[l,2,3-c
-------
Table R-l.    Estimated Ratio Between Selected Strata of Geometric Mean Potential
             Exposure and Potential Absorbed Dose Estimates in Participating NC
             Children, and 95% Confidence Intervals on This Ratio (cont.)
Exposure/Dose/Biomarker Parameter
and Pathway
Estimated Ratio of Geometric Means (95% CI)
Urban vs. Rural
Low Income vs.
Mid/High Income
Day Care vs.
Home Children
fraws-Permethrin
Potential Exposure via Inhalation
Potential Exposure via Dietary Ingestion b
Potential Exposure via Indirect Ingestion
Potential Absorbed Dose via Inhalation
Potential Absorbed Dose via Dietary Ingestion b
Potential Absorbed Dose via Indirect Ingestion
Aggregated Potential Exposure
Aggregated Potential Absorbed Dose
0.71 (0.32,1.60)
1.88 (0.67,5.26)
1.05 (0.39,2.84)
0.77 (0.34,1.77)
2.05 (0.73,5.77)
1.14(0.41,3.16)
1.96 (0.77,4.99)
2.13(0.83,5.48)
2.45** (1.37,4.36)
0.95 (0.46,1.96)
1.05 (0.50,2.19)
2.31** (1.29,4.15)
0.88(0.43,1.82)
0.95 (0.45,2.03)
0.81 (0.40,1.65)
0.74(0.36,1.53)
1.46 (0.73,2.91)
1.85 (0.79,4.34)
1.28 (0.57,2.86)
1.28 (0.62,2.61)
1.63 (0.69,3.84)
1.13(0.49,2.60)
1.84(0.82,4.12)
1.58(0.70,3.59)
PCB52
Potential Exposure via Inhalation
Potential Exposure via Dietary Ingestion a
Potential Exposure via Indirect Ingestion8
Potential Absorbed Dose via Inhalation
Potential Absorbed Dose via Dietary Ingestion3
Potential Absorbed Dose via Indirect Ingestion3
0.89(0.59,1.35)
-
~
0.97 (0.62,1.50)
~
~
0.97(0.71,1.33)
-
~
0.93 (0.67,1.29)
~
~
1.30(0.94,1.81)
-
~
1.14(0.80,1.62)
~
~
PCB95
Potential Exposure via Inhalation
Potential Exposure via Dietary Ingestion3
Potential Exposure via Indirect Ingestion3
Potential Absorbed Dose via Inhalation
Potential Absorbed Dose via Dietary Ingestion3
Potential Absorbed Dose via Indirect Ingestion3
0.95 (0.61,1.47)
-
~
1.03 (0.64,1.63)
-
~
1.14(0.82,1.59)
-
~
1.09(0.77,1.54)
-
~
1.16(0.82,1.62)
-
~
1.01 (0.70,1.46)
-
~
PCB 101
Potential Exposure via Inhalation
Potential Exposure via Dietary Ingestion3
Potential Exposure via Indirect Ingestion3
Potential Absorbed Dose via Inhalation
Potential Absorbed Dose via Dietary Ingestion3
Potential Absorbed Dose via Indirect Ingestion3
0.83 (0.50,1.36)
~
-
0.90(0.54,1.50)
-
-
1.12(0.77,1.62)
~
-
1.07(0.73,1.56)
-
-
1.12(0.75,1.66)
~
-
0.98(0.65,1.47)
-
-
3,5,6-TCP(3,5,6-trichloro-2-pyridinol)
Potential Exposure via Inhalation
Potential Exposure via Dietary Ingestion
0.96(0.49,1.89)
0.80 (0.45,1.44)
0.96(0.60,1.54)
0.65* (0.47,0.90)
1.44 (0.80,2.61)
1.82* (1.05,3. 15)

-------
Table R-l.    Estimated Ratio Between Selected Strata of Geometric Mean Potential
                Exposure and Potential Absorbed Dose Estimates in Participating NC
                Children, and 95% Confidence Intervals on This Ratio (cont.)
Exposure/Dose/Biomarker Parameter
and Pathway
Potential Exposure via Indirect Ingestion
Potential Absorbed Dose via Inhalation
Potential Absorbed Dose via Dietary Ingestion
Potential Absorbed Dose via Indirect Ingestion
Aggregated Potential Exposure
Aggregated Potential Absorbed Dose
Estimated Ratio of Geometric Means (95% CI)
Urban vs. Rural
0.67(0.30,1.50)
1.06 (0.54,2.07)
0.87(0.50,1.53)
0.72(0.32,1.63)
0.79(0.46,1.37)
0.86(0.51,1.45)
Low Income vs.
Mid/High Income
1.09 (0.59,2.01)
0.92(0.57,1.49)
0.60** (0.43,0.84)
1.01 (0.54,1.86)
0.61* (0.41,0.89)
0.56** (0.38,0.81)
Day Care vs.
Home Children
0.92(0.49,1.74)
1.26(0.71,2.25)
1.62 (0.96,2.72)
0.81 (0.43,1.54)
1.76* (1.05,2.95)
1.54 (0.95,2.50)
a Results are not presented because, for each environmental sample type whose measurements were used to calculate the
potential exposure/absorbed dose, less than 45% of the measurements were detected.
b For each environmental sample type whose measurements were used to calculate the potential exposure/absorbed dose, less
than 45% of the measurements were detected. However, results are presented because this was one of the eight pollutants
mentioned at the end of Section 9.2.
c The largest detection percentage among the environmental sample types whose measurements were used to calculate the
potential exposure/absorbed dose was between 45 and 50%.

* Statistically significantly different from 1 at the 0.05 level, but not at the 0.01 level.
** Statistically significantly different from  1 at the 0.01 level.
                                                   R-9

-------
Table R-2.    Estimated Ratio Between Selected Strata of Geometric Mean Potential
             Exposure and Potential Absorbed Dose Estimates in Participating OH
             Children, and 95% Confidence Intervals on This Ratio
Exposure/Dose/Biomarker Parameter
and Pathway
Estimated Ratio of Geometric Means (95% CI)
Urban vs. Rural
Low Income vs.
Mid/High Income
Day Care vs.
Home Children
Benz[a] anthracene
Potential Exposure via Inhalation"
Potential Exposure via Dietary Ingestiona
Potential Exposure via Indirect Ingestion
Potential Absorbed Dose via Inhalation"
Potential Absorbed Dose via Dietary Ingestion"
Potential Absorbed Dose via Indirect Ingestion
-
~
3.69** (1.80,7.56)
-
~
3.65** (1.74,7.66)
-
~
0.43** (0.26,0.70)
-
~
0.43** (0.26,0.72)
-
~
3.29** (1.88,5.76)
-
~
3.08** (1.73,5.47)
Benzo [AJfluoranthene
Potential Exposure via Inhalation"
Potential Exposure via Dietary Ingestion a
Potential Exposure via Indirect Ingestion
Potential Absorbed Dose via Inhalation"
Potential Absorbed Dose via Dietary Ingestion"
Potential Absorbed Dose via Indirect Ingestion
~
-
3.55** (1.80,6.99)
-
-
3. 52** (1.74,7.12)
~
-
0.43** (0.27,0.69)
-
-
0.43** (0.26,0.70)
~
-
3. 15** (1.86,5. 32)
-
-
2.94** (1.71,5.07)
Benzo [AJfluoranthene
Potential Exposure via Inhalation"
Potential Exposure via Dietary Ingestion"
Potential Exposure via Indirect Ingestion
Potential Absorbed Dose via Inhalation"
Potential Absorbed Dose via Dietary Ingestion"
Potential Absorbed Dose via Indirect Ingestion
~
-
3. 18** (1.59,6.36)
~
-
3. 16** (1.54,6.51)
~
-
0.43** (0.26,0.69)
~
-
0.43** (0.26,0.71)
~
-
3. 16** (1.85,5.40)
~
-
2.95** (1.69,5.16)
Benzo |#/»']perylene
Potential Exposure via Inhalation"
Potential Exposure via Dietary Ingestion"
Potential Exposure via Indirect Ingestion
Potential Absorbed Dose via Inhalation"
Potential Absorbed Dose via Dietary Ingestion"
Potential Absorbed Dose via Indirect Ingestion
-
~
3. 18** (1.61,6.30)
~
~
3. 16** (1.55,6.43)
-
~
0.43** (0.27,0.69)
~
~
0.43** (0.26,0.71)
-
~
3. 12** (1.83,5. 32)
~
~
2.92** (1.68,5.08)
Benzo [a]pyrene
Potential Exposure via Inhalation"
Potential Exposure via Dietary Ingestion"
Potential Exposure via Indirect Ingestion
Potential Absorbed Dose via Inhalation"
Potential Absorbed Dose via Dietary Ingestion"
Potential Absorbed Dose via Indirect Ingestion
-
~
3.35** (1.64,6.81)
-
~
3. 32** (1.59,6.95)
-
~
0.41** (0.25,0.67)
-
~
0.41** (0.25,0.69)
-
~
3.09** (1.77,5. 38)
-
~
2.89** (1.62,5.12)
                                       R-10

-------
Table R-2.    Estimated Ratio Between Selected Strata of Geometric Mean Potential
             Exposure and Potential Absorbed Dose Estimates in Participating OH
             Children, and 95% Confidence Intervals on This Ratio (cont.)
Exposure/Dose/Biomarker Parameter
and Pathway
Estimated Ratio of Geometric Means (95% CI)
Urban vs. Rural
Low Income vs.
Mid/High Income
Day Care vs.
Home Children
Benzo[e]pyrene
Potential Exposure via Inhalation3
Potential Exposure via Dietary Ingestion3
Potential Exposure via Indirect Ingestion
Potential Absorbed Dose via Inhalation8
Potential Absorbed Dose via Dietary Ingestion a
Potential Absorbed Dose via Indirect Ingestion
~
~
3.23** (1.63,6.39)
~
-
3.21** (1.57,6.53)
~
~
0.43** (0.27,0.70)
~
-
0.44** (0.26,0.72)
~
~
3.04** (1.79,5. 16)
~
-
2.84** (1.64,4.92)
Benzylbutylphthalate
Potential Exposure via Inhalation3
Potential Exposure via Dietary Ingestion
Potential Exposure via Indirect Ingestion
Potential Absorbed Dose via Inhalation3
Potential Absorbed Dose via Dietary Ingestion
Potential Absorbed Dose via Indirect Ingestion
-
1.75 (0.62,4.91)
0.63 (0.32,1.24)
-
1.73 (0.61,4.94)
0.63(0.31,1.27)
-
0.87(0.41,1.86)
0.96(0.59,1.55)
-
0.95 (0.44,2.04)
0.97(0.59,1.61)
-
2.83** (1.33,6.02)
2.73** (1.64,4.57)
-
2.44* (1.14,5.25)
2.54** (1.51,4.29)
Bisphenol-A
Potential Exposure via Inhalation
Potential Exposure via Dietary Ingestion
Potential Exposure via Indirect Ingestion
Potential Absorbed Dose via Inhalation
Potential Absorbed Dose via Dietary Ingestion
Potential Absorbed Dose via Indirect Ingestion
Aggregated Potential Exposure
Aggregated Potential Absorbed Dose
0.95(0.61,1.48)
1.17(0.64,2.12)
1.04(0.61,1.79)
0.96(0.61,1.50)
1.20(0.67,2.15)
1.03 (0.57,1.87)
1.42 (0.79,2.55)
1.48 (0.79,2.77)
1.38* (1.00,1. 90)
1.14(0.77,1.69)
0.68(0.45,1.03)
1.31(0.94,1.81)
1.15 (0.77,1.72)
0.68(0.44,1.07)
1.28 (0.79,2.07)
1.27(0.76,2.13)
1.39(0.98,1.97)
1.44(0.97,2.13)
1.07(0.70,1.63)
1.29(0.91,1.83)
1.34(0.91,1.96)
0.99(0.65,1.53)
1.55 (0.97,2.46)
1.43 (0.87,2.33)
a^oAa-Chlordane
Potential Exposure via Inhalation
Potential Exposure via Dietary Ingestion3
Potential Exposure via Indirect Ingestion
Potential Absorbed Dose via Inhalation
Potential Absorbed Dose via Dietary Ingestion3
Potential Absorbed Dose via Indirect Ingestion
1.03 (0.49,2.20)
~
1.49 (0.62,3.59)
1.01(0.48,2.14)
-
1.47(0.61,3.57)
1.44 (0.88,2.35)
~
1.01 (0.53,1.90)
1.42 (0.86,2.34)
-
1.02(0.54,1.94)
0.78(0.44,1.39)
~
1.05 (0.55,2.03)
0.73 (0.41,1.28)
-
0.98(0.51,1.89)
gamma-Chlordaae
Potential Exposure via Inhalation
Potential Exposure via Dietary Ingestion3
Potential Exposure via Indirect Ingestion
1.09(0.49,2.41)
~
1.40 (0.56,3.50)
1.42 (0.85,2.37)
~
1.05 (0.54,2.03)
0.79(0.43,1.46)
~
1.10(0.55,2.18)
                                       R-ll

-------
Table R-2.    Estimated Ratio Between Selected Strata of Geometric Mean Potential
             Exposure and Potential Absorbed Dose Estimates in Participating OH
             Children, and 95% Confidence Intervals on This Ratio (cont.)
Exposure/Dose/Biomarker Parameter
and Pathway
Potential Absorbed Dose via Inhalation
Potential Absorbed Dose via Dietary Ingestion a
Potential Absorbed Dose via Indirect Ingestion
Estimated Ratio of Geometric Means (95% CI)
Urban vs. Rural
1.06 (0.48,2.34)
-
1.38(0.55,3.47)
Low Income vs.
Mid/High Income
1.40 (0.83,2.37)
-
1.06 (0.54,2.07)
Day Care vs.
Home Children
0.74(0.41,1.34)
-
1.02 (0.52,2.03)
Chlorpyrifos
Potential Exposure via Inhalation
Potential Exposure via Dietary Ingestion
Potential Exposure via Indirect Ingestion
Potential Absorbed Dose via Inhalation
Potential Absorbed Dose via Dietary Ingestion
Potential Absorbed Dose via Indirect Ingestion
Aggregated Potential Exposure
Aggregated Potential Absorbed Dose
1.54 (0.78,3.06)
0.92 (0.50,1.72)
1.42(0.58,3.45)
1.53 (0.76,3.09)
0.94(0.51,1.73)
1.42(0.57,3.53)
1.03 (0.59,1.79)
1.08(0.61,1.90)
1.25 (0.76,2.04)
2.00** (1.29,3.08)
1.30 (0.68,2.48)
1.17(0.70,1.96)
2.06** (1.34,3.18)
1.35 (0.69,2.62)
1.64* (1.04,2.58)
1.66* (1.04,2.66)
1.48 (0.83,2.65)
1.02(0.66,1.60)
2.52** (1.31,4.85)
1.44 (0.80,2.60)
0.92(0.60,1.39)
2.33* (1.20,4.54)
1.20(0.75,1.94)
1.07 (0.67,1.72)
Chrysene
Potential Exposure via Inhalation0
Potential Exposure via Dietary Ingestion a
Potential Exposure via Indirect Ingestion
Potential Absorbed Dose via Inhalation0
Potential Absorbed Dose via Dietary Ingestion a
Potential Absorbed Dose via Indirect Ingestion
1.36(0.88,2.11)
~
3.51** (1.76,6.98)
1.39(0.89,2.19)
~
3.47** (1.70,7.11)
1.17(0.86,1.59)
~
0.42** (0.26,0.68)
1.10(0.79,1.52)
~
0.42** (0.25,0.70)
1.37(0.97,1.92)
~
3.24** (1.91,5. 50)
1.34(0.95,1.90)
~
3.03** (1.75,5.23)
Cyfluthrin
Potential Exposure via Inhalation3
Potential Exposure via Dietary Ingestion a
Potential Exposure via Indirect Ingestion
Potential Absorbed Dose via Inhalation"
Potential Absorbed Dose via Dietary Ingestion a
Potential Absorbed Dose via Indirect Ingestion
~
-
2.47* (1.07,5.69)
-
-
2.44* (1.04,5.73)
~
-
0.79(0.44,1.39)
-
-
0.79(0.44,1.43)
~
-
1.64(0.85,3.14)
-
-
1.53 (0.79,2.96)
Diazinon
Potential Exposure via Inhalation
Potential Exposure via Dietary Ingestion b
Potential Exposure via Indirect Ingestion
Potential Absorbed Dose via Inhalation
Potential Absorbed Dose via Dietary Ingestionb
Potential Absorbed Dose via Indirect Ingestion
0.61 (0.27,1.42)
0.84(0.63,1.14)
1.57 (0.49,5.00)
0.62 (0.27,1.45)
0.83(0.60,1.15)
1.58(0.49,5.11)
1.57 (0.88,2.82)
1.15(0.93,1.41)
0.77(0.35,1.69)
1.57 (0.87,2.83)
1.16(0.93,1.46)
0.76(0.35,1.68)
2.02* (1.13,3.59)
1.37** (1.11, 1.69)
3.45** (1.38,8.61)
1.88* (1.05,3.38)
1.28* (1.02,1.60)
3.22* (1.27,8.17)
                                       R-12

-------
Table R-2.    Estimated Ratio Between Selected Strata of Geometric Mean Potential
             Exposure and Potential Absorbed Dose Estimates in Participating OH
             Children, and 95% Confidence Intervals on This Ratio (cont.)
Exposure/Dose/Biomarker Parameter
and Pathway
Aggregated Potential Exposure
Aggregated Potential Absorbed Dose
Estimated Ratio of Geometric Means (95% CI)
Urban vs. Rural
0.86(0.50,1.49)
0.88(0.51,1.51)
Low Income vs.
Mid/High Income
1.25 (0.83,1.86)
1.28(0.86,1.90)
Day Care vs.
Home Children
1.66* (1.11,2.48)
1.52* (1.01,2.29)
Dibenzo [a,h ] anthracene
Potential Exposure via Inhalation3
Potential Exposure via Dietary Ingestiona
Potential Exposure via Indirect Ingestion
Potential Absorbed Dose via Inhalation a
Potential Absorbed Dose via Dietary Ingestion a
Potential Absorbed Dose via Indirect Ingestion
-
~
3.50** (1.75,7.03)
-
~
3.47** (1.68,7.14)
-
~
0.44** (0.27,0.71)
-
~
0.44** (0.27,0.73)
-
~
3. 19** (1.85,5. 51)
-
~
2.98** (1.70,5.25)
Di-«-butylphthalate
Potential Exposure via Inhalation
Potential Exposure via Dietary Ingestion b
Potential Exposure via Indirect Ingestion
Potential Absorbed Dose via Inhalation
Potential Absorbed Dose via Dietary Ingestionb
Potential Absorbed Dose via Indirect Ingestion
Aggregated Potential Exposure
Aggregated Potential Absorbed Dose
0.65* (0.45,0.93)
0.95 (0.44,2.05)
1.31(0.74,2.29)
0.63* (0.44,0.92)
0.94 (0.43,2.05)
1.26 (0.70,2.28)
0.92 (0.46,1.87)
0.93 (0.46,1.90)
1.05(0.85,1.31)
1.15 (0.66,2.02)
0.76(0.51,1.15)
1.04(0.81,1.32)
1.25 (0.71,2.21)
0.76(0.49,1.17)
1.21 (0.70,2.09)
1.27 (0.73,2.20)
1.44* (1.09,1. 90)
2.17** (1.24,3. 82)
2.02** (1.32,3.10)
1.34* (1.02,1.76)
1.87* (1.06,3.31)
1.88** (1.23,2.88)
2.07** (1.21,3. 52)
1.76* (1.03,3.02)
/7,/>'-DDE
Potential Exposure via Inhalation3
Potential Exposure via Dietary Ingestion
Potential Exposure via Indirect Ingestion0
Potential Absorbed Dose via Inhalation a
Potential Absorbed Dose via Dietary Ingestion
Potential Absorbed Dose via Indirect Ingestion0
~
0.95 (0.52,1.74)
0.91 (0.41,2.05)
~
0.96 (0.52,1.77)
0.91 (0.40,2.08)
~
0.86(0.58,1.27)
0.92(0.53,1.58)
~
0.84(0.56,1.27)
0.91 (0.52,1.58)
~
1.44 (0.90,2.29)
1.15(0.61,2.16)
~
1.33(0.83,2.11)
1.08 (0.56,2.06)
2,4-D (2,4-dichlorophenoxyacetic acid)
Potential Exposure via Inhalation15
Potential Exposure via Dietary Ingestion b
Potential Exposure via Indirect Ingestion
Potential Absorbed Dose via Inhalation11
Potential Absorbed Dose via Dietary Ingestionb
Potential Absorbed Dose via Indirect Ingestion
Aggregated Potential Exposure
0.60 (0.30,1.22)
1.37(0.73,2.59)
2.80* (1.03,7.62)
0.59(0.29,1.18)
1.36 (0.72,2.57)
2.84* (1.04,7.79)
1.58 (0.68,3.67)
0.87(0.61,1.24)
1.00(0.66,1.51)
0.29** (0.15,0.54)
0.80(0.56,1.16)
0.98(0.65,1.49)
0.29** (0.15,0.54)
0.86(0.58,1.30)
0.96(0.57,1.61)
1.36(0.85,2.19)
1.85 (0.86,3.97)
0.90(0.54,1.52)
1.28 (0.80,2.07)
1.73 (0.80,3.75)
1.23 (0.67,2.26)
                                       R-13

-------
Table R-2.    Estimated Ratio Between Selected Strata of Geometric Mean Potential
             Exposure and Potential Absorbed Dose Estimates in Participating OH
             Children, and 95% Confidence Intervals on This Ratio (cont.)
Exposure/Dose/Biomarker Parameter
and Pathway
Aggregated Potential Absorbed Dose
Estimated Ratio of Geometric Means (95% CI)
Urban vs. Rural
1.56 (0.67,3.64)
Low Income vs.
Mid/High Income
0.83 (0.56,1.25)
Day Care vs.
Home Children
1.15(0.62,2.12)
Indeno[l,2,3-c
-------
Table R-2.    Estimated Ratio Between Selected Strata of Geometric Mean Potential
             Exposure and Potential Absorbed Dose Estimates in Participating OH
             Children, and 95% Confidence Intervals on This Ratio (cont.)
Exposure/Dose/Biomarker Parameter
and Pathway
Estimated Ratio of Geometric Means (95% CI)
Urban vs. Rural
Low Income vs.
Mid/High Income
Day Care vs.
Home Children
PCB52
Potential Exposure via Inhalation
Potential Exposure via Dietary Ingestiond
Potential Exposure via Indirect Ingestion
Potential Absorbed Dose via Inhalation
Potential Absorbed Dose via Dietary Ingestion d
Potential Absorbed Dose via Indirect Ingestion
0.63(0.34,1.14)

0.78(0.39,1.57)
0.63(0.35,1.14)

0.78(0.38,1.60)
0.93 (0.66,1.31)

0.79(0.48,1.30)
0.92(0.63,1.34)

0.81 (0.48,1.35)
1.36(0.83,2.23)

1.54(0.91,2.62)
1.28 (0.80,2.04)

1.42 (0.83,2.42)
PCB95
Potential Exposure via Inhalation
Potential Exposure via Dietary Ingestion d
Potential Exposure via Indirect Ingestion a
Potential Absorbed Dose via Inhalation
Potential Absorbed Dose via Dietary Ingestion d
Potential Absorbed Dose via Indirect Ingestion a
0.77(0.41,1.46)

-
0.78(0.41,1.47)

-
0.96(0.63,1.47)

-
0.94(0.61,1.45)

-
1.43 (0.89,2.30)

-
1.34(0.84,2.13)

-
PCB 101
Potential Exposure via Inhalation
Potential Exposure via Dietary Ingestion d
Potential Exposure via Indirect Ingestion a
Potential Absorbed Dose via Inhalation
Potential Absorbed Dose via Dietary Ingestion d
Potential Absorbed Dose via Indirect Ingestion a
0.65 (0.33,1.28)

~
0.65 (0.33,1.29)

~
0.84(0.54,1.32)

~
0.83(0.53,1.31)

~
1.73* (1.05,2.85)

~
1.62 (0.99,2.68)

~
                                       R-15

-------
Table R-2.    Estimated Ratio Between Selected Strata of Geometric Mean Potential
                Exposure and Potential Absorbed Dose Estimates in Participating OH
                Children, and 95% Confidence Intervals on This Ratio  (cont.)
Exposure/Dose/Biomarker Parameter
and Pathway
Estimated Ratio of Geometric Means (95% CI)
Urban vs. Rural
Low Income vs.
Mid/High Income
Day Care vs.
Home Children
3,5,6-TCP(3,5,6-trichloro-2-pyridinol)
Potential Exposure via Inhalation
Potential Exposure via Dietary Ingestion
Potential Exposure via Indirect Ingestion
Potential Absorbed Dose via Inhalation
Potential Absorbed Dose via Dietary Ingestion
Potential Absorbed Dose via Indirect Ingestion
Aggregated Potential Exposure
Aggregated Potential Absorbed Dose
1.53(0.75,3.11)
0.83 (0.48,1.46)
1.68 (0.76,3.72)
1.49(0.72,3.11)
0.84 (0.49,1.44)
1.65 (0.73,3.74)
0.67(0.35,1.32)
0.67(0.35,1.28)
1.70* (1.11,2.61)
0.87(0.60,1.27)
0.92(0.52,1.64)
1.73* (1.11,2.70)
0.87(0.60,1.26)
0.96(0.53,1.74)
0.90(0.59,1.38)
0.92(0.60,1.40)
1.01 (0.60,1.70)
1.14(0.75,1.73)
1.81* (1.01,3.24)
0.94(0.55,1.59)
1.07(0.73,1.57)
1.67(0.93,3.01)
1.23 (0.75,2.00)
1.13(0.71,1.78)
a Results are not presented because, for each environmental sample type whose measurements were used to calculate the
potential exposure/absorbed dose, less than 45% of the measurements were detected.
b For each environmental sample type whose measurements were used to calculate the potential exposure/absorbed dose, less
than 45% of the measurements were detected. However, results are presented because this was one of the eight pollutants
mentioned at the end of Section 9.2.
c The largest detection percentage among the environmental sample types whose measurements were used to calculate the
potential exposure/absorbed dose was between 45 and 50%.
d No available data for calculations to be made.

* Statistically significantly different from 1 at the 0.05 level, but not at the 0.01 level.
** Statistically significantly different from 1 at the 0.01 level.
                                                  R-16

-------
Table R-3.   P-values of Statistical Tests to Determine the Significance of Urbanicity,
            Income Status, and Day Care Attendance on 1) NC Children's Exposure and
            Absorbed Dose Estimates, and 2) the Difference in Estimates Between NC
            Children and Adults in the Same Household(a)
Exposure/Dose/Biomarker
Parameter and Pathway
Analysis on Child Measures
Urbanicity
Effect
Income
Status
Effect
Day Care
Attendance
Effect
Analysis on Differences Between
Child and Adult Measures in Same Household
Child vs.
Adult
Difference1"1
Urbanicity
Effect
Income
Status
Effect
Day Care
Attendance
Effect
Benz[a]anthracene
Potential Exposure via Inhalation
(ng/day)
Potential Exposure via Dietary
Ingestion (ng/day)(c)
Potential Exposure via Indirect
Ingestion (ng/day)
Potential Absorbed Dose via
Inhalation (ng/kg/day)
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)(c)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)
0.132
-
0.733
0.078
-
0.884
0.056
-
0.135
0.106
-
0.084
0.514
-
0.080
0.255
-
0.191
1.000

O.001**
<0.001**

O.001**
0.515

0.860
0.797

0.938
0.001**

0.874
0.315

0.830
<0.001**

0.035*
0.026*

0.085
Benzo[fo]fluoranthene
Potential Exposure via Inhalation
(ng/day)
Potential Exposure via Dietary
Ingestion (ng/day)(c)
Potential Exposure via Indirect
Ingestion (ng/day)
Potential Absorbed Dose via
Inhalation (ng/kg/day)
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)(c)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)
0.173
-
0.830
0.104
-
0.984
0.010*
-
0.271
0.029*
-
0.177
0.747
-
0.046*
0.821
-
0.125
1.000

<0.001**
<0.001**

O.001**
0.666

0.988
0.294

0.802
0.109

0.598
0.870

0.401
0.028*

0.069
0.223

0.154
Benzo[fc]fluoranthene
Potential Exposure via Inhalation
(ng/day)
Potential Exposure via Dietary
Ingestion (ng/day)(c)
Potential Exposure via Indirect
Ingestion (ng/day)
Potential Absorbed Dose via
Inhalation (ng/kg/day)
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)(c)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)
0.394
-
0.616
0.198
-
0.765
0.036*
-
0.184
0.123
-
0.116
0.930
-
0.077
0.447
-
0.185
1.000

<0.001**
<0.001**

O.001**
0.934

0.975
0.429

0.826
0.032*

0.773
0.984

0.518
o.oor*

0.064
0.142

0.141
Benzo[g/ii]perylene
Potential Exposure via Inhalation
(ng/day)
Potential Exposure via Dietary
Ingestion (ng/day)(c)
0.304
-
0.083
-
0.878
-
1.000

0.963

0.405

0.584

                                       R-17

-------
Table R-3.   P-values of Statistical Tests to Determine the Significance of Urbanicity,
            Income Status, and Day Care Attendance on 1) NC Children's Exposure and
            Absorbed Dose Estimates, and 2) the Difference in Estimates Between NC
            Children and Adults in the Same Household(a) (cont.)
Exposure/Dose/Biomarker
Parameter and Pathway
Potential Exposure via Indirect
Ingestion (ng/day)
Potential Absorbed Dose via
Inhalation (ng/kg/day)
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)(c)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)
Analysis on Child Measures
Urbanicity
Effect
0.906
0.186
-
0.938
Income
Status
Effect
0.195
0.145
-
0.124
Day Care
Attendance
Effect
0.097
0.502
-
0.238
Analysis on Differences Between
Child and Adult Measures in Same Household
Child vs.
Adult
Difference'111
<0.001**
<0.001**

O.001**
Urbanicity
Effect
0.919
0.400

0.885
Income
Status
Effect
0.697
0.457

0.468
Day Care
Attendance
Effect
0.051
0.926

0.119
Benzo[a]pyrene
Potential Exposure via Inhalation
(ng/day)
Potential Exposure via Dietary
Ingestion (ng/day)(c)
Potential Exposure via Indirect
Ingestion (ng/day)
Potential Absorbed Dose via
Inhalation (ng/kg/day)
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)(c)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)
0.486
-
0.942
0.307
-
0.910
0.007"
-
0.150
0.022*
-
0.093
0.880
-
0.098
0.615
-
0.228
1.000

<0.001**
O.001**

<0.001**
0.830

0.783
0.462

0.991
0.064

0.926
0.930

0.645
0.013*

0.052
0.252

0.118
Benzo[e]pyrene
Potential Exposure via Inhalation
(ng/day)
Potential Exposure via Dietary
Ingestion (ng/day)(c)
Potential Exposure via Indirect
Ingestion (ng/day)
Potential Absorbed Dose via
Inhalation (ng/kg/day)
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)(c)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)
0.431
-
0.744
0.221
-
0.901
0.014*
-
0.246
0.046*
-
0.159
0.755
-
0.078
0.615
-
0.196
1.000

<0.001**
O.001**

<0.001**
0.941

0.923
0.434

0.879
0.036*

0.791
0.949

0.542
0.001**

0.053
0.085

0.124
Benzylbutylphthalate
Potential Exposure via Inhalation
(ng/day)(c)
Potential Exposure via Dietary
Ingestion (ng/day)(c)
Potential Exposure via Indirect
Ingestion (ng/day)
Potential Absorbed Dose via
Inhalation (ng/kg/day)(c)
-
-
0.122
-
-
-
0.127
-
-
-
0.193
-
-

O.001**
-
-

0.502
-
-

0.266
-
-

0.014*
-
                                       R-18

-------
Table R-3.   P-values of Statistical Tests to Determine the Significance of Urbanicity,
            Income Status, and Day Care Attendance on 1) NC Children's Exposure and
            Absorbed Dose Estimates, and 2) the Difference in Estimates Between NC
            Children and Adults in the Same Household(a) (cont.)
Exposure/Dose/Biomarker
Parameter and Pathway
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)(c)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)
Analysis on Child Measures
Urbanicity
Effect
-
0.177
Income
Status
Effect
-
0.323
Day Care
Attendance
Effect
-
0.383
Analysis on Differences Between
Child and Adult Measures in Same Household
Child vs.
Adult
Difference'111

<0.001"
Urbanicity
Effect

0.660
Income
Status
Effect

0.134
Day Care
Attendance
Effect

0.036*
Bisphenol-A
Potential Exposure via Inhalation
(ng/day)
Potential Exposure via Dietary
Ingestion (ng/day)
Potential Exposure via Indirect
Ingestion (ng/day)(d)
Potential Absorbed Dose via
Inhalation (ng/kg/day)
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)(d)
Aggregated Potential Exposure
(ng/day)
Aggregated Potential Absorbed
Dose (ng/kg/day)
0.924
0.176
0.569
0.682
0.295
0.622
0.129
0.227
0.140
0.616
0.287
0.231
0.419
0.118
0.502
0.346
0.450
o.ooi"
0.531
0.236
0.003"
0.871
<0.001"
0.004"
1.000

O.001"
<0.001"

O.001"


0.762

0.251
0.414

0.400


0.506

0.955
0.922

0.685


0.698

0.838
0.995

0.634


a/p/ia-Chlordane
Potential Exposure via Inhalation
(ng/day)
Potential Exposure via Dietary
Ingestion (ng/day)(c)
Potential Exposure via Indirect
Ingestion (ng/day)
Potential Absorbed Dose via
Inhalation (ng/kg/day)
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)(c)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)
0.500
-
0.363
0.668
-
0.487
0.273
-
0.574
0.362
-
0.399
0.397
-
0.150
0.665
-
0.281
1.000

<0.001"
O.001"

<0.001"
0.129

0.037*
0.385

0.066
0.341

0.724
0.953

0.875
0.023*

0.002"
0.103

0.006"
gamma-Chlordane
Potential Exposure via Inhalation
(ng/day)
Potential Exposure via Dietary
Ingestion (ng/day)(c)
Potential Exposure via Indirect
Ingestion (ng/day)
Potential Absorbed Dose via
Inhalation (ng/kg/day)
0.546
-
0.422
0.695
0.220
-
0.560
0.302
0.395
-
0.160
0.635
0.998

O.001"
O.001"
0.116

0.030*
0.318
0.361

0.839
0.886
0.019*

0.002"
0.074
                                       R-19

-------
Table R-3.   P-values of Statistical Tests to Determine the Significance of Urbanicity,
            Income Status, and Day Care Attendance on 1) NC Children's Exposure and
            Absorbed Dose Estimates, and 2) the Difference in Estimates Between NC
            Children and Adults in the Same Household(a) (cont.)
Exposure/Dose/Biomarker
Parameter and Pathway
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)(c)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)
Analysis on Child Measures
Urbanicity
Effect
-
0.543
Income
Status
Effect
-
0.388
Day Care
Attendance
Effect
-
0.286
Analysis on Differences Between
Child and Adult Measures in Same Household
Child vs.
Adult
Difference'111

<0.001"
Urbanicity
Effect

0.056
Income
Status
Effect

0.948
Day Care
Attendance
Effect

0.005"
Chlorpyrifos
Potential Exposure via Inhalation
(ng/day)
Potential Exposure via Dietary
Ingestion (ng/day)
Potential Exposure via Indirect
Ingestion (ng/day)
Potential Absorbed Dose via
Inhalation (ng/kg/day)
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)
Aggregated Potential Exposure
(ng/day)
Aggregated Potential Absorbed
Dose (ng/kg/day)
0.695
0.742
0.747
0.885
0.560
0.906
0.920
0.754
0.945
0.604
0.967
0.938
0.767
0.726
0.368
0.537
0.170
0.446
0.262
0.342
0.695
0.485
0.531
0.853
1.000

O.001"
<0.001"

O.001"


0.055

0.691
0.386

0.900


0.187

0.287
0.985

0.203


0.727

0.468
0.877

0.634


Chrysene
Potential Exposure via Inhalation
(ng/day)
Potential Exposure via Dietary
Ingestion (ng/day)(c)
Potential Exposure via Indirect
Ingestion (ng/day)
Potential Absorbed Dose via
Inhalation (ng/kg/day)
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)(c)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)
0.123
-
0.801
0.071
-
0.949
0.006"
-
0.178
0.020*
-
0.110
0.737
-
0.053
0.368
-
0.132
1.000

<0.001"
O.001"

<0.001"
0.849

0.916
0.343

0.878
0.003"

0.787
0.465

0.899
0.006"

0.051
0.120

0.116
Cyfluthrin
Potential Exposure via Inhalation
(ng/day)(c)
Potential Exposure via Dietary
Ingestion (ng/day)(c)
Potential Exposure via Indirect
Ingestion (ng/day)(e)
Potential Absorbed Dose via
Inhalation (ng/kg/day)(c)
-
-
0.360
-
-
-
0.353
-
-
-
0.876
-
-

O.001"
-
-

0.835
-
-

0.077
-
-

0.285
-
                                       R-20

-------
Table R-3.   P-values of Statistical Tests to Determine the Significance of Urbanicity,
            Income Status, and Day Care Attendance on 1) NC Children's Exposure and
            Absorbed Dose Estimates, and 2) the Difference in Estimates Between NC
            Children and Adults in the Same Household(a) (cont.)
Exposure/Dose/Biomarker
Parameter and Pathway
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)(c)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)(e)
Analysis on Child Measures
Urbanicity
Effect
-
0.462
Income
Status
Effect
-
0.256
Day Care
Attendance
Effect
-
0.906
Analysis on Differences Between
Child and Adult Measures in Same Household
Child vs.
Adult
Difference'111

<0.001**
Urbanicity
Effect

0.732
Income
Status
Effect

0.092
Day Care
Attendance
Effect

0.370
Diazinon
Potential Exposure via Inhalation
(ng/day)
Potential Exposure via Dietary
Ingestion (ng/day)(d)
Potential Exposure via Indirect
Ingestion (ng/day)
Potential Absorbed Dose via
Inhalation (ng/kg/day)
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)(d)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)
Aggregated Potential Exposure
(ng/day)
Aggregated Potential Absorbed
Dose (ng/kg/day)
0.881
0.542
0.613
0.965
0.787
0.706
0.842
0.994
0.019*
0.703
0.254
0.027*
0.806
0.395
0.216
0.318
0.417
0.164
0.425
0.634
0.354
0.575
0.271
0.482
0.999

O.001**
<0.001**

O.001**


0.716

0.730
0.462

0.883


0.377

0.393
0.206

0.333


0.042*

0.007**
0.110

0.012*


Dibenzo[a,/i]anthracene
Potential Exposure via Inhalation
(ng/day)(c)
Potential Exposure via Dietary
Ingestion (ng/day)(c)
Potential Exposure via Indirect
Ingestion (ng/day)
Potential Absorbed Dose via
Inhalation (ng/kg/day)(c)
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)(c)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)
-
-
0.551
-
-
0.702
-
-
0.230
-
-
0.145
-
-
0.091
-
-
0.217
-

<0.001**
-

<0.001**
-

0.960
-

0.784
-

0.662
-

0.453
-

0.033*
-

0.082
Di-n-butylphthalate
Potential Exposure via Inhalation
(ng/day)
Potential Exposure via Dietary
Ingestion (ng/day)(d)
Potential Exposure via Indirect
Ingestion (ng/day)
Potential Absorbed Dose via
Inhalation (ng/kg/day)
0.358
0.680
0.638
0.155
0.334
0.096
0.902
0.577
<0.001**
0.157
0.147
0.007**
1.000

O.001**
O.001**
0.842

0.592
0.350
0.060

0.321
0.687
<0.001**

0.028*
0.006**
                                       R-21

-------
Table R-3.   P-values of Statistical Tests to Determine the Significance of Urbanicity,
            Income Status, and Day Care Attendance on 1) NC Children's Exposure and
            Absorbed Dose Estimates, and 2) the Difference in Estimates Between NC
            Children and Adults in the Same Household(a) (cont.)
Exposure/Dose/Biomarker
Parameter and Pathway
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)(d)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)
Aggregated Potential Exposure
(ng/day)
Aggregated Potential Absorbed
Dose (ng/kg/day)
Analysis on Child Measures
Urbanicity
Effect
0.755
0.515
0.732
0.769
Income
Status
Effect
0.032*
0.552
0.200
0.068
Day Care
Attendance
Effect
0.271
0.500
0.085
0.177
Analysis on Differences Between
Child and Adult Measures in Same Household
Child vs.
Adult
Difference'111

<0.001"


Urbanicity
Effect

0.810


Income
Status
Effect

0.152


Day Care
Attendance
Effect

0.078


p,p'-DDE
Potential Exposure via Inhalation
(ng/day)(c)
Potential Exposure via Dietary
Ingestion (ng/day)
Potential Exposure via Indirect
Ingestion (ng/day)(c)
Potential Absorbed Dose via
Inhalation (ng/kg/day)(c)
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)(c)
-
0.918
-
-
0.841
-
-
0.753
-
-
0.973
-
-
0.084
-
-
0.229
-
-

-
-

-
-

-
-

-
-

-
-

-
-

-
-

-
2,4-D (2,4-dichlorophenoxyacetic acid)
Potential Exposure via Inhalation
(ng/day)(e)
Potential Exposure via Dietary
Ingestion (ng/day)
Potential Exposure via Indirect
Ingestion (ng/day)
Potential Absorbed Dose via
Inhalation (ng/kg/day)(e)
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)
Aggregated Potential Exposure
(ng/day)
Aggregated Potential Absorbed
Dose (ng/kg/day)
0.545
0.452
0.001"
0.368
0.333
0.001"
0.417
0.318
0.077
0.945
<0.001"
0.114
0.695
<0.001"
0.730
0.950
0.006"
0.035*
0.031*
0.02*
0.090
0.011*
0.079
0.252
0.976
0.443
<0.001"
O.001"
O.001"
<0.001"
0.309
O.001"
0.547
0.706
0.752
0.380
0.638
0.638
0.814
0.896
0.814
0.169
0.037*
0.816
0.152
0.039*
0.498
0.463
<0.001"
0.023*
0.144
<0.001"
0.029*
0.270
0.018*
0.031*
Heptachlor
Potential Exposure via Inhalation
(ng/day)
Potential Exposure via Dietary
Ingestion (ng/day)(c)
0.805
-
0.363
-
0.137
-
0.988

0.048*

0.245

0.004"

                                       R-22

-------
Table R-3.    P-values of Statistical Tests to Determine the Significance of Urbanicity,
             Income Status, and Day Care Attendance on 1) NC Children's Exposure and
             Absorbed Dose Estimates, and 2) the Difference in Estimates Between NC
             Children and Adults in the Same Household(a) (cont.)
Exposure/Dose/Biomarker
Parameter and Pathway
Potential Exposure via Indirect
Ingestion (ng/day)(c)
Potential Absorbed Dose via
Inhalation (ng/kg/day)
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)(c)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)(c)
Analysis on Child Measures
Urbanicity
Effect
-
0.667
-
-
Income
Status
Effect
-
0.478
-
-
Day Care
Attendance
Effect
-
0.249
-
-
Analysis on Differences Between
Child and Adult Measures in Same Household
Child vs.
Adult
Difference'111
-
<0.001**

-
Urbanicity
Effect
-
0.162

-
Income
Status
Effect
-
0.757

-
Day Care
Attendance
Effect
-
0.025*

-
lndeno[1 ,2,3-cd]pyrene
Potential Exposure via Inhalation
(ng/day)
Potential Exposure via Dietary
Ingestion (ng/day)(c)
Potential Exposure via Indirect
Ingestion (ng/day)
Potential Absorbed Dose via
Inhalation (ng/kg/day)
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)(c)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)
0.435
-
0.942
0.265
-
0.796
0.013*
-
0.221
0.036*
-
0.139
0.89
-
0.162
0.468
-
0.347
1.000

<0.001**
O.001**

<0.001**
0.882

0.864
0.476

0.935
0.341

0.865
0.600

0.597
0.189

0.034*
0.678

0.085
Pentachlorophenol
Potential Exposure via Inhalation
(ng/day)
Potential Exposure via Dietary
Ingestion (ng/day)(c)
Potential Exposure via Indirect
Ingestion (ng/day)
Potential Absorbed Dose via
Inhalation (ng/kg/day)
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)(c)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)
0.39
-
0.810
0.588
-
0.977
0.153
-
0.896
0.220
-
0.879
0.109
-
0.526
0.266
-
0.312
0.999
-
<0.001**
O.001**
-
<0.001**
0.023*
-
0.708
0.132
-
0.884
0.049*
-
0.242
0.235
-
0.152
0.006**
-
0.269
0.036*
-
0.397
c/s-Permethrin
Potential Exposure via Inhalation
(ng/day)
Potential Exposure via Dietary
Ingestion (ng/day)(d)
Potential Exposure via Indirect
Ingestion (ng/day)
Potential Absorbed Dose via
Inhalation (ng/kg/day)
0.320
0.268
0.946
0.441
0.003**
0.743
0.622
0.006**
0.297
0.104
0.628
0.516
1.000

O.001**
O.001**
0.080

0.475
0.331
0.860

0.665
0.708
0.769

0.159
0.951
                                       R-23

-------
Table R-3.   P-values of Statistical Tests to Determine the Significance of Urbanicity,
            Income Status, and Day Care Attendance on 1) NC Children's Exposure and
            Absorbed Dose Estimates, and 2) the Difference in Estimates Between NC
            Children and Adults in the Same Household(a) (cont.)
Exposure/Dose/Biomarker
Parameter and Pathway
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)(d)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)
Aggregated Potential Exposure
(ng/day)
Aggregated Potential Absorbed
Dose (ng/kg/day)
Analysis on Child Measures
Urbanicity
Effect
0.210
0.823
0.244
0.191
Income
Status
Effect
0.610
0.839
0.572
0.437
Day Care
Attendance
Effect
0.175
0.875
0.087
0.171
Analysis on Differences Between
Child and Adult Measures in Same Household
Child vs.
Adult
Difference'111

<0.001**


Urbanicity
Effect

0.639


Income
Status
Effect

0.516


Day Care
Attendance
Effect

0.297


frans-Permethrin
Potential Exposure via Inhalation
(ng/day)
Potential Exposure via Dietary
Ingestion (ng/day)(d)
Potential Exposure via Indirect
Ingestion (ng/day)
Potential Absorbed Dose via
Inhalation (ng/kg/day)
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)(d)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)
Aggregated Potential Exposure
(ng/day)
Aggregated Potential Absorbed
Dose (ng/kg/day)
0.403
0.228
0.915
0.538
0.170
0.800
0.157
0.116
0.003"
0.892
0.896
0.005**
0.737
0.903
0.552
0.413
0.278
0.153
0.541
0.494
0.260
0.773
0.136
0.262
1.000

<0.001**
O.001**

<0.001**


0.047*

0.558
0.253

0.714


0.297

0.861
0.786

0.931


0.127

0.045*
0.376

0.099


PCB52
Potential Exposure via Inhalation
(ng/day)
Potential Exposure via Dietary
Ingestion (ng/day)(c)
Potential Exposure via Indirect
Ingestion (ng/day)(c)
Potential Absorbed Dose via
Inhalation (ng/kg/day)
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)(c)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)(c)
0.582
-
-
0.876
-
-
0.859
-
-
0.659
-
-
0.112
-
-
0.453
-
-
1.000

-
<0.001**

-
0.928

-
0.546

-
0.462

-
0.936

-
0.063

-
0.246

-
PCB95
Potential Exposure via Inhalation
(ng/day)
Potential Exposure via Dietary
Ingestion (ng/day)(c)
0.818
-
0.434
-
0.395
-
1.000

0.808

0.757

0.059

                                       R-24

-------
Table R-3.   P-values of Statistical Tests to Determine the Significance of Urbanicity,
            Income Status, and Day Care Attendance on 1) NC Children's Exposure and
            Absorbed Dose Estimates, and 2) the Difference in Estimates Between NC
            Children and Adults in the Same Household(a) (cont.)
Exposure/Dose/Biomarker
Parameter and Pathway
Potential Exposure via Indirect
Ingestion (ng/day)(c)
Potential Absorbed Dose via
Inhalation (ng/kg/day)
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)(c)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)(c)
Analysis on Child Measures
Urbanicity
Effect
-
0.912
-
-
Income
Status
Effect
-
0.632
-
-
Day Care
Attendance
Effect
-
0.952
-
-
Analysis on Differences Between
Child and Adult Measures in Same Household
Child vs.
Adult
Difference'111
-
<0.001"

-
Urbanicity
Effect
-
0.421

-
Income
Status
Effect
-
0.653

-
Day Care
Attendance
Effect
-
0.276

-
PCB 101
Potential Exposure via Inhalation
(ng/day)
Potential Exposure via Dietary
Ingestion (ng/day)(c)
Potential Exposure via Indirect
Ingestion (ng/day)(c)
Potential Absorbed Dose via
Inhalation (ng/kg/day)
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)(c)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)(c)
0.448
-
-
0.675
-
-
0.544
-
-
0.731
-
-
0.573
-
-
0.915
-
-
1.000

-
O.001"

-
0.802

-
0.452

-
0.992

-
0.625

-
0.004"

-
0.041*

-
                                       R-25

-------
Table R-3.    P-values of Statistical Tests to Determine the Significance of Urbanicity,
                Income Status, and Day Care Attendance on 1) NC Children's Exposure and
                Absorbed Dose Estimates, and 2) the Difference in Estimates Between NC
                Children and Adults in the Same Household(a) (cont.)
Exposure/Dose/Biomarker
Parameter and Pathway
Analysis on Child Measures
Urbanicity
Effect
Income
Status
Effect
Day Care
Attendance
Effect
Analysis on Differences Between
Child and Adult Measures in Same Household
Child vs.
Adult
Difference'111
Urbanicity
Effect
Income
Status
Effect
Day Care
Attendance
Effect
3,5,6-TCP (3,5,6-trichloro-2-pyridinol)
Potential Exposure via Inhalation
(ng/day)
Potential Exposure via Dietary
Ingestion (ng/day)
Potential Exposure via Indirect
Ingestion (ng/day)
Potential Absorbed Dose via
Inhalation (ng/kg/day)
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)
Aggregated Potential Exposure
(ng/day)
Aggregated Potential Absorbed
Dose (ng/kg/day)
0.912
0.451
0.320
0.863
0.633
0.419
0.403
0.569
0.870
0.011*
0.778
0.745
0.003**
0.985
0.012*
0.003**
0.216
0.033*
0.793
0.419
0.068
0.505
0.034*
0.080
1.000
0.198
<0.001**
O.001**
O.001**
<0.001**
0.247
O.001**
0.502
0.968
0.500
0.897
0.845
0.685
0.892
0.965
0.138
0.892
0.406
0.967
0.813
0.304
0.822
0.942
0.499
0.004**
0.533
0.392
0.010*
0.389
0.013*
0.031*
(a) Blank cells in this table indicate that insufficient data were available in this study to make the statistical comparison specified in
the column heading for the given pollutant and exposure route.
(b) Tests for statistical significance of the child-adult differences are one-sided tests to determine whether estimates for children are
significantly higher than for adults.
(c) Tests were not performed because, for each environmental sample type whose measurements were used to calculate the
potential exposure/absorbed dose, less than 45% of the measurements were detected.
(d) For each environmental sample type whose measurements were used to calculate the potential exposure/absorbed dose, less
than 45% of the measurements were detected.  However, tests were performed because this was one of the eight pollutants
mentioned at the end of Section 9.2.
(e) The largest detection percentage among the environmental sample types whose measurements were used to calculate the
potential exposure/absorbed dose was between 45 and 50%.

* Statistically significant at the 0.05 level, but not at the 0.01  level.
** Statistically significant at the 0.01 level.
                                                   R-26

-------
Table R-4.   P-values of Statistical Tests to Determine the Significance of Urbanicity,
            Income Status, and Day Care Attendance on 1) OH Children's Exposure and
            Absorbed Dose Estimates, and 2) the Difference in Estimates Between OH
            Children and Adults in the Same Household(a)
Exposure/Dose/Biomarker
Parameter and Pathway
Analysis on Child Measures
Urbanicity
Effect
Income
Status
Effect
Day Care
Attendance
Effect
Analysis on Differences Between
Child and Adult Measures in Same Household
Child vs.
Adult
Difference1"1
Urbanicity
Effect
Income
Status
Effect
Day Care
Attendance
Effect
Benz[a]anthracene
Potential Exposure via Inhalation
(ng/day)(c)
Potential Exposure via Dietary
Ingestion (ng/day)(c)
Potential Exposure via Indirect
Ingestion (ng/day)
Potential Absorbed Dose via
Inhalation (ng/kg/day)(c)
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)(c)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)
-
-
0.001"
-
-
0.001"
-
-
0.001"
-
-
0.002"
-
-
<0.001"
-
-
<0.001"
-

O.001"
-

O.001"
-

0.386
-

0.338
-

0.022*
-

0.074
-

<0.001"
-

<0.001"
Benzo[fo]fluoranthene
Potential Exposure via Inhalation
(ng/day)(c)
Potential Exposure via Dietary
Ingestion (ng/day)(c)
Potential Exposure via Indirect
Ingestion (ng/day)
Potential Absorbed Dose via
Inhalation (ng/kg/day)(c)
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)(c)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)
-
-
<0.001"
-
-
0.001"
-
-
0.001"
-
-
0.001"
-
-
<0.001"
-
-
<0.001"
-

<0.001"
-

O.001"
-

0.544
-

0.466
-

0.029*
-

0.085
-

<0.001"
-

<0.001"
Benzo[fc]fluoranthene
Potential Exposure via Inhalation
(ng/day)(c)
Potential Exposure via Dietary
Ingestion (ng/day)(c)
Potential Exposure via Indirect
Ingestion (ng/day)
Potential Absorbed Dose via
Inhalation (ng/kg/day)(c)
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)(c)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)
-
-
0.001"
-
-
0.002"
-
-
0.001"
-
-
0.001"
-
-
<0.001"
-
-
<0.001"
-

<0.001"
-

O.001"
-

0.371
-

0.328
-

0.024*
-

0.074
-

<0.001"
-

<0.001"
Benzo[g/ii]perylene
Potential Exposure via Inhalation
(ng/day)(c)
Potential Exposure via Dietary
Ingestion (ng/day)(c)
-
-
-
-
-
-
-

-

-

-

                                       R-27

-------
Table R-4.   P-values of Statistical Tests to Determine the Significance of Urbanicity,
            Income Status, and Day Care Attendance on 1) OH Children's Exposure and
            Absorbed Dose Estimates, and 2) the Difference in Estimates Between OH
            Children and Adults in the Same Household(a) (cont.)
Exposure/Dose/Biomarker
Parameter and Pathway
Potential Exposure via Indirect
Ingestion (ng/day)
Potential Absorbed Dose via
Inhalation (ng/kg/day)(c)
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)(c)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)
Analysis on Child Measures
Urbanicity
Effect
0.001"
-
-
0.002"
Income
Status
Effect
0.001"
-
-
0.001"
Day Care
Attendance
Effect
<0.001"
-
-
<0.001"
Analysis on Differences Between
Child and Adult Measures in Same Household
Child vs.
Adult
Difference'111
<0.001"
-

O.001"
Urbanicity
Effect
0.510
-

0.441
Income
Status
Effect
0.037*
-

0.105
Day Care
Attendance
Effect
<0.001"
-

<0.001"
Benzo[a]pyrene
Potential Exposure via Inhalation
(ng/day)(c)
Potential Exposure via Dietary
Ingestion (ng/day)(c)
Potential Exposure via Indirect
Ingestion (ng/day)
Potential Absorbed Dose via
Inhalation (ng/kg/day)(c)
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)(c)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)
-
-
0.001"
-
-
0.002"
-
-
<0.001"
-
-
0.001"
-
-
<0.001"
-
-
0.001"
-

<0.001"
-

<0.001"
-

0.390
-

0.344
-

0.032*
-

0.096
-

<0.001"
-

<0.001"
Benzo[e]pyrene
Potential Exposure via Inhalation
(ng/day)(c)
Potential Exposure via Dietary
Ingestion (ng/day)(c)
Potential Exposure via Indirect
Ingestion (ng/day)
Potential Absorbed Dose via
Inhalation (ng/kg/day)(c)
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)(c)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)
-
-
0.001"
-
-
0.002"
-
-
0.001"
-
-
0.001"
-
-
<0.001"
-
-
<0.001"
-

<0.001"
-

<0.001"
-

0.488
-

0.420
-

0.033*
-

0.096
-

<0.001"
-

<0.001"
Benzylbutylphthalate
Potential Exposure via Inhalation
(ng/day)(c)
Potential Exposure via Dietary
Ingestion (ng/day)
Potential Exposure via Indirect
Ingestion (ng/day)
Potential Absorbed Dose via
Inhalation (ng/kg/day)(c)
-
0.281
0.174
-
-
0.718
0.861
-
-
0.008"
<0.001"
-
-

O.001"
-
-

0.915
-
-

0.039*
-
-

<0.001"
-
                                       R-28

-------
Table R-4.   P-values of Statistical Tests to Determine the Significance of Urbanicity,
            Income Status, and Day Care Attendance on 1) OH Children's Exposure and
            Absorbed Dose Estimates, and 2) the Difference in Estimates Between OH
            Children and Adults in the Same Household(a) (cont.)
Exposure/Dose/Biomarker
Parameter and Pathway
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)
Analysis on Child Measures
Urbanicity
Effect
0.294
0.190
Income
Status
Effect
0.894
0.917
Day Care
Attendance
Effect
0.023*
0.001**
Analysis on Differences Between
Child and Adult Measures in Same Household
Child vs.
Adult
Difference'111

<0.001**
Urbanicity
Effect

0.950
Income
Status
Effect

0.088
Day Care
Attendance
Effect

o.oor*
Bisphenol-A
Potential Exposure via Inhalation
(ng/day)
Potential Exposure via Dietary
Ingestion (ng/day)
Potential Exposure via Indirect
Ingestion (ng/day)
Potential Absorbed Dose via
Inhalation (ng/kg/day)
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)
Aggregated Potential Exposure
(ng/day)
Aggregated Potential Absorbed
Dose (ng/kg/day)
0.814
0.601
0.876
0.843
0.532
0.907
0.241
0.213
0.048*
0.522
0.068
0.109
0.483
0.097
0.312
0.346
0.064
0.068
0.747
0.153
0.134
0.977
0.066
0.155
1.000

O.001**
<0.001**

O.001**


0.721

0.668
0.824

0.526


0.858

0.049*
0.618

0.217


0.148

0.014*
0.307

0.042*


a/p/ia-Chlordane
Potential Exposure via Inhalation
(ng/day)
Potential Exposure via Dietary
Ingestion (ng/day)(c)
Potential Exposure via Indirect
Ingestion (ng/day)
Potential Absorbed Dose via
Inhalation (ng/kg/day)
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)(c)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)
0.929
-
0.370
0.978
-
0.386
0.142
-
0.987
0.172
-
0.957
0.393
-
0.873
0.263
-
0.950
1.000

<0.001**
O.001**

<0.001**
0.822

0.628
0.965

0.526
0.046*

0.005**
0.889

0.044*
0.661

0.004**
0.998

0.030*
gamma-Chlordane
Potential Exposure via Inhalation
(ng/day)
Potential Exposure via Dietary
Ingestion (ng/day)(c)
Potential Exposure via Indirect
Ingestion (ng/day)
Potential Absorbed Dose via
Inhalation (ng/kg/day)
0.831
-
0.462
0.880
0.178
-
0.892
0.210
0.442
-
0.780
0.302
1.000

O.001**
O.001**
0.871

0.632
0.947
0.044*

0.009**
0.865
0.265

0.002**
0.661
                                       R-29

-------
Table R-4.   P-values of Statistical Tests to Determine the Significance of Urbanicity,
            Income Status, and Day Care Attendance on 1) OH Children's Exposure and
            Absorbed Dose Estimates, and 2) the Difference in Estimates Between OH
            Children and Adults in the Same Household(a) (cont.)
Exposure/Dose/Biomarker
Parameter and Pathway
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)(c)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)
Analysis on Child Measures
Urbanicity
Effect
-
0.483
Income
Status
Effect
-
0.865
Day Care
Attendance
Effect
-
0.948
Analysis on Differences Between
Child and Adult Measures in Same Household
Child vs.
Adult
Difference'111

<0.001"
Urbanicity
Effect

0.528
Income
Status
Effect

0.063
Day Care
Attendance
Effect

0.019*
Chlorpyrifos
Potential Exposure via Inhalation
(ng/day)
Potential Exposure via Dietary
Ingestion (ng/day)
Potential Exposure via Indirect
Ingestion (ng/day)
Potential Absorbed Dose via
Inhalation (ng/kg/day)
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)
Aggregated Potential Exposure
(ng/day)
Aggregated Potential Absorbed
Dose (ng/kg/day)
0.213
0.796
0.438
0.230
0.828
0.452
0.911
0.789
0.372
0.002"
0.421
0.543
0.001"
0.376
0.033*
0.034*
0.177
0.911
0.006"
0.215
0.674
0.014*
0.433
0.753
1.000

O.001"
<0.001"

O.001"


0.165

0.924
0.236

0.895


0.177

0.174
0.468

0.303


0.101

<0.001"
0.087

<0.001"


Chrysene
Potential Exposure via Inhalation
(ng/day)(e)
Potential Exposure via Dietary
Ingestion (ng/day)(c)
Potential Exposure via Indirect
Ingestion (ng/day)
Potential Absorbed Dose via
Inhalation (ng/kg/day)(e)
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)(c)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)
0.163
-
0.001"
0.149
-
0.001"
0.321
-
0.001"
0.566
-
0.001"
0.069
-
<0.001"
0.092
-
<0.001"
1.000

<0.001"
O.001"

<0.001"
0.552

0.449
0.388

0.384
0.282

0.029*
0.205

0.086
0.004"

<0.001"
0.064

<0.001"
Cyfluthrin
Potential Exposure via Inhalation
(ng/day)(c)
Potential Exposure via Dietary
Ingestion (ng/day)(c)
Potential Exposure via Indirect
Ingestion (ng/day)
Potential Absorbed Dose via
Inhalation (ng/kg/day)(c)
-
-
0.034*
-
-
-
0.402
-
-
-
0.135
-
-

O.001"
-
-

0.189
-
-

0.174
-
-

<0.001"
-
                                       R-30

-------
Table R-4.   P-values of Statistical Tests to Determine the Significance of Urbanicity,
            Income Status, and Day Care Attendance on 1) OH Children's Exposure and
            Absorbed Dose Estimates, and 2) the Difference in Estimates Between OH
            Children and Adults in the Same Household(a) (cont.)
Exposure/Dose/Biomarker
Parameter and Pathway
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)(c)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)
Analysis on Child Measures
Urbanicity
Effect
-
0.041*
Income
Status
Effect
-
0.438
Day Care
Attendance
Effect
-
0.207
Analysis on Differences Between
Child and Adult Measures in Same Household
Child vs.
Adult
Difference'111

<0.001"
Urbanicity
Effect

0.186
Income
Status
Effect

0.351
Day Care
Attendance
Effect

0.001"
Diazinon
Potential Exposure via Inhalation
(ng/day)
Potential Exposure via Dietary
Ingestion (ng/day)(d)
Potential Exposure via Indirect
Ingestion (ng/day)
Potential Absorbed Dose via
Inhalation (ng/kg/day)
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)(d)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)
Aggregated Potential Exposure
(ng/day)
Aggregated Potential Absorbed
Dose (ng/kg/day)
0.250
0.265
0.443
0.267
0.257
0.440
0.591
0.629
0.128
0.200
0.514
0.130
0.192
0.500
0.277
0.223
0.018*
0.003"
0.009"
0.035*
0.033*
0.015*
0.015*
0.043*
0.730

O.001"
<0.001"

O.001"


0.168

0.218
0.124

0.182


0.088

0.411
0.764

0.501


0.011*

<0.001"
0.018*

0.001"


Dibenzo[a,/i]anthracene
Potential Exposure via Inhalation
(ng/day)(c)
Potential Exposure via Dietary
Ingestion (ng/day)(c)
Potential Exposure via Indirect
Ingestion (ng/day)
Potential Absorbed Dose via
Inhalation (ng/kg/day)(c)
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)(c)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)
-
-
0.001"
-
-
0.001"
-
-
0.001"
-
-
0.002"
-
-
<0.001"
-
-
<0.001"
-

<0.001"
-

<0.001"
-

0.435
-

0.384
-

0.035*
-

0.104
-

<0.001"
-

<0.001"
Di-n-butylphthalate
Potential Exposure via Inhalation
(ng/day)
Potential Exposure via Dietary
Ingestion (ng/day)(d)
Potential Exposure via Indirect
Ingestion (ng/day)
Potential Absorbed Dose via
Inhalation (ng/kg/day)
0.018*
0.890
0.348
0.016*
0.634
0.615
0.193
0.773
0.012*
0.008"
0.002"
0.039*
1.000

O.001"
O.001"
0.192

0.837
0.119
0.143

0.006"
0.631
0.012*

<0.001"
0.063
                                       R-31

-------
Table R-4.   P-values of Statistical Tests to Determine the Significance of Urbanicity,
            Income Status, and Day Care Attendance on 1) OH Children's Exposure and
            Absorbed Dose Estimates, and 2) the Difference in Estimates Between OH
            Children and Adults in the Same Household(a) (cont.)
Exposure/Dose/Biomarker
Parameter and Pathway
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)(d)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)
Aggregated Potential Exposure
(ng/day)
Aggregated Potential Absorbed
Dose (ng/kg/day)
Analysis on Child Measures
Urbanicity
Effect
0.875
0.434
0.818
0.841
Income
Status
Effect
0.425
0.206
0.476
0.382
Day Care
Attendance
Effect
0.031*
0.005**
0.009**
0.039*
Analysis on Differences Between
Child and Adult Measures in Same Household
Child vs.
Adult
Difference'111

<0.001**


Urbanicity
Effect

0.609


Income
Status
Effect

0.053


Day Care
Attendance
Effect

<0.001**


p,p'-DDE
Potential Exposure via Inhalation
(ng/day)(c)
Potential Exposure via Dietary
Ingestion (ng/day)
Potential Exposure via Indirect
Ingestion (ng/day)(e)
Potential Absorbed Dose via
Inhalation (ng/kg/day)(c)
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)(e)
-
0.872
0.826
-
0.888
0.828
-
0.433
0.754
-
0.410
0.736
-
0.125
0.665
-
0.225
0.824
1.000

<0.001**
<0.001**

<0.001**
0.597

0.114
0.920

0.060
0.466

0.022*
0.669

0.066
0.044*

0.003**
0.074

0.007**
2,4-D (2,4-dichlorophenoxyacetic acid)
Potential Exposure via Inhalation
(ng/day)(d)
Potential Exposure via Dietary
Ingestion (ng/day)(d)
Potential Exposure via Indirect
Ingestion (ng/day)
Potential Absorbed Dose via
Inhalation (ng/kg/day)(d)
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)(d)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)
Aggregated Potential Exposure
(ng/day)
Aggregated Potential Absorbed
Dose (ng/kg/day)
0.156
0.327
0.044*
0.134
0.346
0.042*
0.285
0.303
0.434
0.999

-------
Table R-4.   P-values of Statistical Tests to Determine the Significance of Urbanicity,
            Income Status, and Day Care Attendance on 1) OH Children's Exposure and
            Absorbed Dose Estimates, and 2) the Difference in Estimates Between OH
            Children and Adults in the Same Household(a) (cont.)
Exposure/Dose/Biomarker
Parameter and Pathway
Potential Exposure via Indirect
Ingestion (ng/day)
Potential Absorbed Dose via
Inhalation (ng/kg/day)(c)
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)(c)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)
Analysis on Child Measures
Urbanicity
Effect
0.001"
-
-
0.002"
Income
Status
Effect
0.001"
-
-
0.001"
Day Care
Attendance
Effect
<0.001"
-
-
<0.001"
Analysis on Differences Between
Child and Adult Measures in Same Household
Child vs.
Adult
Difference'111
<0.001"
-

O.001"
Urbanicity
Effect
0.536
-

0.463
Income
Status
Effect
0.035*
-

0.096
Day Care
Attendance
Effect
<0.001"
-

<0.001"
Pentachlorophenol
Potential Exposure via Inhalation
(ng/day)
Potential Exposure via Dietary
Ingestion (ng/day)(c)
Potential Exposure via Indirect
Ingestion (ng/day)
Potential Absorbed Dose via
Inhalation (ng/kg/day)
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)(c)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)
0.196
-
0.364
0.183
-
0.399
0.717
-
0.430
0.642
-
0.520
0.279
-
0.296
0.226
-
0.448
1.000
-
<0.001"
O.001"
-
<0.001"
0.984
-
0.682
0.976
-
0.518
0.641
-
0.180
0.776
-
0.378
0.266
-
0.049*
0.399
-
0.113
c/s-Permethrin
Potential Exposure via Inhalation
(ng/day)(d)
Potential Exposure via Dietary
Ingestion (ng/day)(d)
Potential Exposure via Indirect
Ingestion (ng/day)
Potential Absorbed Dose via
Inhalation (ng/kg/day)(d)
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)(d)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)
Aggregated Potential Exposure
(ng/day)
Aggregated Potential Absorbed
Dose (ng/kg/day)
0.643
0.680
0.076
0.675
0.695
0.082
0.955
0.945
0.288
0.860
0.661
0.384
0.830
0.760
0.406
0.355
0.103
0.005"
0.039*
0.243
0.008"
0.071
0.013*
0.021*
1.000

<0.001"
O.001"

<0.001"


0.966

0.155
0.818

0.121


0.545

0.048*
0.772

0.144


0.050

<0.001"
0.165

<0.001"


frans-Permethrin
Potential Exposure via Inhalation
(ng/day)(d)
Potential Exposure via Dietary
Ingestion (ng/day)(d)
0.826
0.690
0.400
0.891
0.086
0.007"
1.000

0.908

0.360

0.074

                                       R-33

-------
Table R-4.   P-values of Statistical Tests to Determine the Significance of Urbanicity,
            Income Status, and Day Care Attendance on 1) OH Children's Exposure and
            Absorbed Dose Estimates, and 2) the Difference in Estimates Between OH
            Children and Adults in the Same Household(a) (cont.)
Exposure/Dose/Biomarker
Parameter and Pathway
Potential Exposure via Indirect
Ingestion (ng/day)
Potential Absorbed Dose via
Inhalation (ng/kg/day)(d)
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)(d)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)
Aggregated Potential Exposure
(ng/day)
Aggregated Potential Absorbed
Dose (ng/kg/day)
Analysis on Child Measures
Urbanicity
Effect
0.141
0.845
0.705
0.147
0.796
0.759
Income
Status
Effect
0.858
0.482
0.861
0.741
0.852
0.697
Day Care
Attendance
Effect
0.125
0.212
0.010*
0.186
0.135
0.244
Analysis on Differences Between
Child and Adult Measures in Same Household
Child vs.
Adult
Difference'111
<0.001**
<0.001**

O.001**


Urbanicity
Effect
0.338
0.780

0.271


Income
Status
Effect
0.010*
0.824

0.078


Day Care
Attendance
Effect
<0.001**
0.187

0.001**


PCB52
Potential Exposure via Inhalation
(ng/day)
Potential Exposure via Dietary
Ingestion (ng/day)
Potential Exposure via Indirect
Ingestion (ng/day)
Potential Absorbed Dose via
Inhalation (ng/kg/day)
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)
0.126

0.487
0.127

0.493
0.685

0.351
0.650

0.415
0.211

0.108
0.291

0.198
1.000

O.001**
<0.001**

O.001**
0.851

0.394
0.960

0.262
0.036*

0.551
0.991

0.802
0.076

o.oor*
0.246

0.003**
PCB95
Potential Exposure via Inhalation
(ng/day)
Potential Exposure via Dietary
Ingestion (ng/day)
Potential Exposure via Indirect
Ingestion (ng/day)(c)
Potential Absorbed Dose via
Inhalation (ng/kg/day)
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)(c)
0.419

-
0.431

-
0.848

-
0.790

-
0.140

-
0.209

-
1.000

-
<0.001**

-
0.931

-
0.835

-
0.528

-
0.755

-
0.033*

-
0.096

-
PCB 101
Potential Exposure via Inhalation
(ng/day)
Potential Exposure via Dietary
Ingestion (ng/day)
0.209

0.452

0.032*

1.000

0.739

0.832

0.027*

                                       R-34

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Table R-4.    P-values of Statistical Tests to Determine the Significance of Urbanicity,
                Income Status, and Day Care Attendance on 1) OH Children's Exposure and
                Absorbed Dose Estimates, and 2) the Difference in Estimates Between OH
                Children and Adults in the Same Household(a)  (cont.)
Exposure/Dose/Biomarker
Parameter and Pathway
Potential Exposure via Indirect
Ingestion (ng/day)(c)
Potential Absorbed Dose via
Inhalation (ng/kg/day)
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)(c)
Analysis on Child Measures
Urbanicity
Effect
-
0.213

-
Income
Status
Effect
-
0.421

-
Day Care
Attendance
Effect
-
0.057

-
Analysis on Differences Between
Child and Adult Measures in Same Household
Child vs.
Adult
Difference'111
-
<0.001**

-
Urbanicity
Effect
-
0.975

-
Income
Status
Effect
-
0.483

-
Day Care
Attendance
Effect
-
0.085

-
3,5,6-TCP (3,5,6-trichloro-2-pyridinol)
Potential Exposure via Inhalation
(ng/day)
Potential Exposure via Dietary
Ingestion (ng/day)
Potential Exposure via Indirect
Ingestion (ng/day)
Potential Absorbed Dose via
Inhalation (ng/kg/day)
Potential Absorbed Dose via
Dietary Ingestion (ng/kg/day)
Potential Absorbed Dose via
Indirect Ingestion (ng/kg/day)
Aggregated Potential Exposure
(ng/day)
Aggregated Potential Absorbed
Dose (ng/kg/day)
0.240
0.521
0.198
0.278
0.519
0.223
0.245
0.218
0.016*
0.476
0.777
0.016*
0.452
0.879
0.631
0.684
0.958
0.522
0.047*
0.806
0.737
0.085
0.397
0.600
1.000
0.617
<0.001**
O.001**
O.001**
<0.001**
0.498
O.001**
0.678
0.704
0.191
0.794
0.642
0.139
0.493
0.402
0.302
0.580
0.113
0.157
0.603
0.270
0.854
0.691
0.043*
<0.001**
0.006**
0.296
<0.001**
0.017*
<0.001**
<0.001**
(a) Blank cells in this table indicate that insufficient data were available in this study to make the statistical comparison specified in
the column heading for the given pollutant and exposure route.
(b) Tests for statistical significance of the child-adult differences are one-sided tests to determine whether estimates for children are
significantly higher than for adults.
(c) Tests were not performed because, for each environmental sample type whose measurements were used to calculate the
potential exposure/absorbed dose, less than 45% of the measurements were detected.
(d) For each environmental sample type whose measurements were used to calculate the potential exposure/absorbed dose, less
than 45% of the measurements were detected.  However, tests were performed because this was one of the eight pollutants
mentioned at the end of Section 9.2.
(e) The largest detection percentage among the environmental sample types whose measurements were used to calculate the
potential exposure/absorbed dose was between 45 and 50%.

* Statistically significant at the 0.05 level, but not at the 0.01  level.
** Statistically significant at the 0.01 level.
                                                   R-35

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Table R-5.   Estimated Ratio Between Selected Strata of Geometric Mean Urinary
              Biomarker Concentration Data in Participating NC Children, and 95%
              Confidence Intervals on This Ratio
Exposure/Dose/Biomarker Parameter
and Pathway
Estimated Ratio of Geometric Means (95% CI)
Urban vs. Rural
Low Income vs.
Mid/High Income
Day Care vs.
Home Children
2,4-D (2,4-dichlorophenoxyacetic acid)
Urinary concentration (ng/mL)
Urinary concentration, adjusted for specific
gravity (ng/mL)
Urinary concentration, adjusted for creatinine
(umoles/mole)
1.41(0.92,2.16)
1.41 (0.92,2.16)
1.21 (0.77,1.92)
1.23 (0.90,1.69)
1.23 (0.90,1.69)
1.29(0.93,1.79)
1.28(0.94,1.75)
1.28(0.94,1.75)
1.10(0.76,1.60)
Pentachlorophenol
Urinary concentration (ng/mL)
Urinary concentration, adjusted for specific
gravity (ng/mL)
Urinary concentration, adjusted for creatinine
(umoles/mole)
1.20(0.75,1.92)
1.19(0.74,1.91)
1.19(0.72,1.96)
1.25 (0.90,1.75)
1.25 (0.90,1.75)
1.22(0.86,1.73)
0.96(0.65,1.43)
0.96(0.65,1.43)
0.85 (0.56,1.27)
3,5,6-TCP(3,5,6-trichloro-2-pyridinol)
Urinary concentration (ng/mL)
Urinary concentration, adjusted for specific
gravity (ng/mL)
Urinary concentration, adjusted for creatinine
(umoles/mole)
0.99(0.60,1.62)
0.98(0.60,1.61)
1.02(0.63,1.64)
0.90(0.66,1.24)
0.90(0.66,1.24)
0.97(0.73,1.29)
1.08(0.70,1.69)
1.09(0.70,1.69)
0.91 (0.60,1.39)
* Statistically significantly different from 1 at the 0.05 level, but not at the 0.01 level.
** Statistically significantly different from 1 at the 0.01 level.
                                             R-36

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Table R-6.   Estimated Ratio Between Selected Strata of Geometric Mean Urinary
              Biomarker Concentration Data in Participating OH Children, and 95%
              Confidence Intervals on This Ratio
Exposure/Dose/Biomarker Parameter
and Pathway
Estimated Ratio of Geometric Means (95% CI)
Urban vs. Rural
Low Income vs.
Mid/High Income
Day Care vs.
Home Children
2,4-D (2,4-dichlorophenoxyacetic acid)
Urinary concentration (ng/mL)
Urinary concentration, adjusted for specific
gravity (ng/mL)
Urinary concentration, adjusted for creatinine
(umoles/mole)
0.75 (0.45,1.25)
0.75 (0.45,1.25)
0.64(0.40,1.02)
1.36(0.96,1.93)
1.36(0.95,1.93)
1.34(0.97,1.87)
0.65* (0.46,0.92)
0.65* (0.46,0.93)
0.68* (0.49,0.96)
1-hydroxypyrene
Urinary concentration (ng/mL)
Urinary concentration, adjusted for specific
gravity (ng/mL)
Urinary concentration, adjusted for creatinine
(umoles/mole)
0.84(0.55,1.30)
0.84(0.55,1.30)
0.81 (0.54,1.22)
1.22(0.92,1.63)
1.21(0.91,1.61)
1.12(0.85,1.49)
0.85(0.62,1.18)
0.86(0.62,1.19)
0.89(0.65,1.21)
Pentachlorophenol
Urinary concentration (ng/mL)
Urinary concentration, adjusted for specific
gravity (ng/mL)
Urinary concentration, adjusted for creatinine
(umoles/mole)
0.69(0.42,1.15)
0.69(0.42,1.15)
0.67(0.40,1.11)
1.01 (0.72,1.43)
1.01 (0.72,1.43)
0.95(0.69,1.31)
0.77(0.53,1.12)
0.77(0.53,1.12)
0.80(0.54,1.20)
3-phenoxybenzoic acid
Urinary concentration (ng/mL)
Urinary concentration, adjusted for specific
gravity (ng/mL)
Urinary concentration, adjusted for creatinine
(umoles/mole)
1.19(0.62,2.30)
1.18(0.61,2.28)
1.15 (0.53,2.48)
1.16(0.75,1.78)
1.21 (0.78,1.87)
1.05 (0.62,1.76)
0.98(0.60,1.61)
0.95 (0.58,1.55)
0.99(0.56,1.76)
3,5,6-TCP(3,5,6-trichloro-2-pyridinol)
Urinary concentration (ng/mL)
Urinary concentration, adjusted for specific
gravity (ng/mL)
Urinary concentration, adjusted for creatinine
(umoles/mole)
1.19(0.78,1.82)
1.20(0.79,1.82)
1.11 (0.73,1.68)
1.13(0.85,1.52)
1.13 (0.84,1.51)
1.04(0.78,1.40)
0.84(0.62,1.14)
0.85 (0.63,1.14)
0.82(0.61,1.11)
* Statistically significantly different from 1 at the 0.05 level, but not at the 0.01 level.
** Statistically significantly different from 1 at the 0.01 level.
                                             R-37

-------
Table R-7.    P-values of Statistical Tests to Determine the Significance of Urbanicity,
               Income  Status, and Day Care Attendance on 1) NC Children's Urinary
               Biomarker Concentrations, and 2) the Difference in Concentrations Between
               NC Children and Adults in the Same Household
Exposure/Dose/Biomarker
Parameter and Pathway
Analysis on Child Measures
Urbanicity
Effect
Income
Status
Effect
Day Care
Attendance
Effect
Analysis on Differences Between
Child and Adult Measures in Same Household
Child vs.
Adult
Difference'"1
Urbanicity
Effect
Income
Status
Effect
Day Care
Attendance
Effect
2,4-D (2,4-dichlorophenoxyacetic acid)
Urinary concentration (ng/mL)
Urinary concentration, adjusted
for specific gravity (ng/mL)
Urinary concentration, adjusted
for creatinine (umoles/mole)
0.109
0.113
0.395
0.187
0.188
0.127
0.108
0.108
0.582
0.771
0.762
<0.001**
0.492
0.501
0.578
0.148
0.148
0.091
0.109
0.108
0.054
Pentachlorophenol
Urinary concentration (ng/mL)
Urinary concentration, adjusted
for specific gravity (ng/mL)
Urinary concentration, adjusted
for creatinine (umoles/mole)
0.442
0.450
0.496
0.178
0.179
0.266
0.846
0.848
0.404
<0.001**
<0.001**
O.001**
0.762
0.744
0.447
0.069
0.068
0.014*
0.832
0.822
0.422
3,5,6-TCP (3,5,6-trichloro-2-pyridinol)
Urinary concentration (ng/mL)
Urinary concentration, adjusted
for specific gravity (ng/mL)
Urinary concentration, adjusted
for creatinine (umoles/mole)
0.953
0.946
0.942
0.517
0.520
0.828
0.712
0.710
0.667
0.017*
0.015*
O.001**
0.523
0.510
0.569
0.538
0.536
0.352
0.524
0.517
0.230
(a) Tests for statistical significance of the child-adult differences are one-sided tests to determine whether estimates for children are
significantly higher than for adults.

* Statistically significant at the 0.05 level, but not at the 0.01 level.
** Statistically significant at the 0.01 level.
                                              R-38

-------
Table R-8.    P-values of Statistical Tests to Determine the Significance of Urbanicity,
               Income  Status, and Day Care Attendance on 1) OH Children's Urinary
               Biomarker Concentrations, and 2) the Difference in Concentrations Between
               OH Children and Adults in the Same Household
Exposure/Dose/Biomarker
Parameter and Pathway
Analysis on Child Measures
Urbanicity
Effect
Income
Status
Effect
Day Care
Attendance
Effect
Analysis on Differences Between
Child and Adult Measures in Same Household
Child vs.
Adult
Difference'"1
Urbanicity
Effect
Income
Status
Effect
Day Care
Attendance
Effect
2,4-D (2,4-dichlorophenoxyacetic acid)
Urinary concentration (ng/mL)
Urinary concentration, adjusted
for specific gravity (ng/mL)
Urinary concentration, adjusted
for creatinine (umoles/mole)
0.267
0.265
0.059
0.087
0.088
0.078
0.017*
0.018*
0.028*
0.013*
0.013*
<0.001**
0.699
0.706
0.379
0.320
0.321
0.131
0.028*
0.029*
0.127
1-hydroxypyrene
Urinary concentration (ng/mL)
Urinary concentration, adjusted
for specific gravity (ng/mL)
Urinary concentration, adjusted
for creatinine (umoles/mole)
0.425
0.429
0.309
0.172
0.190
0.424
0.323
0.353
0.442
0.109
0.105
O.001**
0.721
0.700
0.952
0.974
0.947
0.784
0.937
0.991
0.441
Pentachlorophenol
Urinary concentration (ng/mL)
Urinary concentration, adjusted
for specific gravity (ng/mL)
Urinary concentration, adjusted
for creatinine (umoles/mole)
0.156
0.154
0.120
0.936
0.941
0.748
0.165
0.167
0.283
O.001**
O.001**
O.001**
0.550
0.558
0.512
0.789
0.790
0.976
0.006**
0.006**
0.213
3-phenoxybenzoic acid
Urinary concentration (ng/mL)
Urinary concentration, adjusted
for specific gravity (ng/mL)
Urinary concentration, adjusted
for creatinine (umoles/mole)
0.600
0.625
0.720
0.497
0.392
0.865
0.941
0.831
0.968
0.292
0.298
<0.001**
0.689
0.681
0.545
0.401
0.311
0.318
0.164
0.121
0.747
3,5,6-TCP (3,5,6-trichloro-2-pyridinol)
Urinary concentration (ng/mL)
Urinary concentration, adjusted
for specific gravity (ng/mL)
Urinary concentration, adjusted
for creatinine (umoles/mole)
0.403
0.395
0.624
0.394
0.426
0.780
0.243
0.263
0.197
0.001**
0.001**
<0.001**
0.256
0.266
0.156
0.557
0.568
0.464
0.937
0.905
0.315
(a) Tests for statistical significance of the child-adult differences are one-sided tests to determine whether estimates for children are
significantly higher than for adults.

* Statistically significant at the 0.05 level, but not at the 0.01 level.
** Statistically significant at the 0.01 level.
                                              R-39

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Table R-9.   Estimated Mean Ratio Between NC Children and Adults in the Same
            Household of Potential Exposure and Potential Absorbed Dose Estimates,
            Calculated Overall and by Stratum, and 95% Confidence Intervals on This
            Mean Ratio
Exposure/Dose/
Biomarker
Parameter and
Pathway
Estimated Mean Ratio (95% CI)
in Preschool Children vs. Adults in the Same Household
Overall
Urban
Rural
Low Income
Mid/High
Income
Day Care
Children
Home
Children
Benz [«] anthracene
Potential Exposure via
Inhalation
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation
Potential Absorbed
Dose via Indirect
Ingestion
0.76
(0.7,0.81)**
2.18
(1.74,2.72)**
3.32
(2.97,3.70)**
9.44
(7.41,12.02)**
0.74
(0.69,0.79)**
2.14
(1.76,2.59)**
3.36
(3.06,3.69)**
9.53
(7.73,11.74)**
0.77
(0.68,0.87)**
2.22
(1.50,3.29)**
3.27
(2.70,3.97)**
9.35
(6.09,14.36)**
0.71
(0.65,0.77)**
2.15
(1.64,2.81)**
3.19
(2.80,3.64)**
9.62
(7.18,12.90)**
0.81
(0.74,0.88)**
2.20
(1.67,2.91)**
3.45
(3.01,3.95)**
9.26
(6.84,12.54)**
0.85
(0.76,0.95)**
2.64
(1.90,3.68)**
3.66
(3.12,4.3)**
11.17
(7.83,15.92)**
0.67
(0.63,0.72)**
1.80
(1.42,2.27)**
3.00
(2.68,3.37)**
7.98
(6.16,10.33)**
Benzo [b] fluoranthene
Potential Exposure via
Inhalation
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation
Potential Absorbed
Dose via Indirect
Ingestion
0.70
(0.65,0.76)**
2.10
(1.7,2.58)**
3.08
(2.77,3.43)**
9.11
(7.25,11.44)**
0.71
(0.67,0.76)**
2.10
(1.75,2.51)**
3.25
(2.97,3.56)**
9.37
(7.70,11.39)**
0.69
(0.61,0.79)**
2.09
(1.44,3.04)**
2.92
(2.43,3.52)**
8.85
(5.89,13.31)**
0.68
(0.62,0.74)**
2.18
(1.69,2.82)**
3.06
(2.70,3.48)**
9.79
(7.41,12.94)**
0.73
(0.67,0.8)**
2.01
(1.55,2.62)**
3.10
(2.72,3.53)**
8.47
(6.35,11.31)**
0.75
(0.67,0.85)**
2.44
(1.8,3.31)**
3.25
(2.77,3.81)**
10.36
(7.47,14.38)**
0.66
(0.61,0.71)**
1.80
(1.44,2.26)**
2.92
(2.62,3.26)**
8.00
(6.23,10.28)**
Benzo [k] fluoranthene
Potential Exposure via
Inhalation
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation
Potential Absorbed
Dose via Indirect
Ingestion
0.71
(0.68,0.75)**
2.11
(1.7,2.62)**
3.14
(2.89,3.42)**
9.16
(7.25,11.57)**
0.71
(0.68,0.74)**
2.11
(1.75,2.54)**
3.25
(3.03,3.49)**
9.40
(7.69,11.49)**
0.72
(0.66,0.77)**
2.12
(1.45,3.11)**
3.04
(2.61,3.54)**
8.93
(5.89,13.56)**
0.69
(0.66,0.73)**
2.16
(1.66,2.81)**
3.14
(2.84,3.48)**
9.69
(7.29,12.89)**
0.74
(0.7,0.78)**
2.07
(1.58,2.71)**
3.14
(2.82,3.49)**
8.66
(6.45,11.63)**
0.76
(0.71,0.82)**
2.49
(1.81,3.41)**
3.3
(2.93,3.71)**
10.51
(7.49,14.74)**
0.67
(0.64,0.7)**
1.80
(1.43,2.26)**
2.99
(2.73,3.29)**
7.99
(6.19,10.3)**
Benzo [ghi] perylene
Potential Exposure via
Inhalation
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation
Potential Absorbed
Dose via Indirect
Ingestion
0.68
(0.65,0.72)**
2.14
(1.73,2.64)**
3.00
(2.74,3.28)**
9.28
(7.37,11.68)**
0.68
(0.65,0.71)**
2.11
(1.76,2.54)**
3.11
(2.88,3.36)**
9.43
(7.74,11.50)**
0.68
(0.62,0.74)**
2.16
(1.48,3.15)**
2.89
(2.46,3.39)**
9.12
(6.05,13.77)**
0.67
(0.63,0.71)**
2.20
(1.70,2.85)**
3.07
(2.75,3.43)**
9.87
(7.45,13.08)**
0.69
(0.65,0.73)**
2.07
(1.59,2.71)**
2.93
(2.61,3.27)**
8.72
(6.51,11.66)**
0.69
(0.64,0.75)**
2.53
(1.85,3.44)**
2.99
(2.62,3.40)**
10.71
(7.67,14.94)**
0.67
(0.64,0.71)**
1.81
(1.44,2.27)**
3.01
(2.73,3.32)**
8.04
(6.25,10.33)**
Benzo[fl]pyrene
Potential Exposure via
Inhalation
0.71
(0.67,0.75)**
0.71
(0.67,0.74)**
0.72
(0.65,0.78)**
0.69
(0.65,0.73)**
0.73
(0.69,0.78)**
0.75
(0.69,0.82)**
0.67
(0.64,0.71)**
                                      R-40

-------
Table R-9.   Estimated Mean Ratio Between NC Children and Adults in the Same
            Household of Potential Exposure and Potential Absorbed Dose Estimates,
            Calculated Overall and by Stratum, and 95% Confidence Intervals on This
            Mean Ratio (cont.)
Exposure/Dose/
Biomarker
Parameter and
Pathway
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation
Potential Absorbed
Dose via Indirect
Ingestion
Estimated Mean Ratio (95% CI)
in Preschool Children vs. Adults in the Same Household
Overall
2.16
(1.74,2.68)**
3.12
(2.85,3.42)**
9.35
(7.40,11.82)**
Urban
2.09
(1.74,2.52)**
3.23
(2.98,3.49)**
9.34
(7.63,11.42)**
Rural
2.22
(1.52,3.25)**
3.02
(2.57,3.55)**
9.36
(6.18,14.19)**
Low Income
2.17
(1.67,2.82)**
3.13
(2.81,3.49)**
9.73
(7.32,12.93)**
Mid/High
Income
2.14
(1.63,2.8)**
3.11
(2.78,3.48)**
8.99
(6.70,12.06)**
Day Care
Children
2.56
(1.86,3.52)**
3.25
(2.85,3.72)**
10.83
(7.70,15.23)**
Home
Children
1.82
(1.45,2.28)**
2.99
(2.72,3.30)**
8.08
(6.28,10.39)**
Benzo[e]pyrene
Potential Exposure via
Inhalation
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation
Potential Absorbed
Dose via Indirect
Ingestion
0.72
(0.69,0.76)**
2.13
(1.72,2.64)**
3.18
(2.90,3.48)**
9.25
(7.32,11.68)**
0.72
(0.69,0.76)**
2.11
(1.75,2.54)**
3.29
(3.04,3.55)**
9.41
(7.70,11.50)**
0.72
(0.66,0.79)**
2.15
(1.47,3.15)**
3.07
(2.61,3.60)**
9.09
(5.99,13.78)**
0.70
(0.66,0.74)**
2.18
(1.68,2.82)**
3.17
(2.84,3.53)**
9.75
(7.34,12.96)**
0.75 (0.7,0.8)**
2.09
(1.60,2.73)**
3.18
(2.84,3.56)**
8.77
(6.53,11.77)**
0.78
(0.72,0.85)**
2.52
(1.84,3.45)**
3.38
(2.97,3.85)**
10.68
(7.61,14.98)**
0.67
(0.64,0.70)**
1.80
(1.43,2.27)**
2.98
(2.71,3.29)**
8.01
(6.22,10.32)**
Benzylbutylphthalate
Potential Exposure via
Inhalation a
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation a
Potential Absorbed
Dose via Indirect
Ingestion
--
2.39**
(1.92,2.96)
--
10.50**
(8.37,13.17)
--
2.22**
(1.88,2.62)
--
9 99**
(8.40,11.88)
--
2.57**
(1.72,3.82)
--
11.04**
(7.27,16.76)
--
2.60**
(1.99,3.41)
--
11.89**
(8.95,15.79)
--
2.19**
(1.68,2.85)
--
9.27**
(7.04,12.22)
--
2.91**
(2.16,3.93)
--
12.51**
(9.14,17.10)
--
1.95**
(1.55,2.47)
--
8.82**
(6.89,11.28)
Bisphenol-A
Potential Exposure via
Inhalation
Potential Exposure via
Indirect Ingestion b
Potential Absorbed
Dose via Inhalation
Potential Absorbed
Dose via Indirect
Ingestion b
0.68**
(0.63,0.74)
1.87**
(1.56,2.25)
3.00**
(2.67,3.36)
8.30**
(6.72,10.25)
0.69**
(0.64,0.74)
1.69**
(1.44,1.98)
3.14**
(2.84,3.46)
7.59**
(6.31,9.13)
0.67**
(0.59,0.78)
2.07**
(1.50,2.87)
2.86**
(2.34,3.51)
9.07**
(6.20,13.27)
0.67**
(0.61,0.74)
1.86**
(1.48,2.35)
3.01**
(2.62,3.45)
8.58**
(6.54,11.25)
0.69**
(0.63,0.77)
1.88**
(1.50,2.35)
2.98**
(2.59,3.44)
8.02**
(6.16,10.45)
0.69**
(0.61,0.78)
1.84**
(1.41,2.41)
2.99**
(2.52,3.55)
7.98**
(5.91,10.77)
0.67**
(0.62,0.73)
1.90**
(1.56,2.31)
3.00**
(2.66,3.38)
8.63**
(6.80,10.96)
alph «-Chlordane
Potential Exposure via
Inhalation
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation
0.79
(0.7,0.89)**
3.21
(2.37,4.34)**
3.48
(3.02,4.02)**
0.72
(0.65,0.8)**
2.36
(1.82,3.06)**
3.28
(2.9,3.72)**
0.86(0.70,1.05)
4.36
(2.56,7.43)**
3.70
(2.88,4.75)**
0.76
(0.66,0.87)**
3.09
(2.15,4.44)**
3.47
(2.93,4.12)**
0.82
(0.71,0.94)**
3.33
(2.29,4.84)**
3.49
(2.93,4.16)**
0.88(0.73,1.06)
4.74
(3.02,7.45)**
3.83
(3.09,4.76)**
0.7
(0.63,0.79)**
2.17
(1.58,2.96)**
3.16
(2.73,3.66)**
                                      R-41

-------
Table R-9.   Estimated Mean Ratio Between NC Children and Adults in the Same
            Household of Potential Exposure and Potential Absorbed Dose Estimates,
            Calculated Overall and by Stratum, and 95% Confidence Intervals on This
            Mean Ratio (cont.)
Exposure/Dose/
Biomarker
Parameter and
Pathway
Potential Absorbed
Dose via Indirect
Ingestion
Estimated Mean Ratio (95% CI)
in Preschool Children vs. Adults in the Same Household
Overall
14.02
(10.17,19.4)**
Urban
10.52
(7.98,13.87)**
Rural
18.7
(10.62,32.9)**
Low Income
13.78
(9.36,20.28)**
Mid/High
Income
14.28
(9.59,21.24)**
Day Care
Children
20.26
(12.57,32.7)**
Home
Children
9.71
(6.95,13.55)**
gflmma-Chlordane
Potential Exposure via
Inhalation
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation
Potential Absorbed
Dose via Indirect
Ingestion
0.81
(0.71,0.93)**
3.3
(2.44,4.46)**
3.59
(3.06,4.22)**
14.49
(10.54,19.9)**
0.74
(0.65,0.83)**
2.39
(1.84,3.09)**
3.33
(2.89,3.83)**
10.73
(8.16,14.10)**
0.90(0.71,1.14)
4.57
(2.68,7.79)**
3.88
(2.94,5.12)**
19.56
(11.14,34.3)**
0.78
(0.67,0.92)**
3.23
(2.24,4.66)**
3.57
(2.95,4.31)**
14.6
(9.92,21.49)**
0.85
(0.72,1.00)*
3.38
(2.32,4.92)**
3.62
(2.98,4.4)**
14.38
(9.67,21.37)**
0.93(0.75,1.15)
4.91
(3.15,7.65)**
4.05
(3.17,5.17)**
20.89
(13.11,33.3)**
0.71
(0.62,0.81)**
2.22
(1.62,3.06)**
3.19
(2.71,3.75)**
10.05
(7.17,14.08)**
Chlorpyrifos
Potential Exposure via
Inhalation
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation
Potential Absorbed
Dose via Indirect
Ingestion
0.70
(0.65,0.76)**
2.01
(1.62,2.50)**
3.12
(2.79,3.48)**
8.82
(6.95,11.19)**
0.66
(0.61,0.70)**
1.93
(1.60,2.31)**
2.97
(2.70,3.27)**
8.69
(7.12,10.6)**
0.76
(0.66,0.87)**
2.10
(1.42,3.10)**
3.27
(2.68,3.98)**
8.95
(5.82,13.78)**
0.68
(0.62,0.74)**
2.19
(1.68,2.86)**
3.11
(2.72,3.56)**
9.89
(7.37,13.28)**
0.73
(0.66,0.80)**
1.85
(1.40,2.42)**
3.12
(2.71,3.58)**
7.86
(5.82,10.61)**
0.71
(0.64,0.80)**
2.14
(1.57,2.92)**
3.09
(2.64,3.63)**
9.22
(6.59,12.9)**
0.70
(0.64,0.75)**
1.89
(1.49,2.40)**
3.14
(2.78,3.54)**
8.44
(6.46,11.03)**
Chrysene
Potential Exposure via
Inhalation
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation
Potential Absorbed
Dose via Indirect
Ingestion
0.72
(0.67,0.78)**
2.12
(1.70,2.66)**
3.14
(2.82,3.51)**
9.2
(7.23,11.71)**
0.73
(0.68,0.78)**
2.10
(1.73,2.55)**
3.31
(3.01,3.63)**
9.37
(7.61,11.53)**
0.72
(0.63,0.81)**
2.15
(1.45,3.18)**
2.99
(2.46,3.63)**
9.04
(5.89,13.87)**
0.68
(0.63,0.74)**
2.08
(1.59,2.72)**
3.06
(2.68,3.49)**
9.31
(6.94,12.47)**
0.77
(0.7,0.83)**
2.17
(1.64,2.87)**
3.23
(2.82,3.7)**
9.10
(6.72,12.32)**
0.79
(0.7,0.89)**
2.54
(1.83,3.52)**
3.37
(2.86,3.96)**
10.71
(7.53,15.23)**
0.66
(0.62,0.71)**
1.78
(1.41,2.25)**
2.93
(2.61,3.29)**
7.90
(6.10,10.24)**
Cyfluthrin
Potential Exposure via
Inhalation a
Potential Exposure via
Indirect Ingestion °
Potential Absorbed
Dose via Inhalation a
Potential Absorbed
Dose via Indirect
Ingestion °
--
2.10
(1.60,2.77)**
--
9.25
(6.91,12.38)**
--
2.16
(1.70,2.74)**
--
9.70
(7.52,12.5)**
--
2.05
(1.27,3.29)**
--
8.82
(5.33,14.62)**
--
2.49
(1.80,3.45)**
--
10.96
(7.77,15.47)**
--
1.78
(1.27,2.49)**
--
7.80
(5.44,11.19)**
--
2.37
(1.57,3.59)**
--
10.3
(6.60,16.06)**
--
1.87
(1.41,2.46)**
--
8.31
(6.19,11.15)**
                                      R-42

-------
Table R-9.   Estimated Mean Ratio Between NC Children and Adults in the Same
            Household of Potential Exposure and Potential Absorbed Dose Estimates,
            Calculated Overall and by Stratum, and 95% Confidence Intervals on This
            Mean Ratio (cont.)
Exposure/Dose/
Biomarker
Parameter and
Pathway
Estimated Mean Ratio (95% CI)
in Preschool Children vs. Adults in the Same Household
Overall
Urban
Rural
Low Income
Mid/High
Income
Day Care
Children
Home
Children
Diazinon
Potential Exposure via
Inhalation
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation
Potential Absorbed
Dose via Indirect
Ingestion
0.77
(0.66,0.9)**
2.75
(1.99,3.81)**
3.38
(2.83,4.04)**
12.08
(8.61,16.97)**
0.79
(0.69,0.91)**
2.61
(1.97,3.47)**
3.59
(3.07,4.20)**
11.81
(8.78,15.87)**
0.75
(0.58,0.98)*
2.90
(1.66,5.07)**
3.18
(2.35,4.31)**
12.37
(6.90,22.17)**
0.80
(0.67,0.96)*
3.02
(2.06,4.42)**
3.62
(2.95,4.45)**
13.50
(9.06,20.1)**
0.74
(0.62,0.89)**
2.51
(1.69,3.74)**
3.15
(2.56,3.90)**
10.82
(7.14,16.4)**
0.88(0.69,1.13)
4.01
(2.43,6.62)**
3.81
(2.89,5.02)**
17.33
(10.29,29.2)**
0.67
(0.58,0.78)**
1.89
(1.37,2.61)**
3.00
(2.53,3.57)**
8.42
(6.01,11.8)**
Dibenzo [a, It] anthracene
Potential Exposure via
Inhalation a
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation a
Potential Absorbed
Dose via Indirect
Ingestion
--
2.15
(1.73,2.66)**
--
9.32
(7.36,11.79)**
--
2.16
(1.79,2.6)**
--
9.62
(7.86,11.77)**
--
2.14
(1.46,3.13)**
--
9.03
(5.93,13.73)**
--
2.22
(1.71,2.89)**
--
9.95
(7.47,13.25)**
--
2.07
(1.58,2.72)**
--
8.73
(6.49,11.74)**
--
2.59
(1.89,3.55)**
--
10.98
(7.81,15.43)**
--
1.78
(1.41,2.24)**
--
7.91
(6.13,10.20)**
Di-n-butylphthalate
Potential Exposure via
Inhalation
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation
Potential Absorbed
Dose via Indirect
Ingestion
0.76**
(0.70,0.82)
2.32**
(1.90,2.85)
3.32**
(2.98,3.70)
10.17**
(8.19,12.64)
0.77**
(0.72,0.82)
2.20**
(1.85,2.62)
3.49**
(3.17,3.83)
9.91**
(8.24,11.92)
0.76**
(0.66,0.86)
2.45**
(1.70,3.54)
3.16**
(2.62,3.83)
10.45**
(7.04,15.49)
0.73**
(0.67,0.79)
2.51**
(1.95,3.23)
3.27**
(2.88,3.72)
11.51**
(8.77,15.09)
0.79**
(0.73,0.87)
2.15**
(1.66,2.78)
3.37**
(2.95,3.85)
9.00**
(6.81,11.88)
0.88*
(0.78,0.99)
2.78**
(2.09,3.70)
3.76**
(3.20,4.43)
11.84**
(8.77,15.98)
0.66**
(0.61,0.71)
1.94**
(1.54,2.44)
2.93**
(2.62,3.28)
8.74**
(6.80,11.24)
/>,/>'-DDE
Potential Exposure via
Inhalation a
Potential Exposure via
Indirect Ingestion a
Potential Absorbed
Dose via Inhalation a
Potential Absorbed
Dose via Indirect
Ingestion a
--
--
--

--
--
--

--
--
--

--
--
--

--
--
--

--
--
--

--
--
--

2,4-D (2,4-dichlorophenoxyacetic acid)
Potential Exposure via
Inhalation °
0.87
(0.75,1.00)*
0.90(0.80,1.02)
0.83(0.65,1.07)
0.86(0.72,1.02)
0.88(0.73,1.05)
1.14(0.93,1.40)
0.66
(0.56,0.77)**
                                      R-43

-------
Table R-9.   Estimated Mean Ratio Between NC Children and Adults in the Same
            Household of Potential Exposure and Potential Absorbed Dose Estimates,
            Calculated Overall and by Stratum, and 95% Confidence Intervals on This
            Mean Ratio (cont.)
Exposure/Dose/
Biomarker
Parameter and
Pathway
Potential Exposure via
Dietary Ingestion
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation °
Potential Absorbed
Dose via Dietary
Ingestion
Potential Absorbed
Dose via Indirect
Ingestion
Aggregated Potential
Exposure
Aggregated Potential
Absorbed Dose
Estimated Mean Ratio (95% CI)
in Preschool Children vs. Adults in the Same Household
Overall
1.03(0.69,1.53)
2.12
(1.71,2.63)**
3.82
(3.25,4.48)**
4.49
(3.00,6.72)**
9.32
(7.30,11.90)**
1.09(0.77,1.53)
4.71
(3.34,6.65)**
Urban
1.11 (0.81,1.51)
2.19
(1.83,2.63)**
4.09
(3.57,4.7)**
4.95
(3.61,6.77)**
9.88
(8.04,12.14)**
1.05(0.79,1.38)
4.60
(3.49,6.07)**
Rural
0.95(0.46,1.99)
2.05
(1.38,3.03)**
3.56
(2.68,4.74)**
4.08
(1.94,8.6)**
8.8
(5.65,13.71)**
1.14(0.60,2.14)
4.82
(2.55,9.14)**
Low Income
1.26(0.79,2.00)
2.53
(1.94,3.3)**
3.87
(3.19,4.7)**
5.56
(3.47,8.91)**
11.35
(8.39,15.35)**
1.20(0.80,1.78)
5.21
(3.48,7.79)**
Mid/High
Income
0.84(0.50,1.41)
1.78
(1.35,2.34)**
3.77
(3.08,4.60)**
3.63
(2.15,6.13)**
7.66
(5.6,10.47)**
0.99(0.62,1.59)
4.26
(2.66,6.83)**
Day Care
Children
1.46(0.84,2.54)
2.39
(1.77,3.23)**
4.95
(3.92,6.25)**
6.30
(3.58,11.09)**
10.35
(7.35,14.58)**
1.50(0.93,2.41)
6.31
(3.9,10.2)**
Home
Children
0.73(0.47,1.12)
1.87
(1.47,2.39)**
2.95
(2.48,3.51)**
3.20
(2.07,4.96)**
8.40
(6.38,11.05)**
0.79(0.54,1.16)
3.52
(2.4,5.16)**
Heptachlor
Potential Exposure via
Inhalation
Potential Exposure via
Indirect Ingestion a
Potential Absorbed
Dose via Inhalation
Potential Absorbed
Dose via Indirect
Ingestion a
0.85
(0.74,0.98)*
--
3.79
(3.22,4.46)**
"
0.75
(0.67,0.85)**
--
3.39
(2.94,3.91)**
"
0.97(0.77,1.22)
--
4.22
(3.18,5.61)**
"
0.81
(0.69,0.95)*
--
3.72
(3.07,4.51)**
"
0.90(0.76,1.05)
--
3.85
(3.16,4.7)**
"
1.01 (0.82,1.25)
--
4.41
(3.44,5.65)**
"
0.72
(0.63,0.82)**
--
3.25
(2.75,3.84)**
"
Indeno[l,2,3-crf]pyrene
Potential Exposure via
Inhalation
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation
Potential Absorbed
Dose via Indirect
Ingestion
0.69
(0.66,0.73)**
2.18
(1.75,2.71)**
3.04
(2.78,3.33)**
9.46
(7.47,11.97)**
0.69
(0.66,0.72)**
2.14
(1.77,2.58)**
3.14
(2.91,3.39)**
9.55
(7.80,11.70)**
0.69
(0.63,0.76)**
2.22
(1.51,3.27)**
2.95
(2.51,3.46)**
9.37
(6.16,14.26)**
0.68
(0.64,0.72)**
2.21
(1.70,2.88)**
3.1
(2.78,3.45)**
9.91
(7.43,13.2)**
0.70
(0.66,0.75)**
2.15
(1.64,2.83)**
2.99
(2.68,3.35)**
9.03
(6.71,12.16)**
0.71
(0.66,0.77)**
2.63
(1.91,3.62)**
3.09
(2.71,3.52)**
11.13
(7.91,15.67)**
0.67
(0.64,0.71)**
1.81
(1.43,2.28)**
3.00
(2.72,3.31)**
8.04
(6.23,10.38)**
Pentachlorophenol
Potential Exposure via
Inhalation
Potential Exposure via
Dietary Ingestion a
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation
0.83
(0.74,0.93)**
--
2.13
(1.69,2.69)**
3.66
(3.17,4.22)**
0.73
(0.66,0.81)**
--
2.04
(1.67,2.49)**
3.3
(2.91,3.74)**
0.94(0.77,1.16)
--
2.23
(1.46,3.39)**
4.05
(3.16,5.2)**
0.77
(0.67,0.88)**
--
2.37
(1.77,3.17)**
3.45
(2.92,4.09)**
0.90(0.78,1.04)
--
1.92
(1.43,2.58)**
3.87
(3.25,4.61)**
0.95(0.79,1.15)
--
2.36
(1.71,3.25)**
4.14
(3.33,5.16)**
0.72
(0.64,0.81)**
--
1.93
(1.48,2.51)**
3.22
(2.79,3.73)**
                                      R-44

-------
Table R-9.   Estimated Mean Ratio Between NC Children and Adults in the Same
            Household of Potential Exposure and Potential Absorbed Dose Estimates,
            Calculated Overall and by Stratum, and 95% Confidence Intervals on This
            Mean Ratio (cont.)
Exposure/Dose/
Biomarker
Parameter and
Pathway
Potential Absorbed
Dose via Dietary
Ingestion "
Potential Absorbed
Dose via Indirect
Ingestion
Estimated Mean Ratio (95% CI)
in Preschool Children vs. Adults in the Same Household
Overall
—
9.38
(7.35,11.97)**
Urban
—
9.21
(7.48,11.34)**
Rural
—
9.55
(6.13,14.87)**
Low Income
—
10.77
(7.93,14.62)**
Mid/High
Income
—
8.17
(5.99,11.16)**
Day Care
Children
—
10.17
(7.26,14.25)**
Home
Children
—
8.65
(6.53,11.46)**
c/s-Permethrin
Potential Exposure via
Inhalation
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation
Potential Absorbed
Dose via Indirect
Ingestion
0.72
(0.65,0.80)**
2.20
(1.73,2.80)**
3.20
(2.79,3.67)**
9.58
(7.36,12.47)**
0.66
(0.61,0.72)**
2.02
(1.64,2.48)**
3.00
(2.67,3.37)**
9.01
(7.2,11.27)**
0.79
(0.66,0.95)*
2.39
(1.56,3.67)**
3.41
(2.68,4.35)**
10.19
(6.35,16.34)**
0.72
(0.63,0.82)**
2.28
(1.7,3.06)**
3.26
(2.76,3.84)**
10.21
(7.39,14.11)**
0.73
(0.64,0.83)**
2.11
(1.56,2.86)**
3.14
(2.65,3.72)**
8.99
(6.45,12.53)**
0.73
(0.63,0.86)**
2.51
(1.77,3.56)**
3.19
(2.61,3.89)**
10.68
(7.32,15.58)**
0.72
(0.64,0.80)**
1.92
(1.48,2.49)**
3.21
(2.77,3.71)**
8.60
(6.44,11.47)**
Zra«s-Permethrin
Potential Exposure via
Inhalation
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation
Potential Absorbed
Dose via Indirect
Ingestion
0.76
(0.69,0.84)**
2.33
(1.78,3.05)**
3.35
(2.93,3.82)**
10.15
(7.61,13.53)**
0.69
(0.63,0.75)**
2.16
(1.72,2.72)**
3.11
(2.77,3.48)**
9.63
(7.54,12.31)**
0.84(0.70,1.00)
2.52
(1.56,4.06)**
3.61
(2.85,4.57)**
10.69
(6.39,17.87)**
0.73
(0.65,0.83)**
2.29
(1.65,3.18)**
3.31
(2.81,3.88)**
10.24
(7.21,14.55)**
0.79
(0.69,0.89)**
2.37
(1.70,3.32)**
3.39
(2.87,4.00)**
10.05
(7.00,14.43)**
0.81
(0.70,0.94)**
2.90
(1.96,4.29)**
3.51
(2.90,4.25)**
12.26
(8.09,18.60)**
0.71
(0.64,0.79)**
1.88
(1.41,2.50)**
3.20
(2.77,3.69)**
8.39
(6.15,11.45)**
PCB52
Potential Exposure via
Inhalation
Potential Exposure via
Indirect Ingestion a
Potential Absorbed
Dose via Inhalation
Potential Absorbed
Dose via Indirect
Ingestion *
0.72
(0.65,0.79)**
--
3.16
(2.78,3.58)**
"
0.72
(0.66,0.79)**
--
3.27
(2.94,3.65)**
"
0.72
(0.6,0.85)**
--
3.04
(2.43,3.80)**
"
0.70
(0.62,0.79)**
--
3.17
(2.72,3.68)**
"
0.74
(0.65,0.83)**
--
3.14
(2.69,3.68)**
"
0.77
(0.67,0.90)**
--
3.34
(2.79,4.02)**
"
0.67
(0.6,0.74)**
--
2.98
(2.6,3.41)**
"
PCB95
Potential Exposure via
Inhalation
Potential Exposure via
Indirect Ingestion a
Potential Absorbed
Dose via Inhalation
0.71
(0.66,0.77)**
--
3.13
(2.81,3.49)**
0.72
(0.67,0.77)**
--
3.27
(2.98,3.59)**
0.71
(0.61,0.81)**
--
3.00
(2.47,3.64)**
0.71
(0.64,0.78)**
--
3.19
(2.80,3.63)**
0.72
(0.65,0.79)**
--
3.08
(2.69,3.52)**
0.76
(0.67,0.86)**
--
3.28
(2.80,3.85)**
0.67
(0.62,0.73)**
--
2.99
(2.66,3.35)**
                                      R-45

-------
Table R-9.    Estimated Mean Ratio Between NC Children and Adults in the Same
                Household of Potential Exposure and Potential Absorbed Dose Estimates,
                Calculated Overall and by Stratum, and 95% Confidence Intervals on This
                Mean Ratio (cont.)
Exposure/Dose/
Biomarker
Parameter and
Pathway
Potential Absorbed
Dose via Indirect
Ingestion "
Estimated Mean Ratio (95% CI)
in Preschool Children vs. Adults in the Same Household
Overall
—
Urban
—
Rural
—
Low Income
—
Mid/High
Income
—
Day Care
Children
—
Home
Children
—
PCB 101
Potential Exposure via
Inhalation
Potential Exposure via
Indirect Ingestion a
Potential Absorbed
Dose via Inhalation
Potential Absorbed
Dose via Indirect
Ingestion a
0.75
(0.68,0.83)**
--
3.30
(2.92,3.74)**
"
0.76
(0.7,0.83)**
--
3.45
(3.1,3.85)**
"
0.74
(0.63,0.88)**
--
3.16
(2.54,3.92)**
"
0.75
(0.67,0.84)**
--
3.37
(2.91,3.91)**
"
0.75
(0.67,0.85)**
--
3.24
(2.78,3.77)**
"
0.85
(0.73,0.99)*
--
3.67
(3.04,4.44)**
"
0.67
(0.61,0.73)**
--
2.97
(2.62,3.37)**
"
3,5,6-TCP(3,5,6-trichloro-2-pyridinol)
Potential Exposure via
Inhalation
Potential Exposure via
Dietary Ingestion
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation
Potential Absorbed
Dose via Dietary
Ingestion
Potential Absorbed
Dose via Indirect
Ingestion
Aggregated Potential
Exposure
Aggregated Potential
Absorbed Dose
0.66
(0.61,0.71)**
1.16(0.81,1.66)
1.83
(1.51,2.2)**
2.92
(2.61,3.26)**
5.12
(3.48,7.52)**
7.99
(6.46,9.88)**
1.13(0.79,1.61)
4.93
(3.34,7.25)**
0.65
(0.6,0.69)**
1.17(0.87,1.58)
1.71
(1.46,2.01)**
2.94
(2.67,3.23)**
5.30
(3.82,7.36)**
7.65
(6.39,9.15)**
1.10(0.80,1.52)
4.96
(3.51,7.03)**
0.68
(0.59,0.77)**
1.15(0.61,2.18)
1.95
(1.38,2.74)**
2.90
(2.38,3.52)**
4.94
(2.52,9.66)**
8.34
(5.66,12.3)**
1.16(0.62,2.14)
4.89
(2.54,9.39)**
0.64
(0.58,0.70)**
1.18(0.78,1.80)
1.94
(1.53,2.45)**
2.91
(2.55,3.33)**
5.27
(3.37,8.24)**
8.70
(6.67,11.34)**
1.10(0.71,1.69)
4.88
(3.07,7.74)**
0.69
(0.63,0.75)**
1.14(0.74,1.78)
1.72
(1.35,2.19)**
2.92
(2.55,3.35)**
4.97
(3.12,7.92)**
7.34
(5.59,9.63)**
1.16(0.75,1.81)
4.97
(3.11,7.94)**
0.65
(0.58,0.73)**
1.79
(1.05,3.04)*
1.74
(1.34,2.28)**
2.81 (2.4,3.3)**
7.77
(4.35,13.9)**
7.44
(5.52,10.03)**
1.65 (0.95,2.86)
7.03
(3.82,12.90)**
0.68
(0.63,0.73)**
0.76(0.52,1.10)
1.91
(1.55,2.36)**
3.03
(2.69,3.41)**
3.37
(2.28,4.97)**
8.57
(6.73,10.92)**
0.77(0.54,1.10)
3.45
(2.38,5.00)**
a Results are not presented because, for each environmental sample type whose measurements were used to calculate the
potential exposure/absorbed dose, less than 45% of the measurements were detected.
b For each environmental sample type whose measurements were used to calculate the potential exposure/absorbed dose, less
than 45% of the measurements were detected.  However, results are presented because this was one of the eight pollutants
mentioned at the end of Section 9.2.
c The largest detection percentage among the environmental sample types whose measurements were used to calculate the
potential exposure/absorbed dose was between 45 and 50%.

* Statistically significantly different from 1 at the 0.05  level, but not at the 0.01 level.
** Statistically  significantly different from  1 at the 0.01 level.
                                                 R-46

-------
Table R-10.  Estimated Mean Ratio Between NC Children and Adults in the Same
              Household of Urinary Biomarker Concentrations, Calculated Overall and by
              Stratum, and 95% Confidence Intervals on This Mean Ratio
Exposure/Dose/
Biomarker
Parameter and
Pathway
Estimated Mean Ratio (95% CI)
in Preschool Children vs. Adults in the Same Household
Overall
Urban
Rural
Low Income
Mid/High
Income
Day Care
Children
Home
Children
2,4-D (2,4-dichlorophenoxyacetic acid)
Urinary concentration
(ng/mL)
Urinary concentration,
adjusted for specific
gravity (ng/mL)
Urinary concentration,
adjusted for creatinine
(umoles/mole)
0.91
(0.70,1.18)
0.91
(0.70,1.18)
1.79**
(1.32,2.43)
0.99(0.81,1.22)
1.00(0.81,1.23)
1.95**
(1.53,2.49)
0.83(0.52,1.33)
0.83(0.52,1.34)
1.64(0.93,2.89)
1.05(0.76,1.44)
1.05(0.77,1.45)
2.19**
(1.49,3.21)
0.78(0.56,1.09)
0.79(0.56,1.10)
1.46(1.00,2.15)
1.07(0.77,1.48)
1.07(0.77,1.49)
2.24**
(1.51,3.33)
0.77(0.56,1.06)
0.77(0.56,1.07)
1.43 (0.99,2.07)
Pentachlorophenol
Urinary concentration
(ng/mL)
Urinary concentration,
adjusted for specific
gravity (ng/mL)
Urinary concentration,
adjusted for creatinine
(umoles/mole)
1.36**
(1.15,1.60)
1.37**
(1.16,1.61)
2.87**
(2.40,3.43)
1.33**
(1.16,1.51)
1.33**
(1.16,1.52)
2.67**
(2.32,3.08)
1.40*
(1.03,1.89)
1.40*
(1.04,1.90)
3.07**
(2.21,4.28)
1.53**
(1.25,1.87)
1.53**
(1.25,1.88)
3.40**
(2.72,4.25)
1.21 (0.98,1.50)
1.21(0.98,1.50)
2.42**
(1.93,3.03)
1.38**
(1.12,1.70)
1.38**
(1.12,1.71)
3.03**
(2.41,3.80)
1.34**
(1.09,1.65)
1.35**
(1.10,1.65)
2.71**
(2.17,3.39)
3,5,6-TCP(3,5,6-trichloro-2-pyridinol)
Urinary concentration
(ng/mL)
Urinary concentration,
adjusted for specific
gravity (ng/mL)
Urinary concentration,
adjusted for creatinine
(umoles/mole)
1.29*
(1.02,1.63)
1.30*
(1.03,1.64)
2.57**
(2.03,3.24)
1.20(0.99,1.45)
1.20(0.99,1.46)
2.40**
(1.98,2.92)
1.39(0.90,2.14)
1.40(0.91,2.15)
2.74**
(1.80,4.18)
1.36*
(1.02,1.82)
1.37*
(1.03,1.82)
2.78**
(2.09,3.69)
1.22(0.91,1.65)
1.23(0.91,1.65)
2.37**
(1.78,3.16)
1.36(0.98,1.91)
1.37(0.98,1.91)
2.86**
(2.04,4.01)
1.22(0.94,1.59)
1.23(0.94,1.59)
2.30**
(1.79,2.97)
* Statistically significantly different from 1 at the 0.05 level, but not at the 0.01 level.
** Statistically significantly different from 1 at the 0.01 level.
                                            R-47

-------
Table R-ll.  Estimated Mean Ratio Between OH Children and Adults in the Same
            Household of Potential Exposure and Potential Absorbed Dose Estimates,
            Calculated Overall and by Stratum, and 95% Confidence Intervals on This
            Mean Ratio
Exposure/Dose/
Biomarker
Parameter and
Pathway
Estimated Mean Ratio (95% CI)
in Preschool Children vs. Adults in the Same Household
Overall
Urban
Rural
Low Income
Mid/High
Income
Day Care
Children
Home
Children
Benz [«] anthracene
Potential Exposure via
Inhalation
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation
Potential Absorbed
Dose via Indirect
Ingestion
-
1.92**
(1.48,2.49)
-
8.23**
(6.12,11.08)
--
1.72**
(1.43,2.07)
--
7.17**
(5.81,8.85)
--
2.14**
(1.33,3.43)
--
9.45**
(5.49,16.26)
--
1.55*
(1.08,2.22)
--
6.80**
(4.52,10.25)
--
2.37**
(1.81,3.12)
--
9.97**
(7.30,13.60)
--
2.92**
(2.10,4.05)
--
12.33**
(8.52,17.85)
--
1.26
(0.93,1.71)
--
5.50**
(3.87,7.81)
Benzo [b] fluoranthene
Potential Exposure via
Inhalation
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation
Potential Absorbed
Dose via Indirect
Ingestion
-
1.90**
(1.46,2.47)
-
8.16**
(6.06,10.99)
--
1.76**
(1.46,2.12)
--
7.35**
(5.96,9.08)
--
2.05**
(1.28,3.30)
--
9.06**
(5.27,15.59)
--
1.55*
(1.08,2.22)
--
6.80**
(4.51,10.23)
--
2.33**
(1.77,3.07)
--
9.80**
(7.18,13.38)
--
2.94**
(2.11,4.09)
--
12.43**
(8.58,18.01)
--
1.23
(0.91,1.67)
--
5.36**
(3.78,7.61)
Benzo [k] fluoranthene
Potential Exposure via
Inhalation (a'
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation
Potential Absorbed
Dose via Indirect
Ingestion
-
1.97**
(1.51,2.57)
--
8.44**
(6.24,11.41)
--
1.75**
(1.45,2.12)
--
7.32**
(5.90,9.07)
--
2.21**
(1.36,3.58)
--
9.73**
(5.61,16.88)
--
1.59*
(1.10,2.29)
--
6.95**
(4.59,10.54)
--
2.44**
(1.84,3.23)
--
10.24**
(7.46,14.04)
--
3.08**
(2.20,4.31)
--
12.99**
(8.91,18.95)
--
1.26
(0.92,1.71)
--
5.48**
(3.84,7.82)
Benzo [ghi] perylene
Potential Exposure via
Inhalation (a'
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation
Potential Absorbed
Dose via Indirect
Ingestion
-
1.94**
(1.49,2.52)
--
8.31**
(6.16,11.21)
--
1.78**
(1.48,2.15)
--
7.43**
(6.01,9.18)
--
2.11**
(1.30,3.40)
--
9.29**
(5.38,16.06)
--
1.59*
(1.11,2.28)
--
6.98**
(4.61,10.55)
--
2.36**
(1.79,3.10)
--
9.89**
(7.23,13.54)
--
3.01**
(2.17,4.19)
--
12.73**
(8.77,18.46)
--
1.24
(0.91,1.69)
--
5.42**
(3.81,7.73)
Benzo[fl]pyrene
Potential Exposure via
Inhalation
-
--
--
--
--
--
--
                                      R-48

-------
Table R-ll.  Estimated Mean Ratio Between OH Children and Adults in the Same
            Household of Potential Exposure and Potential Absorbed Dose Estimates,
            Calculated Overall and by Stratum, and 95% Confidence Intervals on This
            Mean Ratio  (cont.)
Exposure/Dose/
Biomarker
Parameter and
Pathway
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation
Potential Absorbed
Dose via Indirect
Ingestion
Estimated Mean Ratio (95% CI)
in Preschool Children vs. Adults in the Same Household
Overall
1.91**
(1.47,2.48)
-
8.20**
(6.08,11.05)
Urban
1.71**
(1.42,2.06)
--
7.15**
(5.78,8.83)
Rural
2.13**
(1.32,3.43)
--
9.40**
(5.44,16.22)
Low Income
1.56*
(1.09,2.24)
--
6.85**
(4.54,10.35)
Mid/High
Income
2.33**
(1.77,3.07)
--
9.80**
(7.17,13.40)
Day Care
Children
2.88**
(2.07,4.00)
--
12.15**
(8.37,17.63)
Home
Children
1.27
(0.93,1.72)
--
5.53**
(3.89,7.87)
Benzo[e]pyrene
Potential Exposure via
Inhalation
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation
Potential Absorbed
Dose via Indirect
Ingestion
-
1.91**
(1.47,2.47)
-
8.19**
(6.10,10.99)
--
1.75**
(1.46,2.10)
--
7.30**
(5.92,8.99)
--
2.08**
(1.30,3.32)
--
9.18**
(5.37,15.71)
--
1.57*
(1.10,2.23)
--
6.87**
(4.58,10.30)
--
2.32**
(1.77,3.04)
--
9.76**
(7.17,13.28)
--
2.92**
(2.11,4.04)
--
12.33**
(8.54,17.80)
--
1.25
(0.92,1.68)
--
5.43**
(3.84,7.69)
Benzylbutylphthalate
Potential Exposure via
Inhalation
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation
Potential Absorbed
Dose via Indirect
Ingestion
-
1.69**
(1.28,2.22)
-
7.21**
(5.31,9.79)
--
1.71**
(1.40,2.09)
--
7.14**
(5.72,8.92)
--
1.67*
(1.02,2.72)
--
7.27**
(4.19,12.63)
--
1.39
(0.97,2.01)
--
6.01**
(3.97,9.10)
--
2.05**
(1.54,2.73)
--
8.64**
(6.27,11.90)
--
2.51**
(1.75,3.61)
--
10.59**
(7.13,15.74)
--
1.13
(0.83,1.54)
--
4.90**
(3.46,6.95)
Bisphenol-A
Potential Exposure via
Inhalation
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation
Potential Absorbed
Dose via Indirect
Ingestion
0.72**
(0.67,0.78)
1.46**
(1.22,1.74)
3.04**
(2.71,3.42)
6.29**
(5.10,7.77)
0.71**
(0.67,0.75)
1.41**
(1.23,1.61)
3.01**
(2.76,3.28)
5.91**
(5.06,6.91)
0.73**
(0.64,0.84)
1.51*
(1.10,2.08)
3.08**
(2.49,3.81)
6.70**
(4.60,9.77)
0.72**
(0.65,0.80)
1.28
(1.00,1.65)
2.98**
(2.54,3.50)
5.71**
(4.23,7.72)
0.72**
(0.66,0.78)
1.66**
(1.38,2.00)
3.11**
(2.74,3.52)
6.93**
(5.60,8.59)
0.75**
(0.68,0.84)
1.71**
(1.36,2.14)
3.18**
(2.72,3.71)
7.31**
(5.64,9.46)
0.69**
(0.64,0.75)
1.25*
(1.02,1.53)
2.92**
(2.55,3.34)
5.42**
(4.22,6.96)
alph «-Chlordane
Potential Exposure via
Inhalation
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation
0.69**
(0.64,0.73)
1.46**
(1.22,1.75)
2.87**
(2.61,3.16)
0.69**
(0.66,0.72)
1.40**
(1.23,1.59)
2.86**
(2.68,3.06)
0.68**
(0.61,0.76)
1.53*
(1.09,2.13)
2.88**
(2.40,3.44)
0.71**
(0.66,0.77)
1.21
(0.94,1.56)
2.88**
(2.53,3.29)
0.66**
(0.62,0.70)
1.77**
(1.46,2.14)
2.86**
(2.58,3.16)
0.68**
(0.62,0.74)
1.76**
(1.41,2.19)
2.87**
(2.55,3.23)
0.69**
(0.65,0.74)
1.22
(0.98,1.52)
2.87**
(2.56,3.22)
                                      R-49

-------
Table R-ll.  Estimated Mean Ratio Between OH Children and Adults in the Same
            Household of Potential Exposure and Potential Absorbed Dose Estimates,
            Calculated Overall and by Stratum, and 95% Confidence Intervals on This
            Mean Ratio  (cont.)
Exposure/Dose/
Biomarker
Parameter and
Pathway
Potential Absorbed
Dose via Indirect
Ingestion
Estimated Mean Ratio (95% CI)
in Preschool Children vs. Adults in the Same Household
Overall
6.26**
(5.04,7.78)
Urban
5.85**
(5.03,6.81)
Rural
6.69**
(4.49,9.96)
Low Income
5.34**
(3.94,7.23)
Mid/High
Income
7.34**
(5.86,9.20)
Day Care
Children
7.36**
(5.67,9.56)
Home
Children
5.32**
(4.09,6.92)
gflmmfl-Chlordane
Potential Exposure via
Inhalation
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation
Potential Absorbed
Dose via Indirect
Ingestion
0.68**
(0.64,0.72)
1.49**
(1.23,1.79)
2.83**
(2.57,3.12)
6.37**
(5.11,7.93)
0.68**
(0.65,0.71)
1.42**
(1.25,1.62)
2.82**
(2.65,3.01)
5.95**
(5.11,6.94)
0.67**
(0.61,0.75)
1.55*
(1.10,2.19)
2.84**
(2.38,3.39)
6.81**
(4.55,10.19)
0.70**
(0.65,0.75)
1.24
(0.96,1.61)
2.85**
(2.50,3.25)
5.48**
(4.03,7.46)
0.65**
(0.61,0.69)
1.78**
(1.47,2.16)
2.82**
(2.55,3.11)
7.39**
(5.88,9.29)
0.66**
(0.61,0.72)
1.82**
(1.45,2.27)
2.79**
(2.49,3.14)
7.61**
(5.84,9.91)
0.69**
(0.65,0.74)
1.22
(0.97,1.53)
2.87**
(2.57,3.22)
5.33**
(4.08,6.96)
Chlorpyrifos
Potential Exposure via
Inhalation
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation
Potential Absorbed
Dose via Indirect
Ingestion
0.72**
(0.64,0.81)
1.79**
(1.39,2.29)
3.03**
(2.62,3.51)
7.66**
(5.82,10.06)
0.78**
(0.71,0.85)
1.81**
(1.51,2.17)
3.29**
(2.96,3.67)
7.52**
(6.20,9.14)
0.67**
(0.54,0.82)
1.77*
(1.13,2.77)
2.79**
(2.15,3.63)
7.79**
(4.74,12.81)
0.76**
(0.65,0.89)
1.59**
(1.14,2.23)
3.16**
(2.58,3.86)
6.93**
(4.76,10.08)
0.68**
(0.60,0.77)
2.01**
(1.55,2.61)
2.92**
(2.49,3.41)
8.46**
(6.35,11.26)
0.78**
(0.66,0.91)
2.64**
(1.91,3.64)
3.33**
(2.76,4.03)
11.10**
(7.87,15.66)
0.67**
(0.58,0.76)
1.21
(0.91,1.61)
2.76**
(2.32,3.28)
5.28**
(3.84,7.26)
Chrysene
Potential Exposure via
Inhalation
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation ™
Potential Absorbed
Dose via Indirect
Ingestion
0.72**
(0.67,0.76)
1.94**
(1.49,2.52)
2.90**
(2.58,3.25)
8.33**
(6.18,11.23)
0.73**
(0.70,0.76)
1.76**
(1.46,2.13)
3.04**
(2.81,3.28)
7.34**
(5.95,9.07)
0.70**
(0.63,0.78)
2.13**
(1.32,3.44)
2.76**
(2.23,3.41)
9.44**
(5.48,16.28)
0.70**
(0.65,0.76)
1.58*
(1.10,2.27)
2.74**
(2.32,3.23)
6.93**
(4.59,10.45)
0.73**
(0.69,0.78)
2.38**
(1.81,3.14)
3.06**
(2.72,3.44)
10.01**
(7.33,13.69)
0.77**
(0.71,0.83)
3.02**
(2.16,4.20)
3.12**
(2.73,3.58)
12.75**
(8.80,18.50)
0.67**
(0.63,0.72)
1.25
(0.92,1.70)
2.68**
(2.32,3.10)
5.44**
(3.82,7.73)
Cyfluthrin
Potential Exposure via
Inhalation
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation
Potential Absorbed
Dose via Indirect
Ingestion
--
1.99**
(1.54,2.57)
-
8.51**
(6.36,11.38)
--
1.69**
(1.41,2.03)
--
7.07**
(5.74,8.71)
--
2.34**
(1.47,3.72)
--
10.24**
(6.04,17.35)
--
1.76**
(1.24,2.50)
--
7.74**
(5.20,11.51)
--
2.25**
(1.72,2.94)
--
9.36**
(6.90,12.69)
--
2.92**
(2.11,4.04)
--
12.25**
(8.47,17.73)
--
1.35*
(1.01,1.82)
--
5.91**
(4.22,8.27)
                                      R-50

-------
Table R-ll.  Estimated Mean Ratio Between OH Children and Adults in the Same
            Household of Potential Exposure and Potential Absorbed Dose Estimates,
            Calculated Overall and by Stratum, and 95% Confidence Intervals on This
            Mean Ratio  (cont.)
Exposure/Dose/
Biomarker
Parameter and
Pathway
Estimated Mean Ratio (95% CI)
in Preschool Children vs. Adults in the Same Household
Overall
Urban
Rural
Low Income
Mid/High
Income
Day Care
Children
Home
Children
Diazinon
Potential Exposure via
Inhalation
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation
Potential Absorbed
Dose via Indirect
Ingestion
0.94
(0.77,1.15)
2.29**
(1.62,3.22)
3.95**
(3.16,4.93)
9.87**
(6.77,14.38)
0.83*
(0.71,0.97)
1.88**
(1.45,2.45)
3.37**
(2.85,3.99)
7.82**
(5.87,10.41)
1.07
(0.75,1.51)
2.78**
(1.52,5.07)
4.62**
(3.13,6.83)
12.46**
(6.42,24.17)
1.01
(0.81,1.27)
2.10**
(1.36,3.25)
4.01**
(3.08,5.22)
9.13**
(5.63,14.81)
0.87
(0.71,1.07)
2.49**
(1.74,3.55)
3.88**
(3.08,4.89)
10.66**
(7.20,15.79)
1.14
(0.85,1.51)
3.69**
(2.28,5.96)
4.80**
(3.50,6.59)
15.76**
(9.36,26.56)
0.78*
(0.64,0.95)
1.42
(0.99,2.04)
3.24**
(2.59,4.06)
6.18**
(4.14,9.22)
Dibenzo [a, It] anthracene
Potential Exposure via
Inhalation (a'
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation
Potential Absorbed
Dose via Indirect
Ingestion
-
1.96**
(1.51,2.55)
-
8.41**
(6.23,11.35)
--
1.78**
(1.47,2.14)
--
7.41**
(6.00,9.16)
--
2.16**
(1.34,3.49)
--
9.54**
(5.52,16.50)
--
1.61*
(1.12,2.31)
--
7.06**
(4.66,10.68)
--
2.39**
(1.82,3.15)
--
10.02**
(7.33,13.71)
--
3.04**
(2.19,4.22)
--
12.82**
(8.85,18.58)
--
1.27
(0.93,1.72)
--
5.52**
(3.87,7.87)
Di-n-butylphthalate
Potential Exposure via
Inhalation
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation
Potential Absorbed
Dose via Indirect
Ingestion
0.78**
(0.72,0.86)
1.75**
(1.43,2.15)
3.36**
(2.96,3.81)
7.54**
(5.94,9.57)
0.74**
(0.70,0.79)
1.72**
(1.48,1.99)
3.06**
(2.80,3.35)
7.11**
(5.98,8.45)
0.83*
(0.71,0.97)
1.79**
(1.24,2.57)
3.69**
(2.94,4.63)
7.99**
(5.18,12.33)
0.81**
(0.73,0.91)
1.44**
(1.10,1.89)
3.43**
(2.91,4.03)
6.39**
(4.61,8.85)
0.76**
(0.69,0.83)
2.13**
(1.72,2.64)
3.30**
(2.89,3.77)
8.89**
(6.90,11.45)
0.85*
(0.75,0.97)
2.62**
(2.01,3.41)
3.65**
(3.09,4.32)
10.99**
(8.08,14.96)
0.72**
(0.66,0.79)
1.18
(0.94,1.48)
3.09**
(2.70,3.55)
5.17**
(3.92,6.81)
/>,/>'-DDE
Potential Exposure via
Inhalation
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation
Potential Absorbed
Dose via Indirect
Ingestion
0.73**
(0.67,0.80)
1.71**
(1.38,2.12)
3.06**
(2.71,3.46)
7.48**
(5.94,9.41)
0.74**
(0.70,0.80)
1.45**
(1.25,1.69)
3.08**
(2.83,3.35)
6.05**
(5.16,7.10)
0.71**
(0.61,0.84)
2.01**
(1.37,2.97)
3.04**
(2.44,3.79)
9.23**
(6.06,14.05)
0.74**
(0.66,0.83)
1.44*
(1.07,1.92)
3.01**
(2.57,3.53)
6.41**
(4.65,8.83)
0.72**
(0.65,0.79)
2.04**
(1.63,2.55)
3.11**
(2.74,3.54)
8.72**
(6.87,11.06)
0.78**
(0.69,0.89)
2.14**
(1.64,2.81)
3.30**
(2.81,3.87)
9.26**
(7.03,12.20)
0.68**
(0.62,0.75)
1.37*
(1.07,1.75)
2.84**
(2.48,3.25)
6.03**
(4.57,7.97)
2,4-D (2,4-dichlorophenoxyacetic acid)
Potential Exposure via
Inhalation ^
0.87
(0.74,1.01)
0.87**
(0.79,0.96)
0.86
(0.65,1.14)
0.96
(0.80,1.14)
0.79**
(0.66,0.93)
1.04
(0.84,1.29)
0.72**
(0.62,0.84)
                                      R-51

-------
Table R-ll.  Estimated Mean Ratio Between OH Children and Adults in the Same
            Household of Potential Exposure and Potential Absorbed Dose Estimates,
            Calculated Overall and by Stratum, and 95% Confidence Intervals on This
            Mean Ratio  (cont.)
Exposure/Dose/
Biomarker
Parameter and
Pathway
Potential Exposure via
Dietary Ingestion
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation
Potential Absorbed
Dose via Dietary
T *• 0>)
Ingestion
Potential Absorbed
Dose via Indirect
Ingestion
Aggregated Potential
Exposure
Aggregated Potential
Absorbed Dose
Estimated Mean Ratio (95% CI)
in Preschool Children vs. Adults in the Same Household
Overall
0.99
(0.64,1.51)
1.76**
(1.36,2.29)
3.78**
(3.11,4.59)
4.20**
(2.69,6.56)
7.49**
(5.53,10.13)
1.07
(0.61,1.86)
4.56**
(2.54,8.19)
Urban
1.16
(0.85,1.57)
1.77**
(1.49,2.11)
3.67**
(3.26,4.14)
4.83**
(3.52,6.63)
7.42**
(6.04,9.12)
1.20
(0.85,1.70)
5.00**
(3.46,7.23)
Rural
0.84
(0.39,1.82)
1.76*
(1.09,2.83)
3.89**
(2.73,5.53)
3.65**
(1.63,8.17)
7.55**
(4.32,13.19)
0.95
(0.35,2.57)
4.15**
(1.45,11.86)
Low Income
1.06
(0.61,1.84)
1.77**
(1.24,2.52)
4.02**
(3.21,5.03)
4.48**
(2.52,7.96)
7.79**
(5.16,11.78)
1.08
(0.58,2.03)
4.51**
(2.32,8.76)
Mid/High
Income
0.92
(0.58,1.44)
1.76**
(1.35,2.30)
3.55**
(2.87,4.39)
3.93**
(2.45,6.30)
7.19**
(5.24,9.86)
1.06
(0.58,1.92)
4.60**
(2.45,8.64)
Day Care
Children
1.67
(0.94,2.97)
2.40**
(1.77,3.26)
4.62**
(3.54,6.04)
7.14**
(3.94,12.93)
9.96**
(6.90,14.38)
1.76
(0.81,3.82)
7.63**
(3.36,17.33)
Home
Children
0.58*
(0.36,0.92)
1.30
(0.95,1.77)
3.09**
(2.57,3.71)
2.47**
(1.51,4.02)
5.63**
(3.93,8.06)
0.65
(0.39,1.08)
2.72**
(1.59,4.67)
Indeno[l,2,3-crf]pyrene
Potential Exposure via
Inhalation (a'
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation
Potential Absorbed
Dose via Indirect
Ingestion
-
1.96**
(1.50,2.57)
-
8.42**
(6.19,11.45)
--
1.81**
(1.49,2.20)
--
7.55**
(6.07,9.38)
--
2.13**
(1.30,3.49)
--
9.38**
(5.35,16.45)
--
1.60*
(1.10,2.32)
--
7.00**
(4.58,10.70)
--
2.41**
(1.81,3.20)
--
10.11**
(7.33,13.95)

--
3.11**
(2.21,4.38)
--
13.15**
(8.97,19.27)
--
1.24
(0.90,1.70)
--
5.39**
(3.74,7.75)
Pentachlorophenol
Potential Exposure via
Inhalation
Potential Exposure via
Dietary Ingestion
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation
Potential Absorbed
Dose via Dietary
Ingestion
Potential Absorbed
Dose via Indirect
Ingestion
0.64**
(0.53,0.78)
-
1.45**
(1.20,1.76)
2.73**
(2.22,3.36)
~~
6.21**
(5.02,7.69)
0.64**
(0.56,0.74)
--
1.40**
(1.22,1.60)
2.72**
(2.36,3.14)

5.81**
(5.03,6.71)
0.64*
(0.45,0.91)
--
1.51*
(1.06,2.15)
2.74**
(1.88,3.98)

6.64**
(4.48,9.84)
0.66**
(0.52,0.83)
--
1.33*
(1.03,1.72)
2.78**
(2.15,3.59)

5.81**
(4.33,7.80)
0.62**
(0.51,0.77)
--
1.59**
(1.30,1.94)
2.68**
(2.14,3.36)

6.64**
(5.32,8.28)
0.59**
(0.45,0.78)
--
1.65**
(1.30,2.11)
2.57**
(1.94,3.41)

6.95**
(5.40,8.95)
0.69**
(0.57,0.84)
--
1.28*
(1.02,1.60)
2.90**
(2.34,3.59)

5.55**
(4.28,7.18)
c/s-Permethrin
Potential Exposure via
Inhalation
0.76**
(0.69,0.84)
0.76**
(0.70,0.82)
0.76**
(0.64,0.91)
0.77**
(0.68,0.87)
0.75**
(0.67,0.84)
0.82*
(0.71,0.95)
0.71**
(0.64,0.78)
                                      R-52

-------
Table R-ll.  Estimated Mean Ratio Between OH Children and Adults in the Same
            Household of Potential Exposure and Potential Absorbed Dose Estimates,
            Calculated Overall and by Stratum, and 95% Confidence Intervals on This
            Mean Ratio  (cont.)
Exposure/Dose/
Biomarker
Parameter and
Pathway
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation
Potential Absorbed
Dose via Indirect
Ingestion
Estimated Mean Ratio (95% CI)
in Preschool Children vs. Adults in the Same Household
Overall
1.78**
(1.46,2.17)
3.19**
(2.72,3.75)
7.61**
(6.13,9.45)
Urban
1.55**
(1.35,1.78)
3.14**
(2.79,3.53)
6.46**
(5.56,7.51)
Rural
2.04**
(1.42,2.94)
3.25**
(2.44,4.33)
8.96**
(6.03,13.30)
Low Income
1.54**
(1.17,2.03)
3.15**
(2.58,3.85)
6.79**
(5.02,9.18)
Mid/High
Income
2.05**
(1.66,2.53)
3.24**
(2.73,3.83)
8.53**
(6.82,10.68)
Day Care
Children
2.37**
(1.85,3.03)
3.46**
(2.77,4.32)
9.94**
(7.67,12.89)
Home
Children
1.33*
(1.05,1.69)
2.95**
(2.49,3.49)
5.82**
(4.48,7.57)
frflns-Pennethrin
Potential Exposure via
Inhalation
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation
Potential Absorbed
Dose via Indirect
Ingestion
0.76**
(0.68,0.86)
1.71**
(1.39,2.10)
3.20**
(2.71,3.79)
7.34**
(5.81,9.28)
0.76**
(0.70,0.83)
1.55**
(1.33,1.81)
3.13**
(2.77,3.55)
6.49**
(5.45,7.74)
0.77**
(0.63,0.94)
1.88**
(1.30,2.71)
3.27**
(2.43,4.41)
8.30**
(5.46,12.64)
0.78**
(0.69,0.89)
1.39*
(1.04,1.87)
3.17**
(2.58,3.90)
6.27**
(4.48,8.78)
0.75**
(0.67,0.84)
2.09**
(1.69,2.59)
3.24**
(2.72,3.86)
8.60**
(6.75,10.95)
0.82*
(0.70,0.97)
2.33**
(1.80,3.01)
3.47**
(2.75,4.38)
9.79**
(7.30,13.11)
0.71**
(0.63,0.79)
1.25
(0.98,1.60)
2.96**
(2.48,3.52)
5.51**
(4.16,7.30)
PCB52
Potential Exposure via
Inhalation
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation
Potential Absorbed
Dose via Indirect
Ingestion
0.72**
(0.68,0.77)
1.81**
(1.46,2.25)
3.01**
(2.71,3.34)
7.85**
(6.23,9.87)
0.73**
(0.70,0.76)
1.66**
(1.42,1.94)
3.00**
(2.79,3.23)
6.92**
(5.90,8.13)
0.72**
(0.65,0.80)
1.98**
(1.34,2.94)
3.01**
(2.49,3.64)
8.89**
(5.84,13.55)
0.75**
(0.70,0.80)
1.73**
(1.29,2.33)
3.01**
(2.62,3.46)
7.68**
(5.57,10.60)
0.70**
(0.66,0.74)
1.90**
(1.51,2.38)
3.01**
(2.70,3.35)
8.01**
(6.31,10.18)
0.75**
(0.69,0.82)
2.36**
(1.79,3.09)
3.13**
(2.74,3.59)
10.02**
(7.59,13.22)
0.70**
(0.66,0.74)
1.40**
(1.09,1.80)
2.88**
(2.57,3.24)
6.15**
(4.65,8.12)
PCB95
Potential Exposure via
Inhalation
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation
Potential Absorbed
Dose via Indirect
Ingestion (a)
0.74**
(0.68,0.81)
-
3.12**
(2.74,3.55)
"
0.74**
(0.70,0.79)
--
3.08**
(2.81,3.38)
"
0.74**
(0.63,0.87)
--
3.16**
(2.50,3.98)
"
0.75**
(0.67,0.84)
--
3.08**
(2.61,3.63)
"
0.73**
(0.66,0.80)
--
3.16**
(2.76,3.62)
"
0.79**
(0.70,0.90)
--
3.36**
(2.83,4.00)
"
0.69**
(0.63,0.76)
--
2.89**
(2.51,3.33)
"
PCB 101
Potential Exposure via
Inhalation
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation
0.74**
(0.66,0.83)
-
3.12**
(2.68,3.61)
0.75**
(0.69,0.82)
--
3.11**
(2.79,3.46)
0.73**
(0.60,0.88)
--
3.12**
(2.39,4.07)
0.74**
(0.64,0.84)
--
3.02**
(2.50,3.64)
0.74**
(0.66,0.84)
--
3.21**
(2.75,3.76)
0.81**
(0.69,0.94)
--
3.41**
(2.79,4.18)
0.68**
(0.60,0.76)
--
2.84**
(2.43,3.33)
                                      R-53

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Table R-ll.   Estimated Mean Ratio Between OH Children and Adults in the Same
                Household of Potential Exposure and Potential Absorbed Dose Estimates,
                Calculated Overall and by Stratum, and 95% Confidence Intervals on This
                Mean Ratio  (cont.)
Exposure/Dose/
Biomarker
Parameter and
Pathway
Potential Absorbed
Dose via Indirect
Ingestion (a)
Estimated Mean Ratio (95% CI)
in Preschool Children vs. Adults in the Same Household
Overall
~
Urban
—
Rural
—
Low Income
—
Mid/High
Income
—
Day Care
Children
—
Home
Children
—
3,5,6-TCP(3,5,6-trichloro-2-pyridinol)
Potential Exposure via
Inhalation
Potential Exposure via
Dietary Ingestion
Potential Exposure via
Indirect Ingestion
Potential Absorbed
Dose via Inhalation
Potential Absorbed
Dose via Dietary
Ingestion
Potential Absorbed
Dose via Indirect
Ingestion
Aggregated Potential
Exposure
Aggregated Potential
Absorbed Dose
0.74**
(0.66,0.82)
0.94
(0.64,1.39)
1.65**
(1.33,2.05)
3.17**
(2.73,3.68)
4.02**
(2.68,6.01)
7.04**
(5.62,8.81)
1.00
(0.65,1.55)
4.28**
(2.72,6.74)
0.75**
(0.70,0.81)
0.88
(0.68,1.14)
1.44**
(1.23,1.68)
3.11**
(2.83,3.43)
3.67**
(2.78,4.84)
5.98**
(5.12,7.00)
0.86
(0.66,1.14)
3.56**
(2.67,4.74)
0.72**
(0.60,0.88)
1.01
(0.50,2.06)
1.89**
(1.28,2.79)
3.23**
(2.46,4.24)
4.40**
(2.10,9.21)
8.27**
(5.48,12.49)
1.16
(0.51,2.64)
5.15**
(2.21,11.97)
0.76**
(0.67,0.87)
0.88
(0.53,1.47)
1.46*
(1.09,1.96)
3.37**
(2.81,4.04)
3.75**
(2.20,6.38)
6.43**
(4.70,8.80)
1.03
(0.59,1.79)
4.53**
(2.56,8.02)
0.72**
(0.64,0.81)
1.02
(0.68,1.53)
1.86**
(1.48,2.33)
2.99**
(2.54,3.51)
4.31**
(2.81,6.61)
7.70**
(6.10,9.72)
0.98
(0.60,1.58)
4.04**
(2.46,6.64)
0.80**
(0.69,0.93)
1.77*
(1.09,2.86)
2.04**
(1.55,2.69)
3.34**
(2.73,4.07)
7.49**
(4.46,12.56)
8.47**
(6.46,11.09)
1.94*
(1.11,3.42)
8.03**
(4.45,14.49)
0.69**
(0.62,0.76)
0.51**
(0.33,0.79)
1.33*
(1.04,1.71)
3.02**
(2.59,3.51)
2.16**
(1.37,3.40)
5.85**
(4.45,7.68)
0.52**
(0.32,0.82)
2.28**
(1.41,3.68)
(a) Results are not presented because, for each environmental sample type whose measurements were used to calculate the
potential exposure/absorbed dose, less than 45% of the measurements were detected.
(b) For each environmental sample type whose measurements were used to calculate the potential exposure/absorbed dose, less
than 45% of the measurements were detected. However, results are presented because this was one of the eight pollutants
mentioned at the end of Section 9.2.
(c) The largest detection percentage among the environmental sample types whose measurements were used to calculate the
potential exposure/absorbed dose was between 45 and 50%.

* Statistically significantly different from 1 at the 0.05 level, but not at the 0.01 level.
** Statistically  significantly different from 1 at the 0.01 level.
                                                 R-54

-------
Table R-12.   Estimated Mean Ratio Between OH Children and Adults in the Same
              Household of Urinary Biomarker Concentrations, Calculated Overall and by
              Stratum, and 95% Confidence Intervals on This Mean Ratio
Exposure/Dose/
Biomarker
Parameter and
Pathway
Estimated Mean Ratio (95% CI)
in Preschool Children vs. Adults in the Same Household
Overall
Urban
Rural
Low Income
Mid/High
Income
Day Care
Children
Home
Children
2,4-D (2,4-dichlorophenoxyacetic acid)
Urinary concentration
(ng/mL)
Urinary concentration,
adjusted for specific
gravity (ng/mL)
Urinary concentration,
adjusted for creatinine
(umoles/mole)
1.42*
(1.04,1.94)
1.43*
(1.05,1.94)
2.73**
(2.00,3.71)
1.34**
(1.09,1.65)
1.35**
(1.10,1.66)
2.38**
(1.94,2.94)
1.51(0.85,2.68)
1.51(0.85,2.68)
3.12**
(1.76,5.52)
1.59*
(1.04,2.42)
1.59*
(1.04,2.42)
3.22**
(2.12,4.88)
1.28(0.92,1.77)
1.28(0.93,1.77)
2.31**
(1.66,3.21)
1.13(0.78,1.64)
1.14(0.78,1.64)
2.32**
(1.59,3.38)
1.79**
(1.24,2.60)
1.79**
(1.24,2.60)
3.20**
(2.22,4.62)
1-hydroxypyrene
Urinary concentration
(ng/mL)
Urinary concentration,
adjusted for specific
gravity (ng/mL)
Urinary concentration,
adjusted for creatinine
(umoles/mole)
1.18
(0.90,1.54)
1.18
(0.91,1.54)
2.15**
(1.60,2.90)
1.23*
(1.02,1.49)
1.24*
(1.02,1.50)
2.17**
(1.76,2.67)
1.13(0.70,1.82)
1.13(0.70,1.82)
2.13**
(1.23,3.70)
1.18(0.84,1.65)
1.18(0.84,1.65)
2.21**
(1.48,3.30)
1.18(0.89,1.56)
1.19(0.90,1.57)
2.09**
(1.51,2.88)
1.17(0.82,1.68)
1.18(0.82,1.69)
2.32**
(1.58,3.42)
1.19(0.89,1.58)
1.18(0.89,1.58)
1.99**
(1.41,2.81)
Pentachlorophenol
Urinary concentration
(ng/mL)
Urinary concentration,
adjusted for specific
gravity (ng/mL)
Urinary concentration,
adjusted for creatinine
(umoles/mole)
1.65**
(1.31,2.07)
1.65**
(1.32,2.07)
3.08**
(2.37,3.99)
1.54**
(1.32,1.79)
1.55**
(1.33,1.80)
2.83**
(2.37,3.37)
1.76**
(1.16,2.68)
1.76**
(1.16,2.67)
3.35**
(2.07,5.43)
1.61**
(1.18,2.20)
1.61**
(1.19,2.20)
3.09**
(2.17,4.39)
1.68**
(1.33,2.13)
1.68**
(1.33,2.13)
3.07**
(2.32,4.06)
1.33*
(1.02,1.75)
1.34*
(1.02,1.75)
2.75**
(2.00,3.79)
2.03**
(1.55,2.67)
2.03**
(1.55,2.67)
3.44**
(2.52,4.69)
3-phenoxybenzoic acid
Urinary concentration
(ng/mL)
Urinary concentration,
adjusted for specific
gravity (ng/mL)
Urinary concentration,
adjusted for creatinine
(umoles/mole)
1.11
(0.77,1.60)
1.10
(0.76,1.59)
2.15**
(1.42,3.26)
1.03(0.80,1.33)
1.02(0.80,1.32)
1.90**
(1.43,2.53)
1.19(0.61,2.32)
1.19(0.60,2.33)
2.44*
(1.13,5.26)
1.23(0.76,1.99)
1.25 (0.77,2.03)
2.50**
(1.42,4.39)
1.00(0.67,1.47)
0.97(0.66,1.44)
1.86**
(1.19,2.90)
0.93(0.57,1.51)
0.91 (0.57,1.46)
2.06**
(1.24,3.42)
1.31(0.87,1.97)
1.33 (0.88,2.02)
2.25**
(1.38,3.70)
3,5,6-TCP(3,5,6-trichloro-2-pyridinol)
Urinary concentration
(ng/mL)
Urinary concentration,
adjusted for specific
gravity (ng/mL)
Urinary concentration,
adjusted for creatinine
(umoles/mole)
1.66**
(1.24,2.24)
1.67**
(1.24,2.24)
3.08**
(2.32,4.09)
1.41**
(1.15,1.73)
1.42**
(1.16,1.74)
2.53**
(2.09,3.05)
1.96*
(1.13,3.39)
1.96*
(1.13,3.38)
3.76**
(2.22,6.38)
1.77**
(1.19,2.62)
1.77**
(1.19,2.62)
3.31**
(2.27,4.83)
1.57**
(1.14,2.15)
1.57**
(1.14,2.16)
2.87**
(2.11,3.90)
1.68*
(1.15,2.45)
1.69**
(1.15,2.46)
3.39**
(2.38,4.83)
1.65**
(1.18,2.31)
1.65**
(1.17,2.31)
2.80**
(2.01,3.89)
* Statistically significantly different from 1 at the 0.05 level, but not at the 0.01 level.
** Statistically significantly different from 1 at the 0.01 level.
                                           R-55

-------

-------
                                    Appendix S
   Detailed Results of Statistical Analysis to Investigate the Apportioning of Aggregated
Potential Exposure Level and Aggregated Potential Absorbed Dose Estimates for the Study
                        Participants Across Exposure Routes
                                        S-l

-------
S-2

-------
Table S-l.   Estimated Mean Proportion of Aggregate Potential Exposure Level and
            Potential Absorbed Dose in Participating NC Children That is Attributable
            to Each Exposure Route, Calculated Overall and Separately by Stratum, and
            95% Confidence Intervals on the Mean
Exposure Route
Estimate of Overall
Mean Proportion
(95% CI)
Stratum
Estimate of Stratum
Mean Proportion
(95% CI)
Significance Level of
Stratum Effect on the
Overall Proportion
Bisphenol-A
Dietary
Ingestion
Inhalation
Indirect
Ingestion
0.99 (0.98,0.99)
0.01 (0.01,0.02)
0.00 (0.00,0.00)
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Daycare Children
Daycare Children
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Daycare Children
Daycare Children
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Daycare Children
Daycare Children
0.99 (0.98,0.99)
0.99 (0.98,0.99)
0.99 (0.98,0.99)
0.99(0.98,1.00)
0.98 (0.96,0.99)
0.99(0.99,1.00)
0.01 (0.01,0.02)
0.01 (0.00,0.02)
0.01 (0.01,0.02)
0.01 (0.00,0.02)
0.02(0.01,0.04)
0.01 (0.00,0.01)
0.00 (0.00,0.00)
0.00 (0.00,0.00)
0.00 (0.00,0.00)
0.00 (0.00,0.00)
0.00 (0.00,0.00)
0.00 (0.00,0.00)
0.762

0.349

<0.001**

0.798

0.376

<0.001**

-

-

-

Chlorpyrifos
Dietary
Ingestion
Inhalation
Indirect
Ingestion
0.54(0.49,0.59)
0.39 (0.34,0.45)
0.06(0.04,0.10)
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Day Care Children
Day Care Children
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Day Care Children
Day Care Children
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Day Care Children
Day Care Children
0.55 (0.48,0.61)
0.53 (0.46,0.60)
0.56(0.50,0.61)
0.52 (0.44,0.60)
0.57(0.50,0.64)
0.51(0.44,0.59)
0.39 (0.32,0.46)
0.40 (0.33,0.47)
0.39 (0.34,0.45)
0.39 (0.30,0.49)
0.37(0.31,0.44)
0.42(0.34,0.50)
0.05 (0.03,0.08)
0.08(0.05,0.13)
0.05 (0.04,0.07)
0.08(0.04,0.18)
0.06 (0.04,0.09)
0.07(0.04,0.12)
0.755

0.496

0.303

0.847

0.981

0.357

0.097

0.273

0.463

                                       S-3

-------
Table S-l.    Estimated Mean Proportion of Aggregate Potential Exposure Level and
             Potential Absorbed Dose in Participating NC Children That is Attributable
             to Each Exposure Route, Calculated Overall and Separately by Stratum, and
             95% Confidence Intervals on the Mean (cont.)
Exposure Route
Estimate of Overall
Mean Proportion
(95% CI)
Stratum
Estimate of Stratum
Mean Proportion
(95% CI)
Significance Level of
Stratum Effect on the
Overall Proportion
Diazinon
Dietary
Ingestion
Inhalation
Indirect
Ingestion
0.55 (0.48,0.62)
0.40 (0.34,0.46)
0.05 (0.03,0.08)
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Day Care Children
Day Care Children
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Day Care Children
Day Care Children
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Day Care Children
Day Care Children
0.50(0.43,0.57)
0.60 (0.50,0.69)
0.55 (0.48,0.62)
0.55 (0.43,0.66)
0.55 (0.48,0.62)
0.55 (0.43,0.67)
0.46 (0.40,0.53)
0.34 (0.27,0.43)
0.41 (0.35,0.47)
0.39 (0.30,0.49)
0.41 (0.35,0.48)
0.39 (0.30,0.49)
0.04 (0.02,0.07)
0.06 (0.04,0.09)
0.04 (0.02,0.07)
0.06(0.03,0.11)
0.03 (0.02,0.05)
0.06(0.03,0.15)
0.058

0.987

0.983

0.008**

0.701

0.673

0.049*

0.381

0.206

Di-n-butylphthalate
Dietary
Ingestion
Inhalation
Indirect
Ingestion
0.93 (0.91,0.94)
0.06 (0.05,0.07)
0.01 (0.01,0.01)
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Daycare Children
Daycare Children
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Daycare Children
Daycare Children
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Daycare Children
Daycare Children
0.92 (0.90,0.94)
0.93 (0.91,0.95)
0.91 (0.88,0.93)
0.94(0.93,0.96)
0.93 (0.91,0.94)
0.93 (0.90,0.95)
0.07(0.05,0.09)
0.05 (0.04,0.07)
0.08(0.06,0.10)
0.05 (0.03,0.06)
0.06 (0.05,0.07)
0.06 (0.04,0.09)
0.01 (0.01,0.01)
0.01 (0.01,0.02)
0.01 (0.01,0.02)
0.01 (0.01,0.02)
0.01 (0.01,0.02)
0.01 (0.01,0.01)
0.561

0.014*

0.842

0.297

0.010*

0.892

0.301

0.470

0.079

                                        S-4

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Table S-l.    Estimated Mean Proportion of Aggregate Potential Exposure Level and
             Potential Absorbed Dose in Participating NC Children That is Attributable
             to Each Exposure Route, Calculated Overall and Separately by Stratum, and
             95% Confidence Intervals on the Mean (cont.)
Exposure Route
Estimate of Overall
Mean Proportion
(95% CI)
Stratum
Estimate of Stratum
Mean Proportion
(95% CI)
Significance Level of
Stratum Effect on the
Overall Proportion
2,4-D (2,4-dichlorophenoxyacetic acid)
Dietary
Ingestion
Inhalation
Indirect
Ingestion
0.95 (0.93,0.96)
0.03 (0.02,0.04)
0.02(0.01,0.03)
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Day Care Children
Day Care Children
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Day Care Children
Day Care Children
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Day Care Children
Day Care Children
0.95 (0.93,0.97)
0.94(0.91,0.96)
0.92 (0.90,0.94)
0.96 (0.93,0.98)
0.94 (0.92,0.96)
0.95 (0.92,0.97)
0.03 (0.02,0.05)
0.03 (0.01,0.05)
0.04(0.03,0.06)
0.02(0.01,0.04)
0.03 (0.02,0.04)
0.03 (0.02,0.06)
0.01 (0.00,0.02)
0.03 (0.01,0.07)
0.02(0.01,0.04)
0.01 (0.00,0.04)
0.02(0.01,0.04)
0.01 (0.01,0.03)
0.412

0.038*

0.629

0.422

0.021*

0.850

0.009**

0.383

0.191

c/s-Permethrin
Dietary
Ingestion
Inhalation
Indirect
Ingestion
0.55 (0.47,0.63)
0.05 (0.03,0.07)
0.39(0.31,0.47)
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Day Care Children
Day Care Children
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Day Care Children
Day Care Children
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Day Care Children
Day Care Children
0.53 (0.42,0.63)
0.57 (0.47,0.67)
0.60(0.51,0.70)
0.49 (0.38,0.60)
0.50(0.42,0.59)
0.59 (0.45,0.72)
0.07(0.04,0.11)
0.03 (0.02,0.05)
0.03 (0.02,0.05)
0.07(0.03,0.13)
0.06(0.04,0.11)
0.04(0.03,0.05)
0.39(0.30,0.50)
0.39 (0.29,0.49)
0.36 (0.27,0.46)
0.42(0.31,0.54)
0.42(0.34,0.51)
0.36(0.24,0.50)
0.542

0.102

0.309

0.020*

0.065

0.065

0.920

0.401

0.452

                                        S-5

-------
Table S-l.     Estimated Mean Proportion of Aggregate Potential Exposure Level and
               Potential Absorbed Dose in Participating NC Children That is Attributable
               to Each Exposure Route, Calculated Overall and Separately by Stratum, and
               95% Confidence Intervals on the Mean  (cont.)
Exposure Route
Estimate of Overall
Mean Proportion
(95% CI)
Stratum
Estimate of Stratum
Mean Proportion
(95% CI)
Significance Level of
Stratum Effect on the
Overall Proportion
Jrans-Permethrin
Dietary
Ingestion
Inhalation
Indirect
Ingestion
0.57(0.50,0.65)
0.04(0.03,0.06)
0.37(0.30,0.45)
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Day Care Children
Day Care Children
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Day Care Children
Day Care Children
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Day Care Children
Day Care Children
0.57 (0.46,0.67)
0.58 (0.48,0.67)
0.61 (0.51,0.70)
0.53 (0.43,0.63)
0.54(0.45,0.61)
0.61 (0.47,0.73)
0.07(0.04,0.11)
0.03 (0.02,0.04)
0.03 (0.02,0.04)
0.06(0.03,0.12)
0.06(0.03,0.10)
0.03 (0.02,0.04)
0.36 (0.26,0.47)
0.39 (0.30,0.48)
0.36 (0.27,0.46)
0.39(0.29,0.50)
0.40 (0.32,0.48)
0.35 (0.23,0.48)
0.870

0.241

0.390

0.004**

0.068

0.048*

0.651

0.618

0.541

3,5,6-TCP(3,5,6-trichloro-2-pyridinol)
Dietary
Ingestion
Inhalation
Indirect
Ingestion
0.95 (0.93,0.97)
0.03 (0.02,0.04)
0.02(0.01,0.03)
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Day Care Children
Day Care Children
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Day Care Children
Day Care Children
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Day Care Children
Day Care Children
0.94(0.91,0.96)
0.96 (0.93,0.98)
0.95 (0.92,0.96)
0.96 (0.92,0.97)
0.94 (0.90,0.96)
0.96 (0.94,0.98)
0.04 (0.02,0.06)
0.02(0.01,0.03)
0.03 (0.02,0.05)
0.02(0.01,0.04)
0.03 (0.02,0.05)
0.02(0.01,0.04)
0.02(0.01,0.03)
0.02(0.01,0.04)
0.02(0.01,0.03)
0.02(0.01,0.05)
0.03 (0.02,0.06)
0.01 (0.01,0.02)
0.209

0.671

0.093

0.018*

0.146

0.381

0.926

0.454

0.019*

* Statistically significant at the 0.05 level, but not at the 0.01 level.
** Statistically significant at the 0.01 level.
Note: Caution should be taken when interpreting results of statistical analysis when estimated proportions are near 0 or !
                                              S-6

-------
Table S-2.   Estimated Mean Proportion of Aggregate Potential Exposure Level and
            Potential Absorbed Dose in Participating OH Children That is Attributable
            to Each Exposure Route, Calculated Overall and Separately by Stratum, and
            95% Confidence Intervals on the Mean
Exposure Route
Estimate of Overall
Mean Proportion
(95% CI)
Stratum
Estimate of Stratum
Mean Proportion
(95% CI)
Significance Level of
Stratum Effect on the
Overall Proportion
Bisphenol-A
Dietary
Ingestion
Inhalation
Indirect
Ingestion
0.99 (0.99,0.99)
0.01 (0.00,0.01)
0.00 (0.00,0.00)
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Daycare Children
Daycare Children
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Daycare Children
Daycare Children
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Daycare Children
Daycare Children
0.99(0.99,1.00)
0.99 (0.99,0.99)
0.99 (0.99,0.99)
0.99(0.99,1.00)
0.99(0.99,1.00)
0.99 (0.99,0.99)
0.01 (0.00,0.01)
0.01 (0.01,0.01)
0.01 (0.01,0.01)
0.00(0.00,0.01)
0.00(0.00,0.01)
0.01 (0.01,0.01)
0.00 (0.00,0.00)
0.00 (0.00,0.00)
0.00 (0.00,0.00)
0.00 (0.00,0.00)
0.00 (0.00,0.00)
0.00 (0.00,0.00)
0.364

0.087

0.015*

0.516

0.039*

0.008**

-

-

-

Chlorpyrifos
Dietary
Ingestion
Inhalation
Indirect
Ingestion
0.76 (0.69,0.82)
0.19(0.14,0.26)
0.04(0.03,0.06)
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Day Care Children
Day Care Children
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Day Care Children
Day Care Children
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Day Care Children
Day Care Children
0.78 (0.67,0.86)
0.74(0.67,0.81)
0.71 (0.65,0.77)
0.80(0.67,0.89)
0.79 (0.70,0.86)
0.74(0.64,0.81)
0.19(0.12,0.29)
0.20(0.15,0.26)
0.24 (0.20,0.29)
0.16(0.08,0.27)
0.19(0.12,0.27)
0.20(0.15,0.27)
0.03 (0.02,0.04)
0.05 (0.04,0.08)
0.04(0.03,0.06)
0.04 (0.02,0.07)
0.03 (0.02,0.04)
0.06 (0.03,0.09)
0.440

0.174

0.272

0.900

0.147

0.650

<0.001**

0.560

0.038*

                                       S-7

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Table S-2.    Estimated Mean Proportion of Aggregate Potential Exposure Level and
             Potential Absorbed Dose in Participating OH Children That is Attributable
             to Each Exposure Route, Calculated Overall and Separately by Stratum, and
             95% Confidence Intervals on the Mean (cont.)
Exposure Route
Estimate of Overall
Mean Proportion
(95% CI)
Stratum
Estimate of Stratum
Mean Proportion
(95% CI)
Significance Level of
Stratum Effect on the
Overall Proportion
Diazinon
Dietary
Ingestion
Inhalation
Indirect
Ingestion
0.62(0.52,0.70)
0.33 (0.27,0.41)
0.05 (0.03,0.08)
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Day Care Children
Day Care Children
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Day Care Children
Day Care Children
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Day Care Children
Day Care Children
0.60 (0.49,0.70)
0.64(0.53,0.73)
0.62 (0.56,0.68)
0.61 (0.44,0.76)
0.67 (0.59,0.74)
0.57(0.43,0.70)
0.38 (0.28,0.48)
0.30 (0.23,0.37)
0.30 (0.26,0.36)
0.37(0.25,0.50)
0.29 (0.23,0.35)
0.38 (0.28,0.49)
0.03 (0.02,0.06)
0.07(0.04,0.13)
0.06 (0.04,0.08)
0.04(0.01,0.11)
0.05 (0.03,0.08)
0.05(0.03,0.11)
0.519

0.897

0.103

0.155

0.348

0.058

0.009**

0.472

0.667

Di-n-butylphthalate
Dietary
Ingestion
Inhalation
Indirect
Ingestion
0.80 (0.76,0.83)
0.18(0.15,0.21)
0.02(0.01,0.03)
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Day Care Children
Day Care Children
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Day Care Children
Day Care Children
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Day Care Children
Day Care Children
0.82(0.76,0.87)
0.78(0.72,0.83)
0.82(0.80,0.84)
0.78(0.70,0.85)
0.76(0.69,0.81)
0.84(0.80,0.87)
0.16(0.12,0.22)
0.20(0.15,0.26)
0.16(0.14,0.18)
0.21(0.15,0.28)
0.22(0.17,0.28)
0.15(0.12,0.19)
0.01 (0.01,0.03)
0.02(0.01,0.03)
0.02 (0.02,0.03)
0.01 (0.00,0.03)
0.02(0.01,0.05)
0.01 (0.01,0.02)
0.303

0.379

0.017*

0.365

0.186

0.047*

0.447

0.257

0.008**

                                         So
                                         -o

-------
Table S-2.    Estimated Mean Proportion of Aggregate Potential Exposure Level and
             Potential Absorbed Dose in Participating OH Children That is Attributable
             to Each Exposure Route, Calculated Overall and Separately by Stratum, and
             95% Confidence Intervals on the Mean (cont.)
Exposure Route
Estimate of Overall
Mean Proportion
(95% CI)
Stratum
Estimate of Stratum
Mean Proportion
(95% CI)
Significance Level of
Stratum Effect on the
Overall Proportion
2,4-D (2,4-dichlorophenoxyacetic acid)
Dietary
Ingestion
Inhalation
Indirect
Ingestion
0.92(0.89,0.95)
0.03 (0.02,0.04)
0.03 (0.02,0.05)
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Day Care Children
Day Care Children
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Day Care Children
Day Care Children
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Day Care Children
Day Care Children
0.95 (0.90,0.97)
0.89 (0.83,0.93)
0.91 (0.88,0.93)
0.93 (0.88,0.97)
0.93 (0.89,0.95)
0.92(0.85,0.95)
0.02(0.01,0.04)
0.03 (0.02,0.05)
0.02(0.01,0.02)
0.04 (0.02,0.09)
0.03 (0.02,0.05)
0.02(0.01,0.04)
0.02(0.01,0.05)
0.05 (0.03,0.09)
0.07(0.05,0.11)
0.02(0.01,0.03)
0.03 (0.02,0.05)
0.04(0.02,0.08)
0.040*

0.354

0.633

0.417

0.085

0.100

0.058

<0.001**

0.414

c/s-Permethrin
Dietary
Ingestion
Inhalation
Indirect
Ingestion
0.56 (0.48,0.64)
0.04(0.03,0.05)
0.39(0.31,0.48)
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Daycare Children
Daycare Children
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Daycare Children
Daycare Children
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Daycare Children
Daycare Children
0.60 (0.47,0.71)
0.53 (0.44,0.61)
0.61 (0.53,0.68)
0.51(0.37,0.65)
0.58(0.49,0.67)
0.54(0.42,0.66)
0.04(0.02,0.05)
0.05 (0.04,0.07)
0.06 (0.04,0.08)
0.03 (0.02,0.05)
0.04 (0.03,0.06)
0.05 (0.03,0.08)
0.36 (0.25,0.49)
0.42 (0.34,0.50)
0.33 (0.26,0.41)
0.45 (0.32,0.59)
0.38 (0.29,0.47)
0.40 (0.29,0.52)
0.269

0.197

0.618

0.165

0.010*

0.700

0.405

0.088

0.719

                                        S-9

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Table S-2.     Estimated Mean Proportion of Aggregate Potential Exposure Level and
               Potential Absorbed Dose in Participating OH Children That is Attributable
               to Each Exposure Route, Calculated Overall and Separately by Stratum, and
               95% Confidence Intervals on the Mean  (cont.)
Exposure Route
Estimate of Overall
Mean Proportion
(95% CI)
Stratum
Estimate of Stratum
Mean Proportion
(95% CI)
Significance Level of
Stratum Effect on the
Overall Proportion
Jrans-Permethrin
Dietary
Ingestion
Inhalation
Indirect
Ingestion
0.58 (0.49,0.66)
0.04(0.03,0.06)
0.37 (0.29,0.46)
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Daycare Children
Daycare Children
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Daycare Children
Daycare Children
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Daycare Children
Daycare Children
0.58 (0.45,0.70)
0.58 (0.49,0.67)
0.61 (0.53,0.68)
0.55 (0.40,0.70)
0.60(0.51,0.69)
0.56(0.44,0.67)
0.02 (0.02,0.04)
0.06 (0.04,0.08)
0.05 (0.04,0.08)
0.03 (0.02,0.05)
0.03 (0.02,0.04)
0.05 (0.03,0.09)
0.38(0.26,0.51)
0.36 (0.29,0.45)
0.33 (0.26,0.41)
0.41 (0.28,0.56)
0.36 (0.27,0.45)
0.38 (0.28,0.50)
0.962

0.516

0.435

<0.001**

0.015*

0.054

0.820

0.296

0.635

3,5,6-TCP(3,5,6-trichloro-2-pyridinol)
Dietary
Ingestion
Inhalation
Indirect
Ingestion
0.98 (0.96,0.99)
0.02(0.01,0.04)
0.00(0.00,0.01)
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Day Care Children
Day Care Children
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Day Care Children
Day Care Children
Low Income Children
Middle/Upper Income Children
Urban Children
Rural Children
Non-Day Care Children
Day Care Children
0.97(0.93,0.99)
0.99 (0.97,0.99)
0.97(0.96,0.98)
0.99(0.94,1.00)
0.97 (0.94,0.99)
0.99 (0.96,0.99)
0.03(0.01,0.06)
0.01 (0.00,0.02)
0.02(0.01,0.03)
0.01 (0.00,0.06)
0.02(0.01,0.05)
0.01 (0.00,0.03)
0.00(0.00,0.01)
0.00(0.00,0.01)
0.01 (0.00,0.01)
0.00(0.00,0.01)
0.00(0.00,0.01)
0.00(0.00,0.01)
0.023*

0.393

0.148

0.010**

0.493

0.147

-

-

-

* Statistically significant at the 0.05 level, but not at the 0.01 level.
** Statistically significant at the 0.01 level.
Note: Caution should be taken when interpreting results of statistical analysis when estimated proportions are near 0 or 1.
                                              S-10

-------
Table S-3.     Estimated Mean Proportion of Total Potential Exposure Level and Total
               Potential Exposed Dose in NC Adults That is Attributable to Each Exposure
               Route, Calculated Overall and Separately by Stratum, and 95% Confidence
               Intervals on the Mean
Exposure Route
Estimate of Overall
Mean Proportion
(95% CI)
Stratum
Estimate of Stratum
Mean Proportion
(95% CI)
Significance Level of
Stratum Effect on the
Overall Proportion
2,4-D (2,4-dichlorophenoxyacetic acid)
Dietary
Ingestion
Inhalation
Indirect
Ingestion
0.93 (0.82,0.97)
0.05(0.02,0.15)
0.01 (0.00,0.24)
Low Income
Middle/Upper Income
Urban
Rural
Non-Daycare Households
Daycare Households
Low Income
Middle/Upper Income
Urban
Rural
Non-Daycare Households
Daycare Households
Low Income
Middle/Upper Income
Urban
Rural
Non-Daycare Households
Daycare Households
0.92 (0.77,0.97)
0.94(0.80,0.98)
0.90 (0.82,0.95)
0.95 (0.71,0.99)
0.95 (0.82,0.98)
0.91 (0.74,0.97)
0.08 (0.02,0.24)
0.03(0.01,0.14)
0.06(0.03,0.14)
0.04 (0.00,0.26)
0.04(0.01,0.15)
0.06 (0.02,0.22)
0.00 (0.00,0.32)
0.02 (0.00,0.39)
0.02(0.00,0.14)
0.00 (0.00,0.74)
0.01 (0.00,0.25)
0.01 (0.00,0.31)
0.663

0.542

0.455

0.236

0.665

0.509

0.348

0.667

0.721

3,5,6-TCP(3,5,6-trichloro-2-pyridinol)
Dietary
Ingestion
Inhalation
Indirect
Ingestion
0.94(0.84,0.98)
0.05(0.01,0.15)
0.01(0.00,0.10)
Low Income
Middle/Upper Income
Urban
Rural
Non-Daycare Households
Daycare Households
Low Income
Middle/Upper Income
Urban
Rural
Non-Daycare Households
Daycare Households
Low Income
Middle/Upper Income
Urban
Rural
Non-Daycare Households
Daycare Households
0.92 (0.76,0.97)
0.96 (0.85,0.99)
0.92 (0.85,0.96)
0.96(0.74,1.00)
0.95 (0.84,0.99)
0.93 (0.78,0.98)
0.07 (0.02,0.22)
0.03(0.01,0.14)
0.07(0.03,0.14)
0.03 (0.00,0.26)
0.04(0.01,0.15)
0.06(0.01,0.21)
0.01(0.00,0.18)
0.01 (0.00,0.20)
0.01 (0.00,0.08)
0.01 (0.00,0.46)
0.01 (0.00,0.18)
0.01 (0.00,0.21)
0.276

0.556

0.606

0.298

0.529

0.631

0.767

0.978

0.865

* Statistically significant at the 0.05 level, but not at the 0.01 level.
** Statistically significant at the 0.01 level.
Note: Caution should be taken when interpreting results of statistical analysis when estimated proportions are near 0 or 1.
                                              S-ll

-------
Table S-4.     Estimated Mean Proportion of Aggregate Potential Exposure Level and
               Potential Absorbed Dose in Participating OH Adults That is Attributable to
               Each Exposure Route, Calculated Overall and Separately by Stratum, and
               95% Confidence Intervals on the Mean
Exposure Route
Estimate of Overall
Mean Proportion
(95% CI)
Stratum
Estimate of Stratum
Mean Proportion
(95% CI)
Significance Level of
Stratum Effect on the
Overall Proportion
2,4-D (2,4-dichlorophenoxyacetic acid)
Dietary
Ingestion
Inhalation
Indirect
Ingestion
0.93 (0.78,0.98)
0.04(0.01,0.17)
0.03(0.01,0.18)
Low Income
Middle/Upper Income
Urban
Rural
Non-Daycare Households
Daycare Households
Low Income
Middle/Upper Income
Urban
Rural
Non-Daycare Households
Daycare Households
Low Income
Middle/Upper Income
Urban
Rural
Non-Daycare Households
Daycare Households
0.96 (0.77,0.99)
0.88 (0.70,0.96)
0.92 (0.83,0.96)
0.94(0.59,0.99)
0.95 (0.79,0.99)
0.90 (0.70,0.97)
0.04 (0.00,0.30)
0.03(0.01,0.18)
0.03(0.01,0.10)
0.04(0.00,0.51)
0.04 (0.00,0.23)
0.03 (0.00,0.24)
0.01 (0.00,0.18)
0.07(0.02,0.28)
0.05(0.02,0.14)
0.02 (0.00,0.37)
0.02(0.00,0.16)
0.05 (0.01,0.26)
0.225

0.807

0.339

0.942

0.779

0.982

0.157

0.631

0.246

3,5,6-TCP(3,5,6-trichloro-2-pyridinol)
Dietary
Ingestion
Inhalation
Indirect
Ingestion
0.98(0.76,1.00)
0.02 (0.00,0.24)
0.00 (0.00,0.94)
Low Income
Middle/Upper Income
Urban
Rural
Non-Daycare Households
Daycare Households
Low Income
Middle/Upper Income
Urban
Rural
Non-Daycare Households
Daycare Households
Low Income
Middle/Upper Income
Urban
Rural
Non-Daycare Households
Daycare Households
0.98(0.60,1.00)
0.98(0.79,1.00)
0.97 (0.90,0.99)
0.99(0.26,1.00)
0.99(0.73,1.00)
0.97(0.66,1.00)
0.02 (0.00,0.42)
0.01 (0.00,0.21)
0.02 (0.00,0.09)
0.01 (0.00,0.77)
0.01 (0.00,0.29)
0.02 (0.00,0.34)
0.00 (0.00,0.98)
0.00 (0.00,0.93)
0.00(0.00,0.16)
0.00(0.00,1.00)
0.00 (0.00,0.98)
0.00 (0.00,0.96)
0.737

0.818

0.578

0.722

0.856

0.664

0.981

0.877

0.709

* Statistically significant at the 0.05 level, but not at the 0.01 level.
** Statistically significant at the 0.01 level.
Note: Caution should be taken when interpreting results of statistical analysis when estimated proportions are near 0 or 1.
                                              S-12

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Table S-5.   Estimated Ratio Between Two Exposure Routes of Geometric Mean
            Potential Exposure Level and Potential Absorbed Dose Estimates in
            Participating NC Children, and 95% Confidence Intervals on This Ratio
Parameter
Significance
Level for Overall
Differences
Among the
Three Exposure
Routes
Ratio of Geometric Means (95%CI)
Dietary Ingestion
Route vs. Inhalation
Route
Dietary Ingestion
Route vs. Indirect
Ingestion Route
Inhalation Route
vs. Indirect
Ingestion Route
Bisphenol-A
Potential Exposure Level
Potential Absorbed Dose
0.0001
O.0001
207.17**
(139.92,306.76)
207.37**
(139.96,307.25)
2235.24**
(1459.50,3423.30)
2212.20**
(1438.94,3401.01)
10.79**
(7.38,15.77)
10.67**
(7.33,15.53)
Chlorpyrifos
Potential Exposure Level
Potential Absorbed Dose
0.0001
O.0001
1.41
(0.98,2.03)
1.41
(0.98,2.02)
12.60**
(8.24,19.27)
12.61**
(8.24,19.28)
8.92**
(6.61,12.05)
8.93**
(6.61,12.06)
Diazinon
Potential Exposure Level
Potential Absorbed Dose
0.0001
O.0001
1.42
(0.99,2.04)
1.41
(0.98,2.03)
20.70**
(12.62,33.96)
20.68**
(12.62,33.88)
14.58**
(10.84,19.60)
14.62**
(10.88,19.65)
Di-w-butylphthalate
Potential Exposure Level
Potential Absorbed Dose
0.0001
O.0001
22.92**
(16.08,32.67)
22.61**
(15.87,32.20)
126.17**
(86.76,183.47)
124.38**
(85.01,182.00)
5.50**
(4.12,7.35)
5.50**
(4.16,7.27)
2,4-D (2,4-dichlorophenoxyacetic acid)
Potential Exposure Level
Potential Absorbed Dose
0.0001
O.0001
48.67**
(31.68,74.77)
48.63**
(31.63,74.77)
194.41**
(121.38,311.36)
193.78**
(120.86,310.70)
3.99**
(2.37,6.72)
3.98**
(2.37,6.71)
cis-Permethrin
Potential Exposure Level
Potential Absorbed Dose
0.0001
O.0001
22.18**
(11.90,41.34)
22.17**
(11.89,41.31)
2.09
(0.99,4.44)
2.10
(0.99,4.44)
0.09**
(0.06,0.15)
0.09**
(0.06,0.15)
fraws-Permethrin
Potential Exposure Level
Potential Absorbed Dose
0.0001
O.0001
22.02**
(12.06,40.19)
21.81**
(11.95,39.79)
1.80
(0.85,3.82)
1.77
(0.84,3.75)
0.08**
(0.05,0.13)
0.08**
(0.05,0.13)
                                       S-13

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Table S-5.    Estimated Ratio Between Two Exposure Routes of Geometric Mean
              Potential Exposure Level and Potential Absorbed Dose Estimates in
              Participating NC Children, and 95% Confidence Intervals on This Ratio
              (cont.)
Parameter
Significance
Level for Overall
Differences
Among the
Three Exposure
Routes
Ratio of Geometric Means (95%CI)
Dietary Ingestion
Route vs. Inhalation
Route
Dietary Ingestion
Route vs. Indirect
Ingestion Route
Inhalation Route
vs. Indirect
Ingestion Route
3,5,6-TCP(3,5,6-trichloro-2-pyridinol)
Potential Exposure Level
Potential Absorbed Dose
0.0001
0.0001
72.58**
(48.94,107.64)
72.84**
(49.12,108.02)
229.05**
(136.67,383.88)
230.39**
(137.23,386.82)
3.16**
(2.12,4.70)
3.16**
(2.12,4.71)
* Statistically significantly different from 1 at the 0.05 level, but not at the 0.01 level.
** Statistically significantly different from 1 at the 0.01 level.
                                            S-14

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Table S-6.   Estimated Ratio Between Two Exposure Routes of Geometric Mean
            Potential Exposure Level and Potential Absorbed Dose Estimates in
            Participating OH Children, and 95% Confidence Intervals on This Ratio
Parameter
Significance
Level for Overall
Differences
Among the
Three Exposure
Routes
Ratio of Geometric Means (95%CI)
Dietary Ingestion
Route vs. Inhalation
Route
Dietary Ingestion
Route vs. Indirect
Ingestion Route
Inhalation Route
vs. Indirect
Ingestion Route
Bisphenol-A
Potential Exposure Level
Potential Absorbed Dose
0.0001
O.0001
181.33**
(118.07,278.49)
183.70**
(120.11,280.98)
1853.99**
(1235.33,2782.49)
1851.10**
(1233.56,2777.80)
10.22**
(6.74,15.52)
10.08**
(6.67,15.22)
Chlorpyrifos
Potential Exposure Level
Potential Absorbed Dose
0.0001
O.0001
6.03**
(3.62,10.05)
6.06**
(3.63,10.13)
30.88**
(17.83,53.47)
31.03**
(17.93,53.70)
5.12**
(3.23,8.13)
5 12**
(3.24,8.11)
Diazinon
Potential Exposure Level
Potential Absorbed Dose
0.0001
O.0001
2.04**
(1.20,3.44)
2.04**
(1.20,3.46)
20.68**
(10.96,39.00)
20.78**
(11.00,39.27)
10.15**
(5.93,17.38)
10.19**
(5.95,17.45)
Di-w-butylphthalate
Potential Exposure Level
Potential Absorbed Dose
0.0001
O.0001
4.68**
(2.94,7.44)
4.63**
(2.89,7.42)
53.07**
(33.60,83.84)
51.94**
(32.47,83.07)
11.34**
(7.75,16.60)
11.21**
(7.68,16.36)
2,4-D (2,4-dichlorophenoxyacetic acid)
Potential Exposure Level
Potential Absorbed Dose
0.0001
O.0001
52.25**
(29.55,92.38)
51.75**
(29.24,91.58)
47.52**
(25.29,89.31)
47.22**
(25.10,88.85)
0.91
(0.46,1.78)
0.91
(0.47,1.79)
cis-Permethrin
Potential Exposure Level a
Potential Absorbed Dose
-
0.0001
-
22.00**
(11.20,43.24)
-
2.60*
(1.07,6.32)
-
0.12**
(0.07,0.21)
fraws-Permethrin
Potential Exposure Level
Potential Absorbed Dose
O.0001
0.0001
24.32**
(12.72,46.49)
24.29**
(12.70,46.45)
3.52**
(1.40,8.89)
3.38**
(1.34,8.56)
0.14**
(0.08,0.27)
0.14**
(0.07,0.26)
                                       S-15

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Table S-6.    Estimated Ratio Between Two Exposure Routes of Geometric Mean
              Potential Exposure Level and Potential Absorbed Dose Estimates in
              Participating OH Children, and 95% Confidence Intervals on This Ratio
              (cont.)
Parameter
Significance
Level for Overall
Differences
Among the
Three Exposure
Routes
Ratio of Geometric Means (95%CI)
Dietary Ingestion
Route vs. Inhalation
Route
Dietary Ingestion
Route vs. Indirect
Ingestion Route
Inhalation Route
vs. Indirect
Ingestion Route
3,5,6-TCP(3,5,6-trichloro-2-pyridinol)
Potential Exposure Level
Potential Absorbed Dose
0.0001
0.0001
132.32**
(76.69,228.30)
129.55**
(75.17,223.29)
546.95**
(313.76,953.47)
541.95**
(310.36,946.37)
4.13**
(2.59,6.59)
4.18**
(2.63,6.65)
a Model would not converge.

* Statistically significantly different from 1 at the 0.05 level, but not at the 0.01 level.
** Statistically significantly different from 1 at the 0.01 level.
                                            S-16

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Table S-7.    Estimated Ratio of Geometric Mean for Potential Exposure Level and
              Potential Absorbed Dose Estimates in NC Adults, Calculated Between Two
              Exposure Routes, and 95% Confidence Intervals on This Ratio
Parameter
Significance
Level for Overall
Differences
Among the
Three Exposure
Routes
Ratio of Geometric Means (95%CI)
Dietary Ingestion
Route vs. Inhalation
Route
Dietary Ingestion
Route vs. Indirect
Ingestion Route
Inhalation Route
vs. Indirect
Ingestion Route
2,4-D (2,4-dichlorophenoxyacetic acid)
Potential Exposure Level
Potential Absorbed Dose
0.0001
O.0001
40.74**
(25.45,65.21)
40.88**
(25.53,65.47)
379.85**
(212.96,677.50)
379.64**
(212.71,677.60)
9.32**
(5.28,16.48)
9 29**
(5.26,16.38)
3,5,6-TCP(3,5,6-trichloro-2-pyridinol)
Potential Exposure Level
Potential Absorbed Dose
O.0001
0.0001
41.76**
(27.05,64.48)
41.74**
(27.04,64.44)
358.70**
(219.26,586.83)
358.31**
(218.93,586.41)
8.59**
(6.08,12.13)
8.58**
(6.08,12.12)
* Statistically significantly different from 1 at the 0.05 level, but not at the 0.01 level.
** Statistically significantly different from 1 at the 0.01 level.
                                            S-17

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Table S-8.    Estimated Ratio Between Two Exposure Routes of Geometric Mean
              Potential Exposure Level and Potential Absorbed Dose Estimates in
              Participating OH Adults, and 95% Confidence Intervals on This Ratio
Parameter
Significance
Level for Overall
Differences
Among the
Three Exposure
Routes
Ratio of Geometric Means (95%CI)
Dietary Ingestion
Route vs. Inhalation
Route
Dietary Ingestion
Route vs. Indirect
Ingestion Route
Inhalation Route
vs. Indirect
Ingestion Route
2,4-D (2,4-dichlorophenoxyacetic acid)
Potential Exposure Level
Potential Absorbed Dose
0.0001
O.0001
49.33**
(31.89,76.32)
49.32**
(31.89,76.27)
78.75**
(40.28,153.93)
78.63**
(40.16,153.96)
1.60
(0.85,3.00)
1.59
(0.84,3.01)
3,5,6-TCP(3,5,6-trichloro-2-pyridinol)
Potential Exposure Level
Potential Absorbed Dose
O.0001
0.0001
102.37**
(62.73,167.06)
102.51**
(62.72,167.53)
907.46**
(519.56,1584.93)
907.69**
(519.81,1585.00)
8.86**
(5.70,13.79)
8.85**
(5.67,13.82)
* Statistically significantly different from 1 at the 0.05 level, but not at the 0.01 level.
** Statistically significantly different from 1 at the 0.01 level.
                                            S-18

-------