£ EDA United States	°fficeof
Environmental Protection Agency	jpmmm4j Research and Development
National Human Exposure Assessment
Survey (NHEXAS)
Maryland
Quality Systems and Implementation Plan
for Human Exposure Assessment
Emory University
Atlanta, GA 30322
Cooperative Agreement CR 822038
Standard Operating Procedure	NHX/SOP-G03
Title: Identification Numbers for Samples and Forms
Source: Harvard University/Johns Hopkins University
U.S. Environmental Protection Agency
Office of Research and Development
Human Exposure & Atmospheric Sciences Division
Human Exposure Research Branch
Notice: The U.S. Environmental Protection Agency (EPA), through its Office of Research and Development (ORD), partially
funded and collaborated in the research described here. This protocol is part of the Quality Systems
Implementation Plan (QSIP) that was reviewed by the EPA and approved for use in this demonstration/scoping
study. Mention of trade names or commercial products does not constitute endorsement or recommendation by
EPA for use.

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G03 Identification Numbers for Samples and Forms,
Rev. 1.0
page 1 of 5
October 5, 1995
1	Title of Standard Operating Procedure
Harvard University/Emory University/Johns Hopkins University Standard Operating Procedures:
G03 Identification Numbers for Samples and Forms, Rev. 1.0
2	Overview and Purpose
The purpose of this SOP is to indicate the proper method for assigning unique Identification
Numbers for all samples taken and forms used in the NHEXAS Phase I Study.
3	Discussion
The development of unique Identification Numbers for all samples and forms used in the NHEXAS
Phase I Study is of prime importance in that these numbers will be used to collate data taken in
various media and analyzed by various laboratories. All data tracking procedures will be built upon
the use of these Identification Numbers. Further, the Identification Numbers will be used in place
of respondents' names, addresses, and other identifying data to ensure confidentiality and
anonymity. Finally, by design, inspection of any Identification Number will afford immediate
information on the type of sample, geographic stratum, and Cycle number associated with that
sample. Thus the Identification Number contains much of the essential information associated with
any sample.
Each label will be printed in both bar-code and human-readable format, in order to minimize errors
and expedite sample tracking.
4	Personnel Responsibilities
The assignment of the Identification Numbers to the samples is the responsibility of the Principal
Investigator and the Field Coordinator or their designate. Printing of labels is the responsibility of
the Field Coordination Center Supervisor or his designate. All numbers and letters in the
Identification Number have meaning and should not be altered in any way by staff or respondents.
5	Required Equipment and Reagents
0 No equipment is required for the initial assignment.
0 Labels will be printed using a printer and software that can generate both bar codes and human-
readable numbers and letters.
0 For the labeling of samples, printed labels with the appropriate Identification Number will be
affixed to sample containers. Identical labels will be affixed to logsheets, Chain-of-Custody
forms, and other paperwork in the Field Packet brought to each home.
0 Bar code readers will be used in the shipping, receiving, and handling of samples and forms.

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G03 Identification Numbers for Samples and Forms,
Rev. 1.0
page 2 of 5
October 5, 1995
6 Procedure
The Identification number consists of several parts totaling nine digits:
HIN -1 - A - C - ST - R
HIN Household identifying number. This is a unique number identifying each residence in the
investigation. Valid Values: 001 < HIN < 999.
The first digit of the HIN will denote the county, with the numerical order corresponding to
the alphabetical order:
1	= Anne Arundel
2	= Baltimore City
3	= Baltimore County
4	= Queen Anne's
5	= Talbot
I Individual Respondent identifying number. This number uniquely identifies different target
individuals within the same household. If the first target individual drops out and another is
selected, a different digit will be used. The digit 0 is used before a target individual is
selected, and if a household participates only in the Descriptive Questionnaire.
Valid Values: 0 < I < 9.
A Geographic Stratum identifying letter. Identifies the geographic stratum from which the
sample was taken. Redundant with HIN but used for ease of quick assessment and sorting
of data. Valid Values: U (urban stratum), S (suburban stratum), R (rural stratum).
C Cycle identifying number. Identifies monitoring Cycle for a residence. Note that Cycles are
associated with a time period, not the visit number. For example, if Cycle = 4 corresponds
to a visit occurring between April 1, 1996 and May 15, 1996, all samples collected during
this period would have C = 4. A home not visited during this period would not have C = 4
for any sample. The next visit would have the value of C appropriate for the sampling
period (e.g., C = 5). Valid Values: 1 < C < 8.
ST Sample Type identifying number (digits 7 and 8). The sample types are as follows:
01	Baseline Questionnaire
02	Descriptive Questionnaire
03	Technician's Questionnaire
04	Followup Questionnaire
05	Activity Diary
(06 not used)
07 Food Checklist
(08-10 not used)

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G03 Identification Numbers for Samples and Forms,	page 3 of 5
Rev. 1.0	October 5, 1995
11	Outdoor Air - Metals
12	(not used)
13	Indoor Air - Metals
14	Indoor Air - Pesticides & PAHs
15	Personal Air
(16-20 not used)
21	Dust - field sample
22	Dust - for Metals
23	Dust - for Pesticides/PAHs
24	Dust - storage reserve
25	Dust - field spikes
(26 not used)
27	Dust extract - metals
28	Dust extract - pesticides
(29-30 not used)
31	Soil - field sample
32	Soil - for Metals
33	Soil - for Pesticides & PAHs
34	Soil - storage reserve
35	Soil - field spikes
36	Soil - dry weight
37	Soil extract - metals
38	Soil extract - pesticides
(39-40 not used)
41	Dermal Wipe - Metals
42	Dermal Wipe - Pesticides & PAHs
(43-44 not used)
45	Tap/Drinking Water-for Metals
46	Tap/Drinking Water - for Pesticides/PAHs
(47-50 not used)
51	Duplicate Diet - solid foods - field sample
52	Duplicate Diet - beverages - field sample
(53-54 not used)
55	Mini-Market Basket - solid foods
56	Mini-Market Basket - beverages
(57-60 not used)
Food daughter samples (division by FDA)
Analyte
Duplicate Diet
Mini-Market Basket
solids
beverages
solids
beverages
metals
5A
5B
5M
5N
pesticides
5C
5D
5P
5Q
PAHs
5E
5F
5R
5S
archive
5G
5H
5T
5U

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Identification Numbers for Samples and Forms,	page 4 of 5
Rev. 1.0	October 5, 1995
61	Urine - day 2 - field sample
62	Urine - day 2 - metals
(63-64 not used)
65 Urine - day 2 - creatinine
(66-70 not used)
71 Urine - day 8 - field sample
(72 not used)
73	Urine - day 8 - pesticides
74	Urine - day 8 - PAHs
75	Urine - day 8 - creatinine
(76-80 not used)
81	Blood - for Metals
82	Blood - for Pesticides
83	Blood - for PAHs
84	Blood - for VOCs
85	Blood serum - pesticides
86	Blood serum - lipids
(87-99 not used)
Valid values for sample type are: 0 < ST < 99. Note that some values are not used but
are left valid to account for protocol modifications.
R Integer used to identify sample if multiple samples are required in the same location.
This value assures that a unique identifier can be assigned to duplicate quality assurance
samples. They will be assigned as follows:
1	primary sample
2	duplicate sample
3	blank
4	other QA sample if needed
Example: 343-1-S-4-15-1
This is the Identification Number for a sample from residence number 343. The target
individual is the first one from this household (1). Residence 343 is in Baltimore
County and is part of the suburban (S) geographic stratum. The sample was taken
during Cycle 4. The sample type is personal air (15) and it is a primary sample (1).
. 1 Preparation for Collection
At the Field Coordination Center (FCC), the FCC Clerk will print ID labels, check that they are
correct, and affix them to logsheets, chain-of-custody forms, etc.
The Field Technicians, Field Interviewer, and Phlebotomist will review all paperwork for
proper ID labels before leaving the FCC.

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G03
Identification Numbers for Samples and Forms,
Rev. 1.0
page 5 of 5
October 5, 1995
6.2	Sampling Location
Field sampling location is the residence, denoted by the HIN code in the Identification Number.
6.3	Sample Collection Procedure
The Field Technicians, Field Interviewer, and Phlebotomist will properly identify all samples
with the appropriate Identification Number.
6.4	Labeling
Printed labels will show the Identification Number in bar-code and human-readable format.
All samples, including questionnaires, environmental samples, and biological samples will be
labeled with the proper Identification Number. Identical labels will be affixed to the logsheet
(3-part carbonless) and the chain-of-custody form corresponding to each sample.
6.5	Preservation and Storage
The collected samples, logsheets, and chain-of-custody forms are the primary storage location
for Identification Numbers. In addition, the Field Coordinator maintains a record of all
Identification Numbers, cross-referenced to the individual respondent at the Field Coordination
Center. An updated list is transmitted electronically on a daily basis to the Principal
Investigator.
6.6	Handling and Shipping
Hardcopy lists relating Identification Numbers and samples are to be transmitted by express
mail once per week from the Field Coordinator's office to the Principal Investigator.
6.7	Laboratory Analysis: Not Applicable
6.8	Data Workup: Discussed above
6.9	Sample Tracking: Discussed above
7	Quality Assurance Procedures
The Field Coordinator or his designate will check sample identification numbers of all samples
when they are brought from the field, and again when they are being packed for shipping.
7.1	Use of Laboratory and Field Blanks: Not Applicable
7.2	Duplicate Sampling: Not Applicable
7.3	Tolerance Limits, Detection Limits, and Sensitivity Limits: Not applicable
8	References
Harvard University/Emory University/Johns Hopkins University Standard Operating Procedures:
G04 Chain-of-Custody and Sample Tracking
G05 Storage and Shipping of Samples

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