United States
Environmental Protection
Agency
           OSWER9200630390
Hearth     	
Summary Tables
Third Quarter
FY- 1990

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                                 DISCLAIMER

    This "report  is  intended   for  internal  U.S.  Environmental  Protection
Agency distribution  only.   The  information  contained herein  has  been  taken
from  final  documents  prepared  by  the Office  of  Health and  Environmental
Assessment for  the  Office  of  Solid  Waste  and Emergency Response. Washington,
DC and  the Office  of  Air  Quality Planning and Standards,  Research Triangle
Park, NC.   These documents were  reviewed in  accordance with  Agency policy
and approved  for  publication.   Mention of trade names or commercial products
does not constitute endorsement or recommendation for use.
 0618h                                ii                                06/13/90

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                              TABLE  OF  CONTENTS

                                                                        Page
INTRODUCTION 	    1

WHAT'S NEW IN THE THIRD QUARTER HEAST	    4

USER'S GUIDE: CHEMICAL TOXICITY	    9

HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE A: SUBCHRONIC AND
CHRONIC TOXICITY (OTHER THAN CARCINOGENICITY)	A-l

HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE B: CARCINOGENICITY	B-l

USER'S GUIDE: RADIONUCLIDE CARCINOGENICITY 	  C-l

HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE C: RADIONUCLIDE
CARCINOGENICITY	C-8

REFERENCES FOR TABLES A	D-l

REFERENCES FOR TABLES B	  D-88
0618h                                111                               07/18/90

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                                 INTRODUCTION

    This  document  Is  the  third  quarter  update  of  the  Health  Effects
Assessment  Summary  Tables (HEAST)  prepared  by  EPA's  Environmental Criteria
and Assessment  Office In Cincinnati,  OH  for use at both  Superfund and RCRA
(Resource  Conservation  and   Recovery  Act)   sites.    Previously,   the  HEAST
contained only  chemicals  commonly found at  Superfund  sites.   Beginning with
this  quarter,  the  document  will also Include  chemicals  commonly  found  at
RCRA  sites as Identified  by  the  Office of  Solid Waste's Technical Assessment
Branch.  By  Including  chemicals  Identified by OSW, the  Agency  will conserve
resources, enhance  the  completeness  of HEAST tables and  assist In promoting
consistency  within  the  Office  Solid  Waste and  Emergency  Response.   Also
acknowledged are  the  contributions  of the Office of Radiation  Programs,  who
provide Table C of the HEAST  on radlonuclldes.
    This update  completely  replaces  the  previous  edition  of  this document.
Chemicals   considered   are   those   for   which  Health   Effects   Assessment
Documents.   Health    and   Environmental   Effects   Profiles,   Health   and
Environmental Effects  Documents,  Health Assessment documents or  A1r Quality
Criteria Documents have been prepared  by  ECAO.   Radlonuclldes considered  are
those  believed  to  be  most  commonly  encountered at  Superfund sites.   This
report  Is  an excellent  "pointer"  system  to  Identify  current  literature  or
changes  In  assessment criteria  for  many  chemicals  of  Interest  to  the
Superfund program.
    It  Is Important to  remember  that the  numbers  In these tables  alone tell
one very  little  about the adverse  effects of a chemical  or the  quality  of
evidence  on  which   toxlclty   criteria   are  based.    Original   assessment
documents must  be consulted by  risk  assessors In order  for them to fully

0618h                               -1-                              07/18/90

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appreciate the  strengths  and  limitations of a  specific  data base.  Original

source documents will allow for  the  most complete characterization of poten-

tial  toxlclty  associated with  the  range  of  exposure  pathways  generally

evaluated at Superfund and RCRA  sites.   The HEAST 1s structured to point the

user to these sources.

    Me recognize that at  any  one time  there may be multiple Agency documents

or  data  bases  that present conflicting  values or assessments  on  a specific

chemical.  For  this reason the following hierarchy of sources Is recommended

In evaluating chemical toxlclty for Superfund sites:

    1. The Agency's Integrated Risk  Information System (IRIS) and  cited
       references.   This  data  base  Is  updated  monthly but may  still
       have  data  gaps.   Call IRIS  USER Support at  513/569-7254 (FTS
       684-7254) for further  Information.

    2. The Health  Effects Assessment Summary  Tables  (HEAST) and  cited
       references.   Limited copies of the  HEAST are  available  for  EPA
       Superfund  staff,   States  Superfund  programs  and  other  Federal
       agencies  working   on   Superfund   sites  and   EPA  contractors
       working  for  the EPA  Superfund program.   If  you fall  Into  one
       of these groups you can call  the  Toxics Integration Branch  (202)
       475-9490 to be  put  on  the mailing  11st.

       EPA's   Office of  Solid Waste (OSM)  requests  that  their  users
       (I.e.  OSM  staff,  contractors, State solid waste programs) call
       Susan  Griffin of the Office of  Solid Maste at (202) 382-6392 to
       obtain copies.   Regional  OSM staff  are reminded  that copies  of
       the HEAST are sent  to  all  Regional libraries.

       Users   of the  HEAST  In  EPA's Office  of  Air  and  Radiation  and
       state  air programs should call  Fred Hauchman  of  EPA's Office  of
       A1r Quality Planning and Standards at (919) 541-5339.

       All others  must purchase the document from:

       National  Technical  Information Service (NTIS)
       5285 Port Royal Road
       Springfield, VA  22161
       (703)  487-4650

       The NTIS order  number   to  receive  all  of the quarters for FY90 Is
       PB-90-921100.  The order  number   to  receive  the  Third  Quarter
       HEAST  only  1s  PB-90-921103.  There  Is  a charge  to  receive this
       from NTIS.

    3. Consultation with EPA   staff (ECAO's  Chemical  Mixtures Assessment
       Branch at 513/569-7300; FTS 684-7300).


0618h                               -2-                               07/18/90

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    4. Do not  consult  either  the  toxlclty tables  (Appendix A)  1n  the
       Superfund  Public   Health  Evaluation  Manual  (SPHEM,  U.S.  EPA,
       1986) or  the September 1988  Public Health Risk  Evaluation  Data
       Base  (PHRED)  as  these sources  are likely  to  contain  numerous
       values that have since become out-of-date.
    Most cited  Agency  references  (e.g.. HEAs.  HEEPs,  HEEDs, etc.),  are  (or
will  soon  be)  available through  the  National Technical  Information  Service
(NTIS).  5285  Port  Royal   Road,   Springfield,   VA  22161  (703/487-4650  or
800/336-4700).   Carcinogen  Assessment  Group  (CAG) Profiles dted  In  Table  B
are available through RCRA  docket  (800/424-9346).

    Questions  regarding the  contents  of  the   HEAST   (e.g.,  chemicals  not
covered, pending  RfDs) should  be directed  to  EPA's  Environmental  Criteria
and Assessment  Office In Cincinnati,  OH at (513)569-7300.
0618h                               -3-                              07/18/90

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                  WHAT'S NEW IN THE THIRD QUARTER FY90 HEAST
GENERIC ISSUES:
    No  changes  In  format have  been  Introduced  In  the  third  quarter  FY90
update of the HEA Summary Tables (HEAST).

    Beginning with  this  quarter  this document  will also  Include chemicals
commonly  found  at  RCRA  sites as  Identified  by  the Office of  Solid  Waste
Technical Assessment  Branch.   (See chemical  specific  Information for Tables
A and B.)

    Please  note  that  the   RfD  Work   Group  has   decided  to  change  the
terminology "Inhalation Reference  Dose"  to  "Reference  concentration (RfC)".
The  Risk Assessment  Council  has  reviewed  and  approved  this  proposal  on
07/02/90.  Next quarter.  HEAST will  be  changed In  order  to reflect  the RfC
terminology.    For  this  quarter.   Inhalation  Reference  Dose  will  remain
reported as such.

    Slope  factors  and  unit  risk  values  for  approximately  40  additional
nuclldes.  Including  radlolsotopes   of   actinium,   blsmlth,   nickel,  protac-
tinium,  neptunium,  radium,  thorium and  others,  have been  added to Table C.
With  the  exception  of minor  word changes,  the text of the  User's Guide for
Section  C  remains  the  same  as presented  In  the  combined  first  and second
Quarterly Update.

    RfD and CRAVE Workgroup  status  reports dated 06/30/90  were used 1n this
update of the Tables.


CHEMICAL-SPECIFIC CHANGES TO TABLE  A:  OTHER THAN CARCINOGENICITY

    The following chemicals are new entries to Table A -(at the request of
    OSW):

         Aldlcarb
         Aluminum phosphide
         Barium cyanide
         Bis  (2-chloro-1sopropyl)  ether
         Calcium cyanide
         Carbon dlsulflde
         Chlorine cyanide
         Chlorobenzllate
         Copper cyanide
         Cyanogen
         Cyanogen bromide
         2,4-D1chlorophenoxy acetic  acid  (2,4-D)
         Dimethyl  phthalate
         D1-n-octyl  phthalate
         Formic acid
         Hydrogen sulflde
         Methanol
         Nitric oxide
         Phenylmercurlc acetate
         Potassium cyanide

0618h                               -4-                              08/01/90

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         Potassium silver cyanide
         Pronamlde
         Selenourea
         Silver
         Silver cyanide
         Strychnine
         1,2.4,5-Tetrachlorobenzene
         Tetraethyl dlthlopyrophosphate
         Tetraethyl lead
         2,4,5-TMchlorophenoxy proplonlc acid (sllvex)
         Z1nc cyanide
         Z1nc phosphide
Aramlte
    A  footnote  was  added to  Indicate  that this chemical  1s  under review by
the oral RfD Workgroup.

Atrazlne
    A  different  study,  also by Clba-Gelgy, Is  now the basis  for the assess-
ment of  oral  toxlclty.  The  chronic oral  RfD did not  change,  but the foot-
note was changed to Indicate that the RfD Is verified and available on IRIS.

Barium
    The footnote was changed  to  Indicate  that a new oral RfD was verified on
06/21/90 and IRIS will be changed.

Boron
    The  footnote was   changed  to  Indicate  that  the  chronic  oral  RfD  Is
verified and available on IRIS.

Bromomethane
    The chronic  Inhalation  RfD Incorrectly  appeared  as 6E-2;  It has now been
corrected to 6E-3.  The chronic oral RfD  has  been  corrected to 1.4E-3, which
Is  how  It  appears  on IRIS.   The  subchronlc  oral   RfD  has  been  modified
accordingly.

Chloroacetaldehvde
    A footnote has been added  to  Indicate  that this  chemical's assessment of
oral toxlclty Is currently not under discussion.

Chlorodlbromomethane
    This  chemical  1s  also  listed  In  a  separate  entry  as  dlbromochloro-
methane;  therefore,  Chlorodlbromomethane and  corresponding  references  have
been removed.   IRIS lists  this chemical  as dlbromochloromethane.

1.2-c-D1ch1oroethvlene
    Oral RfD values  are now available  for  this chemical.  The chronic  oral
RfD derived  by  the Workgroup  has been  verified  and  Is pending  Input  Into
IRIS.
0618h                               -5-                              07/18/90

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2.4-D1methy1pheno1
    Oral  RfD values are  now available  for  this chemical.  The chronic oral
RfD  derived  by  the  Workgroup has been   verified and  1s  pending Input Into
IRIS.

4.6-D1n1tro-o-cresol
    A  footnote  has  been  added  to Indicate  that this  chemical Is currently
not under discussion.

2.4-D1n1tropheno1
    Oral  RfD values  are  now  available for this  chemical.   The chronic oral
RfD derived  by the Workgroup has been verified and Is available on IRIS.

Dlsulfoton
    This chemical 1s a new entry from a recently finalized HEED.

Fluoranthene
    This chemical was erroneously  listed  as  fluoroethene;  the  error has been
corrected.

n-Hexane
    Data  regarding  Inhalation has been  changed  since  a new   Inhalation RfD
has  been verified  based  on a  human  epldemlologlcal  study.   The  chronic
Inhalation RfD Is pending Input Into IRIS.

Manganese
    A  footnote was  added  to Indicate that this  chemical's  oral risk assess-
ment 1s under review by the Workgroup.

Mercury. Inorganic
    Data  regarding  Inhalation has been  changed  since  a new   Inhalation RfD
has  been verified   based on  several  occupational    studies.   The  chronic
Inhalation RfD 1s pending Input Into IRIS.

Methoxychlor
    A  footnote was  added to  Indicate  that this chemical  1s  under review by
the oral RfD Workgroup.

Methyl bromide
    This entry and  the  corresponding references have been  deleted since the
chemical  Is   already listed  under  bromomethane,  which  1s   the name  that
appears on IRIS.

Methyl ethyl  ketone
    A  footnote was added  to Indicate that this  chemical's  chronic oral RfD,
while  still   available on  IRIS,  Is being  reconsidered  by the Workgroup.  The
Inhalation RfD has recently been verified, pending Input Into  IRIS.

Nickel
    A footnote was  added  to Indicate that this  chemical's  chronic oral RfD,
while still available on IRIS.  Is being reconsidered by the Workgroup.
0618h                               -6-                              07/18/90

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Nitrobenzene
    A  footnote was added  to  Indicate that although  the chronic oral RfD  1s
being  reconsidered by  the  Workgroup It  Is  stm  available  on  IRIS.   The
expression  of  the  Inhalation  RfD as a dose 1n terms  of  mg/kg/day was  removed
to reflect  derivation by the newer  Interim methodology.

Nitrogen dioxide
    This  chemical  1s  a   new  entry  from a  recently  finalized  HEED.   The
Inhalation  RfD  Is  under  review by the RfD Workgroup.  The  oral  RfD. which  1s
an  RfD for nitrogen  dloxIde-N  derived by analogy  to nltrate-N, 1s verified
and available on IRIS.

Phosphlne
    A  footnote  was added  to  Indicate that the  chronic  oral RfD 1s verified
and Is available on IRIS.

Propylene glycol monomethyl ether
    A  recent  Inhalation  assessment verified a chronic  RfD of 7E-1 using the
new methodology.   This  RfD Is  pending  Input  Into  IRIS.   The new relevant
Information was added to this entry.

Selenium
    The  footnote  was  changed  to  Indicate  that  the oral  RfD for selenium  Is
verified but not yet available on IRIS.

Styrene
    A  footnote  was  added  to Indicate  that  the  chronic  oral RfD, while still
available on IRIS, 1s being reconsidered by the Workgroup.

Toluene
    The footnote for  the chronic  oral  RfD  was  changed to  Indicate that a new
value was verified on 06/20/90 and IRIS will be changed.

1.1.1-Trlchloroethane
    A  footnote  was  added  to Indicate  that the  chronic  oral RfD, while still
available on IRIS, Is being reconsidered by the Workgroup.


CHEMICAL-SPECIFIC CHANGES TO TABLE B:  CARCINOGENICITY

    The following chemicals are new entries to Table  B (at  the request of
    OSW):

         ODD
         DDE
         1,2-D1bromo-3-chloropropane
         Dlethylstllesterol
         7,12-D1methylbenz(a)antracene
         1,4-D1oxane
         Heptachlor epoxlde
         3-Methylcholanthracene
         N-nltrospyrrolldlne
         1,1,1,2-Tetrachloroethane
0618h                               -7-                              08/01/90

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Benzotrlchlorlde
    The footnotes were changed  to  Indicate that  the  classification  and oral
slope  factor  have both been  verified.   The  quantitative risk  estimate  for
Inhalation route Is currently under review.

Decabromodlphenyl oxide
    The footnote was  changed  to Indicate that  the  Group C classification Is
verified and 1s available  on IRIS.

1,3-D1ch1oropropene
    A  footnote  was  added  to  Indicate  that  quantitative   risk  estimates,
derived since the EPA Group was  verified, have not been verified.

Direct Black 38
    A  footnote was  added  to  Indicate   that  this  chemical's assessment  Is
under review by CRAVE Workgroup.

Direct Blue 6
    A  footnote was  added  to  Indicate   that  this  chemical's assessment  1s
under review by CRAVE Workgroup.

Direct Brown 95
    A  footnote was  added  to  Indicate   that  this  chemical's assessment  1s
under review by CRAVE Workgroup.

Formaldehyde
    A footnote was added  to  Indicate  that  this  oral slope factor, calculated
In a CAG profile, has not  been reviewed  by the CRAVE Workgroup.

Methyl Ethyl Ketone
    The footnote was  changed  to Indicate that  the  Group D classification 1s
verified and Is available  on IRIS.

Selenium' SulfIde
    A  footnote was  added  to  Indicate   that  this  chemical's assessment  1s
verified; Input Into IRIS  Is pending.

Styrene
    The footnote was  changed  to Indicate that  this chemical's assessment Is
now under review by CRAVE.

2.4.6-Tr1ch1oropheno1
    The  footnote was  changed  to  Indicate that  oral  and  Inhalation  slope
factors are available on  IRIS.

Vinyl chloride
    The  footnote was  changed  to  Indicate that  oral  and  Inhalation  slope
factors have been verified, but  Input  Into IRIS Is pending.
0618h                               -8-                              07/18/90

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                       USER'S GUIDE:  CHEMICAL TOXICITY
    The  Health  Effects  Assessment Summary  Tables  A &  B  summarize reference
doses  (RfDs)  for toxlclty  from subchronlc and  chronic  Inhalation  and oral
exposure  (Table  A)  and  slope  factors and  unit  risk  values  for carclnogen-
Iclty  based on  lifetime  Inhalation  and  oral  exposure  (Table B).   A more
complete  discussion of  how Superfund  develops  and  considers  the  toxlclty
assessment  In  hazardous  waste  sites  Is  presented   In  Chapter  7  of  Risk
Assessment  Guidance for  Superfund:  Human  Health  Evaluation Manual  Part  A.
The chemicals  Included  In the  tables are  the  subjects of final documents of
Health Effects Assessment  documents  (HEAs), Health and Environmental Effects
Profiles  (HEEPs), Health  and Environmental  Effects Documents (HEEDs). Health
Assessment  Documents (HADs) and Air  Quality Criteria  Documents (AQCDs).  The
Information In HEA  Summary  Tables A  and  B Is  excerpted from the HEAs, HEEPs,
HEEDs,  HADs  and AQCDs,  and   expanded   and  updated  quarterly  to  Include
chemicals addressed In  HEAs, HEEDs,  HADs and AQCDs that  have been finalized
since the last update and  to bring  existing values Into conformity with more
recent EPA  assessments,  especially  RfD   or CRAVE  Work Group  verifications.
The  references  listed  for  each  chemical  In   the   Reference  column  and
References  section  represent  not  only  the study  or  studies  that are  the
basis  for  the   RfD,  slope  factor   or   unit  risk,  but  also  the  U.S.  EPA
reference  that   Is  the  source of  the   Agency  analysis  or  risk  assessment
values and  the  IRIS citation  for  values verified by  the RfD  or  CRAVE  work
group.  Verified values are Indicated 1n  the tables by a footnote.
0618h                               -9-                              07/18/90

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    The following documents cited 1n  this  section  may be obtained from their
respective sources:

     From the Center for Environmental Research Information (513)569-7562.
              Risk Assessment Guidance: Volume 1, Human Health Evaluation
              Manual. Part A.  EPA/540/1-89/002.
              A1r Quality Criteria Documents.
     From the National Technical Information Service (NTIS) (703)487-4780.  .
              Interim Methods for Development  of Inhalation
              Reference Doses.  EPA/600/8-88/006F.
              Order number PB90-145723.  The price  Is $31.00.

Table A; Subchronlc and Chronic ToxIcUv (other than Carclnogenlclty)
    The RfD  1s  an  estimate  (with uncertainty  spanning perhaps an  order of
magnitude)  of  the  dally  exposure   to   the  human  population  (Including
sensitive  subgroups)  that 1s  likely  to  be without  an appreciable  risk of
deleterious  effects  during  a portion  of  the  lifetime.  In  the  case of  a
subchronlc RfD  (designated  "RfDs" In  Table A  and formerly called  AIS), or
during the lifetime. In the case  of  a  chronic RfD  (designated "RfD" In Table
A and  formerly  called  AIC).   The RfD  values are  listed  In Table  A  1n  the
column under "Reference Dose."  The RfD  Is  derived by dividing the NOAEL (or
LOAEL  If   a  suitable  NOAEL   1s   not  available)  for  subchronlc  or  chronic
exposure by an uncertainty factor (UF) times a modifying factor (MF):
                             RfD = NOAEL or LOAEL
                                      UF x MF

In Table A, the NOAEL or  LOAEL  that  Is the basis for the RfD value Is listed
under  "Exposure."   When a NOAEL  or  LOAEL  Is  reported In terms  of  exposure
concentration and schedule,  the calculated mg/kg/day  dose  Is  given  In paren-
theses.  The  species In  which  the  NOAEL or  LOAEL was  determined and  the
0618h                               -10-                             07/24/90

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effect  of  concern are  also described,  and  the  reference  for  the  study 1s
presented.   The  effect  of  concern   listed   1s   that  associated  with  the
chemical  and  not  with  the  dose  listed.   In  the  "Exposure,"  "Effect  of
Concern"  and "Reference"  columns.  Information for  the  Inhalation  route Is
given first, separated from Information  for  the oral  route by a semicolon or
slash.
    The  uncertainty  factor used  In  calculating  the  RfD  reflects  scientific
judgment  regarding  the various  types  of data  used  to estimate RfD values.
An  uncertainty  factor of  10 Is  usually used to  account for  variations In
human  sensitivity  when  extrapolating   from  valid human studies  Involving
subchronlc  (for  RfD  ) or  long-term (for RfD)  exposure  of  average,  healthy
subjects.   An  additional  10-fold  factor  Is  usually used  for  each  of  the'
following  extrapolations:    from  long-term  animal studies  to  the  case  of
humans,  from a  LOAEL to a NOAEL, and from  subchronlc studies  to  a chronic
RfD.   In  order  to reflect professional  assessment  of the  uncertainties of
the  study  and  data  base  not explicitly addressed by  the  above uncertainty
factors  (e.g.. completeness  of  the  overall  data base), an  additional uncer-
tainty  factor  or  modifying factor  ranging  from  greater  than  0  to less than
or equal to 10 Is applied.   The default value for  this modifying factor 1s 1.
    A subchronlc RfD  1s usually derived,  If  not previously derived In health
effects documents  that  originally addressed the chemical,  for chemicals  for
which a  chronic  RfD  Is  presented In Table A.  The subchronlc  RfD  Is derived
In either  of two ways.  If  an  uncertainty  factor  to expand from  subchronlc
to  chronic  exposure  was   used  In  the  derivation  of  the  chronic  RfD,  the
subchronlc RfD  Is  derived   from the  same benchmark dose  without application
of the  uncertainty factor  to  expand from  subchronlc to  chronic  exposure.
0618h                               -11-                             07/18/90

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If,  however,  the  chronic  RfD  was  derived without  use  of an  uncertainty
factor  to  expand  from  subchronlc to  chronic  exposure,  the chronic  RfD  Is
adopted as the subchronlc RfD.
    Table A  lists the  uncertainty factor  and modifying  factor,  multiplied
together to  form a single  factor, under  the  heading  "Uncertainty Factor."
For example,  the uncertainty factor  of  500 listed for the  chronic  oral  RfD
for cyanide reflects an  uncertainty  factor of 100 and  a  modifying factor  of
5;  the  uncertainty factor  of  100  listed  for  the subchronlc  oral  RfD  for
bromomethane reflects an uncertainty factor of 100 and  a  modifying factor  of
1.
    RfD  values  are specific for  the  route of exposure  for which  they  are
listed on Table  A.  In the  few Instances  where an oral  RfD has been extrapo-
lated from Inhalation data,  the extrapolation  1s  Indicated by footnoting  the
value.
    The  Interim  methods  for the  derivation of Inhalation RfDs  were adopted
by the Agency In  1988.   These methods  are different  from those used for oral
RfDs because of  (1) the  dynamics  of  the  respiratory  system and Us diversity
across  species,  and  (2) differences  In  the  physlcochemlcal properties  of
contaminants  (such as  the  size  and  shape  of   a  particle  or  whether  the
contaminant  1s   an aerosol or   a  gas).   Parameters  such  as  deposition,
clearance mechanisms and the physlcochemlcal properties  of the Inhaled agent
are considered  In the  determination of  the effective dose  delivered to  the
target  organ.    Additional  Information concerning  this  methodology  can  be
found  In "Interim Methods   for  Development of  Inhalation  Reference Doses"
(U.S.  EPA.  1989.  EPA/600/8-88/066F).   An  RfD value  calculated  using  this
Interim  methodology  Is  generally  reported  as  a   concentration  In  air
0618h                               -12-                             07/18/90

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     3
(mg/m ),  although  It  may  be  converted  to  a  corresponding   Inhaled  dose
(mg/kg/day) by  dividing  by 70  kg  (an assumed  human  body  weight)  and multl-
              3
plying by 20 m /day (an assumed human Inhalation rate).
    Inhalation  RfD  values  reported  1n  HEAs  and   early  HEEDs  that  were
finalized prior to  the Implementation  of the Interim methods were calculated
using methods similar In concept to  those used for oral RfDs. and the values
are  reported  both  as  a  concentration  In air  (In mg/m  for  continuous,  24
hours/day exposure) and as a corresponding Inhaled dose (1n mg/kg/day).
    RfD  values  for oral  exposure  are  reported  as  mg/kg/day.   An  oral  RfD
value can  be  converted to  a  corresponding concentration  1n  drinking water,
assuming human  body weight  of  70  kg  and water  consumption  of 2  I/day,  as
follows:
               mg/8. 1n water = oral RfD (In mg/kq/day) x 70 kg
                                          2 i/day

    The  RfD  1s  used as a  reference  point for  gauging  the  potential effects
of other doses.  Usually, doses that  are less  than the RfD are not likely to
be associated  with health  risks.   As the  frequency of  exposures  exceeding
the RfD  Increases  and as  the  size of the excess  Increases,  the probability
Increases that adverse health effects may  be observed In a human population.
Nonetheless, a  clear  distinction  that would  categorize all  doses  below  the
RfD  as   "acceptable"  (risk-free)   and all  doses  1n  excess  of  the  RfD  as
"unacceptable"  (causing adverse effects)  cannot  be  made.  In  addition,  RfD
values,   and particularly  those  with  limitations  In  the quality or  quantity
of supporting data, are subject to change as  additional  Information becomes
available.
    When RfD values are listed  for chemicals  that are carcinogens,  the entry
under "Effect  of   Concern"  In  Table  A  will  11st cancer  and will  refer  to
0618h                               -13-                             07/18/90

-------
Table B  If additional  Information concerning  carclnogenlclty Is available In
that table.  RfD  values  that  have been derived  for  carcinogens are based on
noncancer endpolnts only and  should  not be assumed  to  be protective against
carclnogenlclty.
Table B; Carclnogenlclty
    In assessing  the  carcinogenic potential  of a chemical,  the Human Health
Assessment Group  (HHAG)  of  the  U.S.  EPA classifies  the  chemical  Into one of
the following groups,  according  to  the weight of evidence  from epldemlolog-
Ical studies and animal studies:
    Group A -  Human Carcinogen  (sufficient evidence of  carclnogenlclty
               In humans)
    Group B -  Probable  Human Carcinogen  (Bl  -  limited  evidence  of
               carclnogenlclty In  humans;  82  -  sufficient  evidence  of
               carclnogenlclty In  animals with  Inadequate  or lack  of
               evidence In  humans)
    Group C -  Possible Human Carcinogen  (limited  evidence  of  carclno-
               genlclty In  animals and Inadequate or  lack of human data)
    Group D -  Not Classifiable as to Human Carclnogenlclty  (Inadequate
               or no evidence)
    Group E -  Evidence of  NoncardnogenlcUy for  Humans  (no  evidence
               of carclnogenlclty 1n  adequate  studies).
These classifications  are shown  under "EPA Group" on  Table B.
    Quantitative  carcinogenic  risk  assessments  are  performed  for  chemicals
In  Groups  A and  B,  and on a case-by-case basis for  chemicals  In  Group C.
Cancer slope factors  (formerly  called cancer  potency  factors  In  the Super-
fund  Public  Health  Evaluation   Manual)  are  estimated  through  the  use  of
mathematical extrapolation  models,  most  commonly  the linearized  multistage
model,  for  estimating  the  largest  possible   linear  slope  (within  the  95%
0618h                               -14-                             07/18/90

-------
confidence  limit)  at  low  extrapolated  doses  that  Is  consistent  with  the
data.  The  slope factor or  risk  Is  characterized as an upper-bound estimate,
I.e.,  the   true  risk  to  humans,  while  not  Identifiable,  Is  not  likely to
exceed the  upper-bound estimate and In fact may be lower.
    Quantitative  carcinogenic  estimates  listed  1n  Table  B  Include  the
following:
       slope factor  = risk per unit dose = risk per mg/kg/day
       route-specific unit  risk  for  Inhalation  exposure =  risk  per
       concentration unit In air = risk per yg/m3
Unit  risk  estimates for  Inhalation  and oral  exposure can  be  calculated by
dividing  the  appropriate  slope  factor  by   70  kg  and  multiplying by  the
                        3
Inhalation  rate  (20 m /day)   or   the   water  consumption   rate   (2  a/day),
respectively,  for  risk  associated with  unit  concentration  In air or water.
Hence,
    risk per yg/m3 (air) =
    slope factor (risk per mg/kg/day)  x   1   x 20 m3/day x 10~3 (mg/yg)
                                        70 kg
    risk per yg/s. (water)  =
    slope factor (risk per mg/kg/day)  x   1   x 2 I/day x 10~3 (mg/yg)
                                        70 kg
Quantitative  estimates  of  carcinogenic  risk are  listed  under  "Unit  Risk
[slope factor]"  In  Table  B.  Information on  the  study  and  data  set used  for
estimation of  the slope factor  Is given  In the other  columns of Table B.   In
the "Exposure" and  "Reference" columns,  Information for  the Inhalation  route
Is given first, separated from  Information for  the  oral  route by a semicolon
or slash.
    Quantitative  carcinogenic   estimates  are  specific  for  the  route   of
exposure for which  they are listed  on Table  B.   Footnotes  are  used In  Table
B  to  Indicate those  Instances  In which  the values  for  Inhalation  or  oral
exposure are based  on extrapolation  from another  route of exposure.

0618h                               -15-                             07/18/90

-------
    To estimate  risk-specific  concentrations  In  air from  the unit  risk  In
air as presented  In Table B, the  specified  level  of risk  Is  divided by the
                                                             3
unit  risk  for air.   Hence  the  air concentration  (In yg/m )  corresponding
to  an upper-bound  Increased  lifetime  cancer  risk  of  1x10    Is  calculated
as follows:
                     In air =         1x10
                              _
                              unit risk In (yg/mj)-'

    To estimate risk-specific concentrations In drinking  water  from the oral
slope  factor  values presented  In Table  B.  the specified  level  of risk  Is
multiplied  by  70  kg  and  divided  by the  slope  factor  and  by  2  a/day.
Hence,  the  water  concentration  corresponding  to  an  upper-bound  Increased
lifetime cancer risk of 1x10"  Is  calculated  as  follows:
               mg/i 1n  water = _ Ix10~5x70  kg   _
                               slope factor  In  (mg/kg/day)-' x 2 I/day
0618h                               -16-                              07/18/90

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MLMLIII LI i LIU
                                                   Nib  MJWMKI  (HULL  A.  bUdlHKUNK ANU LHKUN1L IUX1UIT (UIHLK  I HAN IAKI INUbtNKll T )
                                                                      Update:   Ji-     1990
Compound
Acenaphthene
subchronlc (RfDs)

chronic (RfO)

Acenaphthylene
Acephate
subchronlc (RfOs)
* S *



chronic (RfO)




Acetone
subchronlc (RfOs)



chronic (RFD)



Acetone cyanohydrln
subchronlc (RfDs)




Exposure
Inhalation; Oral
NA; 175 mg/kg/day by
gavage for 90 days
NA; 175 mg/kg/day by
gavage for 90 days


NA; 2 ppm In the diet
for 13 weeks (0.135
mg/kg/day)


NA; 2 ppm In the diet
for 13 weeks (0.135
mg/kg/day)



NA; 100 mg/kg/day
for 90 days by
gavage

NA; 100 mg/kg/day
for 90 days by
gavage

10.1 ppm (35.2 mg/ffl3)
6 hours/day, 5 days/week
for 14 weeks (4.0 mg/kg/
day); 10.8 mg CN/kg/day
for 104 weeks from diet
treated with HCN
Species Effect of Concern Reference Dose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
NA mouse NA; hepatotoxlclty ND 6E-1 NA 300

NA . mouse NA; hepatotoxlclty ND 6E-2J NA 3000

DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT

NA rat NA; Inhibition ND 4E-3 NA 30
of brain AChase



NA rat NA; Inhibition ND 4E-3a NA 30
of brain AChase
(also see Table B)



NA rat NA; Increased ND NA NA 100
liver and kidney
weight, nephro-
toxlclty
NA rat NA; Increased ND lE-l**1 NA 1000
liver and kidney
weight, nephro-
toxldty
rat rat CNS signs; body 1E-1 (4E-2) 7E-2" 100 500
weight, thyroid and
CNS effects



Reference
Inhalation/Oral
U.S. EPA, 1989

U.S. EPA, 1989

U.S. EPA. 1987

U.S. EPA, 1990/
Chevron Chem.
Co.. 1989;
U.S. EPA, 1984,
1990
U.S. EPA. 1987/
Chevron Chem.
Co.. 1989;
U.S. EPA, 1984,
19B9

U.S. EPA, 1988/
U.S. EPA. 1986,
1988, 1990

U.S. EPA. 1988/
U.S. EPA, 1986.
1988, 1990

Blank and Thake,
1984; U.S. EPA,
1988/Howard and
Hanzal, 1955;
U.S. EPA,
1985a.b. 1988
0059h
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                                                                      Update:
                                                             1990
      Compound
                              Exposure
  Inhalation; Oral
                              Species
Inhalation  Oral
Effect of Concern
Inhalation; Oral
                                                Reference  Dose
    Inhalation
[mg/m3 (nig/kg/day)]
   Oral
(mg/kg/day)
Uncertainty Factor
Inhalation    Oral
   Reference
Inhalation/Oral
  chronic (RfD)
Acetonltrlle
10.1 ppm (35.2 mg/m3)
6 hours/day, 5 days/week
foi  14 weeks (4.0 ing/kg/
day); 10.8 mg CN/kg/day
for  104 weeks from diet
treated with HCN
 rat         rat       CMS  signs;  body
                     weight,  thyroid and
                     CNS  effects
                        1E-1  (4E-2)        7E-2"        100       500    Blank and Thake,
                                                                        1984; U.S. EPA.
                                                                        1988/Howard and
                                                                        Hanzal. 1955;
                                                                        U.S.  EPA.
                                                                        19B5a,b.  1988
subchronlc (RfDs)




chronic (RfD)






Acetophenone
subchrontc (RfDs)






chronic (RfD)






Acroleln
subchronlc (RfDs)




100 ppm (168 mg/m3) mouse
6 hours/day. 65/92
days (39.0 mg/kg/day);
100 ppm (168 mg/m3)
6 hours/day. 65/92 days
(19.3 mg/kg/day)
100 ppm (168 mg/m3) mouse
6 hours/day. 65/92 days
(39.0 mg/kg/day); 100
ppm (168 mg/m3) 6
hours/day. 65/92 days
(19.3 mg/kg/day)


0.007 mg/m3 contln- rat
uously for 70 days
(0.0045 mg/kg/day);
10.000 ppm diet (8450
ppm. correcting for
volatilization) for 17
weeks (423 mg/kg/day)
0.007 mg/m3 contln- rat
uously for 70 days
(0.0045 mg/kg/day);
10.000 ppm diet (8450
ppm, correcting for
volatilization) for 17
weeks (423 mg/kg/day)

0.4 ppm, 6 hours/day, rat
5 days/week for 62 days;
NA


mouse elevated relative 5E-1 (1E-1)
liver weight;
elevated relative
liver weight


mouse decreased RBC 5E-2 (1E-2)
counts and hemato-
crlt and hepatic
lesions; decreased
RBC counts and
hematocrlt and
hepatic lesions

rat congestion of 2E-4(5E-5)
cardiac vessels
and liver dys-
trophy, reduced
albumin/globulin
ratio; none
observed
rat congestion of 2E-5(5£-6)
cardiac vessels
and liver dys-
trophy, reduced
albumin/globulin
ratio; none
observed

NA pulmonary function 1E-3
and lung composi-
tion; NA


6E-2 300 300 Coate. 1983;
U.S. EPA. 1987/
Coate. 1983;
U.S. EPA, 1987.
1990

6E-3b>z 3000 3000 Coate, 1983;
U.S. EPA, 1987/
Coate. 1983;
U.S. EPA,
1987, 1990



1E*0 100 300 Imasheva. 1966;
U.S. EPA. 1987/
Hagan et al.,
1967; U.S. EPA.
1990


lE-la 1000 3000 Imasheva. 1966;
U.S. EPA. 1987/
Hagan et al..
1967; U.S. EPA,
1990



ND 300 NA Costa et al..
1986; Kutzman,
1981. 1985;
U.S. EPA. 1987/
U.S. EPA. 1987
0059h
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                            mm 111 LIIILIO
                                                       junrmKi IHOU M. bUbLHKUNIL ANU IHKUN1L  lUXKHf  (UIHtK  I HAN  lAKUNObtNIU I Y)
                                                                       Update:      \  1990
Compound
chronic (RfD)
Acrylamlde
subchronlc (RfOs)
chronk (RfD)
Acrylic acid
subchronlc (RfOs)
chronic (RfD)
Adlponltrlle
Alachlor
subchronlc (RfOs)
chronic (RfD)
Exposure
Inhalation; Oral
0.4 ppm, 6 hours/day.
5 days/week for 62 days;
NA
NA; 0.2 mg/kg/day In the
drinking water for 90
days
NA; 0.2 mg/kg/day In the
drinking water for 90
days
NA; 83 mg/kg/day In the
water for 3 months
NA; 83 mg/kg/day In the
water for 3 months

NA; 1 mg/kg/day by
gavage for 1 year
NA; 1 mg/kg/day by
gavage for 1 year
Species Effect of Concern Reference Dose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation • Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
rat NA pulmonary function 1E-4J ND 3000 NA
and lung composi-
tion; NA (also see
Table B)
NA rat NA; nerve damage ND 2E-3 NA 100
NA rat NA; nerve damage NO 2E-4* NA 1000
(also see
Table B)
NA rat NA; reduced ND 8E-1 NA 100
body weight,
altered organ
weights
NA rat NA; reduced ND 8E-2a NA 1000
body weight,
altered organ
weights
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA dog NA; hemolytlc ND 1E-2 NA 100
anemia, hemo-
slderosls
(also see Table B)
NA dog NA; hemolytlc ND 1E-23 NA 100
anemia, hemo-
slderosls
Reference
Inhalation/Oral
Costa et al..
1986; Kutzman,
1981, 1985;
U.S. EPA, 1987,
1989/U.S. EPA.
1987
U.S. EPA. 1990/
Burek et al.,
1980; U.S. EPA.
1985; U.S. EPA.
1990
U.S. EPA, 1990/
Burek et al.,
1980; U.S. EPA,
1985; U.S. EPA,
1990
U.S. EPA, 1984/
OePass et al..
U.S. EPA, 1984.
1990
U.S. EPA. 1984/
DePass et al..
U.S. EPA. 1984,
1990
U.S. EPA, 1987
U.S. EPA. 1990/
Honsanto
Company. 1984;
U.S. EPA, 1984;
U.S. EPA, 1990
U.S. EPA. 1990/
Honsanto
Company, 1984;
U.S. EPA, 1984;
U.S. EPA. 1990
0059h
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Update: . 1990
Compound
Aldlcarb
subchronlc (RfOs)
chronic (RfO)
Aldrln
subchrontc (RfDs)
chronic (RfD)
Allldochlor
Ally! alcohol
subchronlc (RfDs)
chronic (RfD)
Exposure
Inhalation; Oral
NA; 0.25 mg/kg/day of
aldkaib suUoxide In
diet for 3-6 months
NA; 0.25 mg/kg/day of
aldlcarb sulfoxlde In
diet for 3-6 months
NA; 0.5 ppm In diet
for 2 years (0.025
mg/kg/day)
NA; 0.5 ppm In diet
for 2 years (0.025
mg/kg/day)

NA; 50 ppm In the
drinking water for 15
weeks (4.8 mg/kg/day)
NA; 50 ppm In the
drinking water for 15
weeks (4.8 mg/kg/day)
Allyl chloride (3-chloropropene)
subchronlc (RfOs) occupational; NA
chronic (RfD)
occupational; NA
Species Effect of Concern Reference Dose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
NA rat NA; chollnesterase ND 1.3E-3 NA 100
Inhibition
NA rat NA; chollnesterase ND 1.3E-3* NA 100
Inhibition
NA rat NA; liver lesions ND 3E-5 NA 1000
NA rat NA; liver lesions ND 3E-5* NA 1000
(also see Table
B)
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA rat NA; liver and ND 5E-2 NA 100
kidney
NA rat NA; liver and ND 5E-3a NA 1000
kidney
human NA liver; NA ND 2E-3b NA 100
human NA liver; NA ND 2E-3b NA 100
(also see
Table B)
Reference
Inhalation/Oral
NA/Uell and
Carpenter, 1968;
U.S. EPA. 1990
NA/Uell and
Carpenter, 1968;
U.S. EPA. 1990
NA/Fltzhugh.
el al., 1964;
U.S. EPA, 1990,
1987
NA/Fltzhugh
et al.. 1964;
U.S. EPA, 1990,
1987
U.S. EPA. 1984
U.S. EPA, 1985.
1990/ Carpamlnl
et al.. 1978;
U.S. EPA. 1985,
1990
U.S. EPA. 1985.
1990/ Carpamlnl
et al., 1978;
U.S. EPA, 1985.
1990
U.S. EPA, 1983/
ACGIH, 1980;
U.S. EPA. 1983
U.S. EPA. 1983/
ACGIH, 1980;
U.S. EPA, 1983
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. i j ouiirinni  1(10(1  tt  iUULMKUNlL  ANU LMKUNIL IUA1L1II (UIMLK  I HAN  LAKL INUbtNR 1 11)
                    Update:      \  1990
Compound
Aluminum
Aluminum phosphide
subchronlc (RfOs)
chronic (RfD)
Ametryn
subchronlc (RfDs)
chronic (RfD)
Exposure
Species Effect of Concern Reference Dose Uncertainty Factor
Inhalation; Oral Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)

NA; 0.51 mg phosphlne/kg NA
fumigated chow for 2
years (0.25 mg phosphlne/
kg/day) (0.043 mg
aluminum phosphlne/kg/day)
NA; 0.51 mg phosphlne/kg NA
fumigated chow for 2
years (0.25 mg phosphlne/
kg/day) (0.043 mg
aluminum phosphlne/kg/day)
NA; 10 mg/kg/day. 6 NA
days/week for 13 weeks
by gavage
NA; 10 mg/kg/day. 6 NA
days/week for 13 weeks
by gavage
l-Amlno-2-naphtol and
l-Amlno-2-naphtol hydrochlorlde
m-Amlnophenol
subchronlc (RfDs)
chronic (RfO)
o-Amlnophenol
p-Amlnophenol
4-Amlnopyrldlne
subchronlc (RfDs)
nncok
NA; 1300 ppm In the NA
diet for 13 weeks (65
mg/kg/day)
NA; 1300 ppm In the NA
diet for 13 weeks (65
mg/kg/day)


NA; 3 ppm In diet NA
for 90 days (0.15
mg/kg/day)
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
rat NA; body weight and NA 4E-4 NA 100
clinical parameters
rat NA; body weight and NA 4E-4a NA 100
clinical parameters
rat NA; liver NO 9E-2 NA 100
rat NA; liver NO 9E-3a NA 1000
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
rat NA; thyroid and NO 7E-1 NA 100
body weight
rat NA; thyroid and NO 7E-2 NA 1000
body weight
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
rat NA; Increased liver ND 2E-4 NA 1000
(males) and brain
weight (females)
Reference
Inhalation/Oral
U.S. EPA. 1987
NA/Hackenburg
1972; U.S. EPA,
1990
NA/Hackenburg
1972; U.S. EPA,
1990
U.S. EPA, 1990/
Clba-Gelgy,
1961; U.S. EPA.
1984, 1990
U.S. EPA, 1990/
Clba-Gelgy.
1961; U.S. EPA.
1984. 1990
U.S. EPA, 1986
NA/Re et al..
1984; U.S. EPA.
1985
NA/Re et al.,
1984; U.S. EPA,
1985
U.S. EPA, 1985
U.S. EPA, 1985
U.S. EPA, 1989/
Kohn. 1968; U.S.
EPA. 1980. 1989
                                                                                                  07/12/90

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Compound
chronic (RfD)
Ammonia
subchronk (RfDs)
chronic (RfD)

Exposure
Inhalation; Oral
NA; 3 ppm In diet
for 90 days (0.15
mg/kg/day)
0.36 mg/m3 continuous;
9934 mg/l 1n drinking
water
0.36 mg/m3 continuous;
34 mg/l 1n drinking
water
Update: * 1990
Species Effect of Concern Reference
Inhalation Oral Inhalation; Oral Inhalation
[mg/m3 (mg/kg/day)]
NA rat NA; Increased liver ND
(males) and brain
weight (females)
human human odor threshold; 0.36C
taste threshold
human human odor threshold; 0.36C>9
taste threshold

Dose Uncertainty Factor
Oral Inhalation Oral
(mg/kg/day)
2E-59 NA 10,000
34 mg/l none none
In drinking
water d
34 mg/l none none
In drinking
waterd

Reference
Inhalation/Oral
U.S. EPA, 19B9/
Kohn. 1966; U.S.
EPA, 1980, 1989
Carson et al.,
1981; U.S. EPA,
1987/Campbell
et al., 1958;
U.S. EPA. 1981,
1987; WHO. 1986
Carson et al.,
1981; U.S. EPA.
1987/Campbell
et al., 1958;
U.S. EPA. 1981.
1987; WHO, 1986
Anthracene
  subchronk (RfDs|
  chronic (RfDs
Antimony
  subchronk (RfDs)
  chronic (RfD)
Antimony pentoxide
  subchronk (RfDs)
NA; 1000 mg/kg/day        NA
by gavage for 90 days

NA; 1000 mg/kg/day        NA
by gavage for 90 days
NA; 5 ppm Sb from         NA
antimony potassium
tartrate In drinking
water, lifetime
(0.35 mg Sb/kg/day)

NA; 5 ppm Sb from         NA
antimony potassium
tartrate In drinking
water, lifetime
(0.35 mg Sb/kg/day)
NA; 5 ppm Sb from         NA
antimony potassium
tartrate In drinking
water, lifetime
(0.35 mg Bs/kg/day,
0.46 mg Sb20s kg/day)
mouse    NA; No effects         ND
mouse    NA; No effects         ND
rat      cancer; reduced        NDe
         llfespan,  altered
         blood chemistries
rat      cancer; reduced        NDe
         llfespan,  altered
         blood chemistries
rat      cancer; reduced        NDe
         llfespan, altered
         blood chemistries
3E»0          NA


3E.ll>1       NA
4E-4
NA
4E-4*
5E-4'
         300   U.S. EPA. 19B7/
               U.S. EPA. 1989

        3000   U.S. EPA, 1987/
               U.S. EPA, 1989
        1000   U.S. EPA. 1987/
               Schroeder
               et al.. 1970;
               U.S. EPA. 1990
        1000   U.S. EPA, 1987/
               Schroeder
               et al., 1970;
               U.S. EPA, 1985,
               1990
NA      1000   U.S. EPA, 1987/
               Schroeder
               et al.. 1970;
               U.S. EPA, 1990
NA
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                                                              inuLi  H. SUULMKUWJL HNU U1KUWH. lUAltill  (UIHLN I MAN IKKl INUbtNK 1 I I )
                                                                      Update:      -.  1990
Compound
chronic (RfO)





Antimony potassium
tartrate
subchronlc (RfDs)






Exposure
Inhalation; Oral
NA; 5 ppm Sb from
antimony potassium
tartrate In drinking
water, lifetime
(0.35 mg Sb/kg/day,
0.46 mg SbpOs kg/day)


NA; 5 ppm Sb from
antimony potassium
tartrate In drinking
water, lifetime
(0.35 mg Sb/kg/day,
0.93 mg SbK tartrate/
kg/day)
Species Effect of Concern Reference Dose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
NA rat cancer; reduced NDe 5E-4* NA 1000
llfespan, altered
blood chemistries





NA rat cancer; reduced NDe 9E-4f NA 1000
llfespan, altered
blood chemistries




Reference
Inhalation/Oral
U.S. EPA, 1987/
Schroeder
et al.. 1970;
U.S. EPA, 1985,
1987, 1990



U.S. EPA. 19B7/
Schroeder
et al.. 1970;
U.S. EPA. 1990



  chronic (RfO)
NA; 5 ppm Sb from
antimony potassium
tartrate In drinking
water, lifetime
(0.35 mg Sb/kg/day,
0.93 mg SbK tartrate/
kg/day)
NA         rat      cancer; reduced
                    llfespan, altered
                    blood chemistries
NO'
9E-4f         NA      1000    U.S. EPA. 1987/
                              Schroeder
                              et al., 1970;
                              U.S. EPA. 1987,
                              1990
Antimony tetroxlde
subchronlc (RfDs)




chronic (RfD)




Antimony trloxlde
subchronlc (RfDs)





NA; 5 ppm Sb from antl- NA
mony potassium tartrate
In drinking water, life-
time (0.35 mg Sb/kg/day.
0.44 mg Sb204/kg/day)
NA; 5' ppm Sb from antl- NA
mony potassium tartrate
In drinking water, life-
time (0.35 mg Sb/kg/day.
0.44 mg Sb204/kg/day)

NA; 5 ppm Sb from NA
antimony potassium
tartrate 1n drinking
water, lifetime
(0.35 mg Sb/kg/day ,
0.42 mg Sb203/kg/day)
rat cancer; reduced NDe
llfespan, altered
blood chemistries


rat cancer; reduced NDe
llfespan, altered
blood chemistries



rat cancer; reduced NDe
llfespan, altered
blood chemistries



4E-4f NA 1000 U.S. EPA, 1987/
Schroeder
et al., 1970;
U.S. EPA.
1990
4E-4f NA 1000 U.S. EPA. 1987/
Schroeder
et al.. 1970;
U.S. EPA. 1985,
1987, 1990

4E-4f NA 1000 U.S. EPA. 1987/
Schroeder
et al.. 1970;
U.S. EPA, 1990


0059h
                                                     A-7
                                                                                                07/12/90

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                                                                  ot-ii it it\i\ i  i nun  ft.
Update:
                                                                                                   MI1U UIM\VI«1C  I UA i t, i I I  V U MIL U  I I If 111 V,fll\lll*UULi*lll I I f
                                                                                                    ,  1990
Compound
chronic (RfD)
Aramlte
subchronlc (RfDs)
chronic (RfD)
Arsenic
subchronlc (RfOs)
chronic (RfD)
Atrazlne
subchronlc (RfDs)
chronic (RfD)
Exposure Species
Inhalation; Oral Inhalation Oral
NA; 5 ppm Sb from NA rat
antimony potassium
tartrate In drinking
water, lifetime
(0.35 mg Sb/kg/day,
0.42 mg Sb?03/kg/day)
NA; 500 ppm In diet NA dog
for 52 weeks (12.5
mg/kg/day)
NA; 100 ppm In NA rat
diet for 104 weeks
(5 mg/kg/day)
NA; 1 pg/kg/day NA human
NA; 1 pg/kg/day NA human
NA; 10 ppm In the diet. NA rat
2-generatton study
(0.5 mg/kg/day)
NA; 10 ppm In the diet. NA rat
2-generatlon study
(0.5 mg/kg/day)
Effect of Concern Reference Dose Uncertainty Factor
Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
cancer; reduced NO* 4E-4* NA 1000
llfespan, altered
blood chemistries
NA; degenerative ND 1E-1 NA 100
liver effect
NA; Increased ND 5E-29 NA 100
liver weight
(also see Table B)
NA; keratosls and ND 1E-3 NA 1
hyperplgmentatlon
cancer; keratosls ND IE -39 NA 1
and hyperplgmenta-
tlon (also see
Table B)
NA; decreased ND 5E-3 NA 100
body weight of
pups
NA; decreased ND 5E-3» NA 100
body weight of
pups
Reference
Inhalation/Oral
U.S. EPA. 1987/
Schroeder
et al., 1970;
U.S. EPA, 1985,
19B7, 1990
U.S. EPA, 1989/
Oser and Oser,
1960
U.S. EPA, 1989/
Popper et al..
1960; Oser and
Oser, 1962
U.S. EPA, 1984/
Tseng. 1977
U.S. EPA, 1984/
Tseng, 1977
U.S. EPA. 1990/
Clba-Gelgy.
1987; U.S. EPA,
1984. 1990
U.S. EPA, 1990/
Clba-Gelgy.
1987; U.S. EPA,
1984. 1990
0059h
                                                                                              A-8
                                                                                              07/12/90

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   in. in MI LI i LUIS
                                                      bunriHKr iflbU A: S.UUIHKUNII ANU LHKUN1C IUX1UIY (OIHtR THAN CARCINOGtNlCI IY)
                                                                      Update:      e,  1990
Compound
Barium
subchronlc (RfDs)







chronic (RfD)






Exposure Species
Inhalation; Oral Inhalation Oral

1.15 mg BaC03/m3 rat rat
(0.80 mg Ba/m3) 4
hours/day for 4 months
(0.14 mg Ba/kg/day);
100 ppm Ba from Bad 2
(5.1 mg Ba/kg/day) In
drinking water for
<16 months
1.15 mg BaC03/m3 rat rat
(0.80 mg/Ba/m3) 4
hours/day for 4 months
(0.14 mg Ba/kg/day);
100 ppm Ba from Bad?
(5.1 mg Ba/kg/day) In
drinking water for
Effect of Concern
Inhalation; Oral

fetotoxlclty;
Increased blood
pressure





fetotoxlclty;
Increased blood
pressure




Reference Dose Uncertainty Factor
Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)

5E-3 (lE-3)bb 5E-2 100 100







5E-4 (lE-4)°b 5E-2ff 1000 100






Reference
Inhalation/Oral

Tarasenko et
al., 1977;
U.S. EPA, 1984/
Perry et al.,
1983; U.S. EPA.
1990


Tarasenko et
al., 1977;
U.S. EPA. 1984/
Perry et al..
1983; U.S. EPA.
1984. 1985.
1990
Barium cyanide
  subchronlc (RfDs)
  chronic (RfD)
                        <16 months
NA; 10 ppm barium In
drinking water for up
to 16 months, equivalent
to barium cyanide at
7 mg/kg/day

NA; 10 ppm barium In
drinking water for up
to 16 months, equivalent
to barium cyanide at
7 mg/kg/day
NA         rat      NA; hypertension       NO
NA         rat      NA; hypertension       NO
7E-2          NA       100    NA/Perry et al..
                              1983; U.S. EPA,
                              1990
7E-2Z         NA       100    NA/Perry et al.,
                              1983; U.S. EPA.
                              1990
Benefln
subchronlc (RfDs)
chronic (RfD)
Benzal chloride
0059h
NA; 25 mg/kg/day In the NA dog NA; hematologlcal ND 3E-1
diet for 1 year effects
NA; 25 mg/kg/day In the NA dog NA; hematologlcal NO 3E-1*
diet for 1 year effects
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
A-9
NA 100 U.S. EPA. 1990/
Ell Lilly Co..
1972; U.S. EPA.
1984, 1990
NA 100 U.S. EPA. 1990/
Ell Lilly Co..
1972; U.S. EPA.
1984, 1990
U.S. EPA, 1985
07/12/90

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                                                                     Update:  *  e, 1990
Compound
Benzaldehyde
subchronlc (RfOs)



chronic (RfD)



Benzaldehyde cyanohydrln
Benzldlne
subchronlc (RFOS)




chronic (RfO)




Benzole acid
subchronlc (RfOs)



chronic (RfD)



Benzyl Alcohol
subchronlc (RfOs)



chronic (RfD)



Exposure
Inhalation; Oral

NA; 200 mg/kg/day by
gavage 5 days/week for
13 weeks

NA; 200 mg/kg/day by
gavage 5 days/week for
13 weeks



NA; 160 ppm benzldlne
dlhydrochlorlde In
drinking water for
33 months
(27.2 mg/kg/day)
NA; 160 ppm benzldlne
dlhydrochlorlde In
drinking water for
33 months
(27.2 mg/kg/day)

NA; per capita dally
dietary Intake of
benzole acid equiva-
lent to 312 mg/day
NA; per capita dally
dietary Intake of
benzole acid equiva-
lent to 312 mg/day

NA; 200 mg/kg by
gavage 5 days/week
for 13 weeks
(143 mg/kg/day)
NA; 400 mg/kg by
gavage 5 days/week
for 103 weeks
(286 mg/kg/day)
Species Effect of Concern Reference Dose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation
[mg/m3 (mg/kg/day)]

NA rat NA; kidney. NO
foreslomach


NA rat NA; kidney. NO
forestomach


DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT

NA mouse NA; brain cell ND
and liver cell
changes


NA mouse NA; brain cell ND
and liver cell
changes (also
see Table B)


NA human NA; Irritation, ND
malaise


NA human NA; Irritation, ND
malaise



NA rat NA; decrease In ND
body weight


NA rat NA; hyperplasla of ND
the epithelium of
the forestomach

Oral Inhalation Oral
(mg/kg/day)

1E+0 NA 100



lE-la NA 1000





3E-3 NA 1000




3E-3a NA 1000





4E*0 NA 1



4E+Oa NA 1




1E+0 NA 1000



3E-1 NA 1000



> Reference
Inhalation/Oral

U.S. EPA. 1990/
Kluwe et al.,
1983; U.S. EPA.
1985, 1990
U.S. EPA, 1990/
Kluwe et al..
1983; U.S. EPA,
1985, 1990
U.S. EPA. 1988

U.S. EPA. 1987/
Minefield
et al., 1983;
U.S. EPA, 1990

U.S. EPA. 1987/
Minefield
et al.. 1983;
U.S. EPA. 1990


U.S. EPA. 1987/
FASEB, 1973;
U.S. EPA, 1987

U.S. EPA, 1987/
FASEB. 1973;
U.S. EPA.
1987. 1990

U.S. EPA, 1989/
NTP, 1988; U.S.
EPA, 1989

U.S. EPA, 1989/
NTP, 1988; U.S.
EPA. 1989

0059h
A-10
07/12/90

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Compound
Beryl Hum
subchronk (RfOs)
chronic (RfO)
l.T-Blphenyl
subchronk (RfOs)
chronic (RfD)
81s(2-chloro1sopropyl)
subchronk (RfDs)
chronic (RfO)

Exposure
Inhalation; Oral
NA; 5 ppm In drinking
water for lifetime
(0.54 mg/kg/day)
NA; 5 ppm In drinking
water for lifetime
(O.S4 mg/kg/day)
NA; 0.1X In the diet
for 700 days (SO mg/kg/
day)
NA; 0.1X In the diet
for 700 days (50 mg/kg/
day)
ether
NA; 400 ppm In diet for
up to 104 weeks
(35.8 mg/kg/day)
NA; 400 ppm In diet for
up to 104 weeks
(35.8 mg/kg/day)
Bls(2-ethylhexyl) phthalate
subchronk (RfDs) NA; 0.04X of diet for
1 year (19 mg/kg/day)
chronic (RfD)
NA; 0.04X of diet for
1 year (19 mg/kg/day)
Update: " -e, 1990
Species Effect of Concern Reference
Inhalation Oral Inhalation; Oral Inhalation
[mg/m3 (mg/kg/day))
NA rat NA; none observed NO
NA rat NA; none observed NO
(also see Table B)
NA rat NA; kidney NO
damage
NA rat NA; kidney NO
damage
NA mouse NA; decrease In hemo- ND
globln and possible
erythrocyte destruc-
tion
NA mouse NA; decrease In hemo- ND
globln and possible
erythrocyte destruc-
tion
NA guinea NA; Increased ND
pig relative liver
weight
NA guinea NA; Increased ND
pig relative liver
weight (also see
Table B)

Dose Uncertainty Factor
Oral Inhalation Oral
(mg/kg/day)
5E-3 NA 100
5E-3a NA 100
5E-2 NA 1000
5E-2a NA 1000
4E-2 NA 1000
4E-2a NA 1000
2E-2 NA 1000
2E-2a NA 1000

Reference
Inhalation/Oral
U.S. EPA, 1987/
Schroeder and
Kitchener . 1975;
U.S. EPA. 1990
U.S. EPA, 1987/
Schroeder and
Kitchener, 1975;
U.S. EPA. 1990
NA/Ambrose
et al.. 1960;
U.S. EPA, 1984,
1990
NA/Ambrose
et al.. 1960;
U.S. EPA. 1984,
1990
NA/Hltsumorl et
al.. 1979; U.S.
EPA. 1990
NA/Hltsumorl et
al., 1979; U.S.
EPA. 1990
U.S. EPA. 1987/
Carpenter
et al.. 1953;
U.S. EPA. 1990
U.S. EPA, 1987/
Carpenter
et al.. 1953;
U.S. EPA, 1990
0059h
                                                                             A-ll
07/12/90

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Compound
Bis phenol A
subchronk (RfDs)


chronic (RfD)

Boron
suhrhronk (RfDs)

chronic (RfO)


Exposure
Inhalation; Oral
NA; 0-1000 ppm for
18 weeks, 2 generations
(NOAEL 750 ppm =
62 mg/kg/day)
NA; 0, 1000. 2000 ppm
(1000 ppm = 50 mg/kg/day)

NA; 350 ppm In diet
(8.75 mg/kg/day) for
2 years
NA; 350 ppm In diet
(8.75 mg/kg/day) for
2 years
Bromlnated dlbenzo-p-dloxlns
and dlbenzofurans
Bromoacetone
Bromochloroethane
Br omodkh lor ome thane
subchronk (RfDs)
c&ronk (RfD)
Bromoform
subchronk (RfDs)


NA; 25 mg/day by gavage
5 days/week for 102
weeks (17.9 mg/kg/day)
NA; 25 mg/day by gavage
5 days/week for 102
weeks (17.9 mg/kg/day)
NA; 25 mg/kg by gavage
5 days/week for 13 weeks
(17.9 mg/kg/day)
Update: >e. 1990
Species Effect of Concern Reference Dose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
NA rat NA; reduced body ND 6E-1 NA 100
weight


NA rat NA; reduced body ND 5E-2a NA 1.000
weight

NA dog NA; testlcular ND 9E-2 NA 100
lesions

NA dog NA; testlcular ND 9E-2a NA 100
lesions

DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA mouse NA; renal cytomegaly ND 2E-2 NA 1000
NA mouse NA. renal cytomegaly ND 2E-2a NA 1000
(also see Table 8)
NA rat NA; liver effects ND 2E-1 NA 100

Reference
Inhalation/Oral
U.S. EPA. 1988/
U.S. EPA, 1984,
14RR 1990
I7OO. I77U

U.S. EPA, 1988a/
NTP, 1982;
U.S. EPA,
1988, 1990
U.S. EPA, 1987/
Weir and
Fisher, 1972;
U.S. EPA. 1987
U.S. EPA, 1987/
Weir and
Fisher. 1972;
U.S. EPA. 1987
U.S. EPA,
1985a.b. 1986
U.S. EPA. 1986
U.S. EPA, 1985
U.S. EPA, 1987/
NTP, 1986/
U.S. EPA. 1990
U.S. EPA. 1987/
NTP, 1986;
U.S. EPA, 1990
U.S. EPA. 1987/
NTP, 1988;
U.S. EPA, 1989.
1990
0059h
                                                                             A-12
                                                                                                                                                  07/12/90

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Compound

chronic (RfO)



Bromomethane
subchronlc (RfDs)





chronic (RfO)





4-Bromophenyl phenyl
Bromophos
subchronlc (RfDs)



chronic (RfO)




Bromoxynll
subchronlc (RfDs)



chronic (RfD)




Exposure
Inhalation; Oral

NA; 25 mg/kg by gavage
5 days/week for 13 weeks
(17.9 mg/kg/day)


26.6 ppm (103 mg/m3)
7.5 hours/day. 4 days/
week for 8 months (HEC=
18 mg/m3); 2 mg/kg
5 days/week for 13 weeks
(1.4 mg/kg/day)
26.6 ppm (103 mg/m3)
7.5 hours/day. 4 days/
week for 8 months (HEC=
18 mg/m3); 2 mg/kg
5 days/week for 13
weeks (1.4 mg/kg/day)
ether

NA; 5 mg/kg/day In the
diet for 3 generations


NA; 5 mg/kg/day In the
diet for 3 generations




NA; 100 ppm In the diet
for 2 years (5 mg/kg/
day)

NA; 100 ppm In the diet
for 2 years (5 mg/kg/
day)

Update: e. 1990
Species Effect of Concern Reference Dose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
NA rat NA; liver effects NO 2E-2a NA 1000
(also see Table B)



rabbit rat neurotoxlclty; 6E-2 1.4E-2 300 100
hyperplasla
of forestomach
epithelium


rabbit rat neurotoxlclty; 6E-3J 1.4E-33'1 3000 1000
hyperplasla of
forestomach
epithelium


DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT

NA rat NA; depression ND 5E-2 NA 100
of plasma and
liver cholln-
esterase
NA rat NA; depression ND 5E-3 NA 1000
of plasma and
liver cholln-
esterase (also see
Table B)

NA rat NA; no adverse ND 2E-2 NA 300
effects


NA rat NA; no adverse ND 2E-2a NA 300
effects



Reference
Inhalation/Oral

U.S. EPA, 19B7/
NTP. 1988;
U.S. EPA. 1989.
1990

Russo et al..
1984/Oanse et
al.. 1984;
U.S. EPA, 1987


Russo et al..
1984/Oanse
et al.. 1984;
U.S. EPA. 1986,
1987. 1990

U.S. EPA. 1986

U.S. EPA, 1986/
Leuschner
et al.. 1967;
U.S. EPA, 1986
U.S. EPA. 1986/
Leuschner
et al.. 1967;
U.S. EPA, 1986


U.S. EPA. 1990/
Union Carbide,
1982; U.S. EPA.
1984, 1990
U.S. EPA, 1990/
Union Carbide,
1982; U.S. EPA,
1984. 1990
0059h
A-13
07/12/90

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                                                                     Update:    te, 1990
Compound
Bromoxynll octanoate
subchronlc (RfDs)



chronic (RfD)



Busan 77
Busan 90
1-Butanol (n-Butanol)
Subchronlc (RfOs)


chronic (RfD)


Butylate
subchronlc (RfDs)



chronic (RfO)




Butyl benzyl phthalate
subchronlc (RfDs)



Exposure
Inhalation; Oral

NA; 100 ppm In the diet
for 2 years (5 mg/kg/
day)

NA; 100 ppm In the diet
for 2 years (5 mg/kg/
day)




NA; 125 mg/kg/day by
gavage for 13 weeks

NA; 125 mg/kg/day by
gavage for 13 weeks


NA; 5 mg/kg/day by
gavage for 12 months


NA; 5 mg/kg/day by
gavage for 12 months




NA; 0.2BX of diet
for 26 weeks (159
mg/kg/day)

Species
Inhalation Oral

NA rat



NA rat



DATA
DATA

NA rat


NA rat



NA dog



NA dog





NA rat



Effect of Concern Reference Dose Uncertainty Factor
Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)

NA; no adverse ND 2E-2 NA 300
effects


NA; no adverse ND 2E-2a NA 300
effects


INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT

NA; effects ND 1E*0 ND 100
on erythrocyte

NA; effects ND lE-la ND 1000
on erythrocyte


NA; liver ND 5E-2 NA 100
effects


NA; liver ND 5E-2a NA 100
effects




NA; effects on body ND 2E+0 NA 100
weight gain, testes,
liver, kidney

Reference
Inhalation/Oral

U.S. EPA, 1990/
Union Carbide,
1982; U.S. EPA,
1984, 1990
U.S. EPA. 1990/
Union Carbide.
1982; U.S. EPA.
1984, 1990
U.S. EPA. 1984
U.S. EPA. 1984

U.S. EPA, 1989/
U.S. EPA, 1986,
1989, 1990
U.S. EPA, 1989/
U.S. EPA, 1986.
1989. 1990

U.S. EPA. 1984/
Stauffer Chem.
Co.. 1987; U.S.
EPA. 1984. 1990
U.S. EPA, T984/
Stauffer Chem.
Co.. 1987; U.S.
EPA. 1984. 1989,
1990

U.S. EPA, 1987.
1989/NTP, 1985;
U.S. EPA, 1986,
1987. 1989, 1990
0059h
                                                                             A-14
07/12/90

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buMMAKK lAbLt A.  SUbLHKUNll ANU LHKUN1L IUX1L1IY (OIHtK IHAN CAKClNOGtNlCl IY)
               Update-     ne.  1990
Compound
chronic (RfO)
t-Butylchlorlde
Butyrolactone, gamma
Cacodyllc acid
subchronlc (RfDs)
chronic (RfD)
Cadmium
subchronlc (RfOs)
chronic (RfD)
Calcium cyanide
subchronlc (RfDs)
chronic (RfD)
Caprolactam
subchronlc (RfDs)
Exposure
Inhalation; Oral
NA; 0.28X of diet
for 26 weeks (159
mg/kg/day)


NA; 1B4 mg/kg cacodyllc
acid In diet for 90 days
(9.2 mg/kg/day)
NA; 184 mg/kg cacodyllc
acid In diet for 90 days
(9.2 mg/kg/day)
NA; NA
NA; NA
NA; 10.B mg/kg/day
fumigated cyanide In
food for 2 years
(19.1 mg calcium
cyanlde/kg/day)
NA; 10.B mg/kg/day
fumigated cyanide In
food for 2 years
(19.1 mg calcium
cyanide/kg/day)
NA; 0.1X diet 90 days
(50 mg/kg/day)
Species Effect of Concern Reference Dose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
NA rat NA; effects on body NO 2E-la NA 1000
weight gain, testes,
liver, kidney
(also see Table B)
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT1
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA rat NA; none ND 3E-2" NA 300
NA rat NA; none ND 3E-39.cc NA 3000
NA NA cancer; NA ND NDh NA NA
NA human cancer (see Table B); ND IE -3 (food)9'1 NA 10
renal damage 5E-4 (water)
NA rat NA; weight loss, NA 4E-2" NA 500
thyroid effects and
fliyelln degeneration
NA rat NA; weight loss, ND 4E-2a>n NA 500
thyroid effects and
myelln degeneration
NA rat NA; renal effects ND 5E-1 NA 100
Reference
Inhalation/Oral
U.S. EPA, 1987,
1989/NTP, 1985;
U.S. EPA, 1986,
1987, 1989, 1990
U.S. EPA. 1988/
U.S. EPA, 1988
U.S. EPA. 1984/
U.S. EPA, 19B4/
U.S. EPA, 1989/
Nees, 1968;
U.S. EPA, 1989
U.S. EPA, 1989/
Nees, 1968;
U.S. EPA. 1989
U.S. EPA, 1984/
U.S. EPA, 1984
U.S. EPA, 1984/
U.S. EPA. 1988,
1990
N A/Howard and
Hanzal. 1955;
Phllbrlck et
al.. 1979; U.S.
EPA. 1990
N A/Howard and
Hanzal. 1955;
Phllbrlck et
al.. 1979; U.S.
EPA, 1990
U.S. EPA, 1988/
Powers et al.,
1984; U.S. EPA,
1988
                      A-15
                                                                                            07/12/90

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                                                                       Update:  ~ -»e, 1990
Compound
chronic (RfD)
Captafol
subchronlc (RfDs)
chronic (RfD)
Captan
subchronlc (RfOs)
chronic (RfD)
Carbaryl
subchronlc (RfDs)
chronic (RfD)
Exposure Species
Inhalation; Oral Inhalation Oral
NA; 1000 ppm for 3 NA rat
generations
(50 mg/kg/day)
NA; 2 mg/kg/day In NA dog
capsules for 12 months
NA; 2 mg/kg/day In NA dog
capsules for 12 months
NA; 12.5 mg/kg/day In NA rat
the diet (multi-
generation)
NA; 12.5 mg/kg/day In NA rat
the diet (multi-
generation)
NA; 200 ppm In the diet NA rat
for 2 years (9.6 mg/kg/
day)
NA; 200 ppm In the diet NA rat
for 2 years (9.6 mg/kg/
day)
Effect of Concern Reference Dose Uncertainty Factor
Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
NA; reduced body NO 5E-la NA 100
weight
NA; kidney and ND 2E-3 NA 1000
bladder effects
NA; kidney and ND 2E-3a NA 1000
bladder effects
(also see Table B)
NA; decreased ND 1E-1 NA 100
body weight
NA; decreased ND 1E-13 NA 100
body weight
NA; kidney and ND 1E-1 NA 100
and liver
toxlclty
NA; kidney and ND lE-la NA 100
and liver
toxlclty
Reference
Inhalation/Oral
U.S. EPA, 1988a/
Serota et al.,
1984; U.S. EPA.
1988, 1990
U.S. EPA. 1990/
Ortho-Chevron
Chemical Co.,
1985; U.S. EPA.
1984. 1990
U.S. EPA, 1990/
Ortho-Chevron
Chemical Co.,
1985; U.S. EPA,
1984, 1990
U.S. EPA, 1990/
Stauffer Chem.
Co., 1982;
Chevron Chem.
Co.. 1982; U.S.
EPA, 1984, 1990
U.S. EPA, 1990/
Stauffer Chem.
Co., 1982;
Chevron Chem.
Co.. 1982; U.S.
EPA. 1984. 1990
U.S. EPA, 1990/
Carpenter et
al., 1961; U.S.
EPA. 1984. 1990
U.S. EPA. 1990/
Carpenter et
al., 1961; U.S.
EPA, 1984, 1990
0059h
A-16
07/12/90

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                           HtALlH EmCIS ASSESSMtNIS SUMMARY  TABLE A: SUBCHP'  '- AND CHRONIC TOXICI1Y (OTHER THAN CARCINOGENICITY)
                                                                     Update     ,e,  1990
Exposure Species Effect of Concern Reference Dose Uncertainty Factor Reference
Compound
Carbofuran
subchronlc (RfDs)
chronic (RfD)
Carbon dlsulflde
subchronlc (RfDs)
Inhalation; Oral Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral Inhalation/Oral
[mg/in3 (mg/kg/day)] (mg/kg/day)
NA; 0.5 mg/kg/day In NA
the diet for 1 year
NA; 0.5 mg/kg/day 1n NA
the diet for 1 year
NA; 20 ppm (62.3 mg/m») NA
Inhalation 6 hours/day
during pregnancy and
dog NA; hematolog- ND
leal, testlcular
and uterine
effects
dog NA; hematolog- ND
leal, testlcular
and uterine
effects
rabbit NA; fetal toxlclty; ND
malformation
5E-3 NA 100 U.S. EPA.
FNC Corp.
U.S. EPA.
1990
5E-3« NA 100 U.S. EPA.
FMC Corp.
U.S. EPA.
1990
1E-1 NA 100 NA/Hardln
al., 1981
EPA, 1990
1990/
. 1983;
1984.
1990/
, 1983;
1984,
et
; U.S.
  chronic (RfD)
Carbon tetrachlorlde
  subchronlc (RfDs)
  chronic (RfD)
Chloral
before breeding (1.6
mVday breathing rate
and 0.5 absorption factor
used to calculate dose
of 11.0 mg/kg/day)

NA; 20 ppm (62.3 mg/m»)   NA
Inhalation 6 hours/day
during pregnancy and
before breeding (1.6
mVday breathing rate
and 0.5 absorption factor
used to calculate dose
of 11.0 mg/kg/day)
NA; 1 mg/day, 5 days/     NA
week for 12 weeks
(0.71 mg/kg/day)
NA; 1 mg/day. 5 days/     NA
week for 12 weeks
(0.71 mg/kg/day)
rabbit   NA;  fetal  toxlclty;     1E-21
         malformation
              NA
rat      NA;  liver  lesions       ND
rat      NA;  liver  lesions      ND
         (also see  Table  B)
7E-3
7E-4a
NA
NA
         100    NA/Hardln et
                al.. 1981; U.S.
                EPA. 1990
 100    U.S.  EPA,  1984/
        Bruckner  et  al..
        1986; U.S. EPA,
        1990

1000    U.S.  EPA.  1984/
        Bruckner  et  al.,
        1986; U.S. EPA.
        1990
subchronlc (RfDs)
NA; 15.7 mg/kg/day NA
from drinking water
mouse NA; hepatotoxlclty ND
2E-2 NA 1000 U.S. EPA, 198B/
Sanders et al.,
1982; U.S. EPA.
1988
0059h
                                                    A-17
                                                                                    08/01/90

-------
                                                                     Update:
                                                         " NA
thyroid effects and
myelln degeneration
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT^
rat NA; myocarditis ND 2E-2 NA
rat NA; myocarditis ND 2E-3 NA
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT (SEE TABLE B)
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT (SEE TABLE B)
A-18
1000 U.S. EPA, 1988/
Velslcol
Chemical Corp.,
1983; U.S. EPA,
1990
500 NA/Howard and
Hanzal. 1955;
PMlbrlck et
al.. 1979; U.S.
EPA. 1990
500 NA/Howard and
Hanzal, 1955;
Phllbrlck et
al., 1979; U.S.
EPA, 1990
U.S. EPA. 1988
1000 U.S. EPA, 19B8/
IRDC. 1982;
U.S. EPA, 1988
10,000 U.S. EPA, 1988/
IRDC. 1982;
U.S. EPA, 1988
U.S. EPA. 1987
U.S. EPA. 1987
07/12/90

-------
   mm m LIILI.I:>
                                                       MjnnAKT  iflbLt A: bUULHKi"" i. ANU IHKUNK  IOX1LIIY (UIHLK  IHAN CAHClNOGtNlCl I Y)
                                                                      Update      e,  1990
Compound
4-Chloroanlllne
(p-Chloroanlllne)
subchronlc (RfD$)
chronic (RfD)
Exposure
Inhalation; Oral
NA; 250 ppm In diet
for 78 weeks (12.5
mg/kg/day)
NA; 250 ppm In diet
for 78 weeks (12.5
mg/kg/day)
Species Effect of Concern
Inhalation Oral Inhalation; Oral
NA rat NA; proliferate
lesions of the
spleen
NA rat NA; prollferatlve
lesions of the
spleen (also
Reference
Inhalation
[mg/m3 (mg/kg/day)]
NO
NO
Dose Uncertainty Factor
Oral Inhalation Oral
(mg/kg/day)
4E-3 NA 3000
4E-3a NA 3000
Reference
Inhalation/Oral
U.S. EPA. 1987/
NCI. 1979; U.S.
EPA. 1990
U.S. EPA. 1987/
NCI. 1979; U.S.
EPA. 1990
Chlorobenzene
  subchronlc (RfOs)
75 ppm (345 mg/m3)
7 hours/day. 5 days/
week for 120 days
(53 mg/kg/day);
27.3 mg/kg/day by
capsule for 90 days
                                                                      see Table B)
rat        dog      liver and kidney
                    effects; liver and
                    kidney effects
2E-1 (5E-2)       2E-1        1000       100    Dllley. 1977;
                                                U.S. EPA, 1984/
                                                Monsanto, 1967;
                                                U.S. EPA, 1985,
                                                1989. 1990
chronic (RfD)





Chlorobenzllate
subchronlc (RfDs)




chronic (RfD)




p-Chlorobenzolc acid
subchronlc (RfDs)



75 ppm (345 mg/m3) rat
7 hours/day, 5 days/
week for 120 days
(53 mg/kg/day);
27.3 mg/kg/day by
capsule for 90 days

NA; 5 mg/kg/day In NA
starch suspension by
gastric Intubation for
13 days during gestation
period
NA; 5 mg/kg/day In NA
starch suspension by
gastric Intubation for
13 days during gestation
period

NA; 0.2X In diet for NA
5 months (173.3
mg/kg/day)

dog liver and kidney 2E-2 (5E-3)
effects; liver and
kidney effects
(also see Table 8)



rabbit NA; decreased stool ND
quantity, food
consumption and
weight gain;
hyperlrrltabllUy
rabbit NA; decreased stool ND
quantity, food
consumption and
weight gain;
hyperlrrltablllty

rat NA; none observed ND



2E-2a 10.000 1000 Dllley, 1977;
U.S. EPA, 1984/
Monsanto, 1967;
U.S. EPA, 1985,
1989. 1990


2E-2 NA 300 NA/Clba-Gelgy
Corp., 1984a;
U.S. EPA, 1990


2E-2a NA 300 NA/Clba-Gelgy
Corp., 19B4a;
U.S. EPA. 1990



2E»0 NA 100 U.S. EPA. 1987/
Kleckebusch
et al., 1960;
U.S. EPA. 1987
0059h
                                                     A-19
                                                                                                                                                  07/12/90

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                                                                      Update:
      ,  1990
Compound
chronic (RfO)



Exposure
Inhalation; Oral
NA; 0.2X In diet for
5 months (173.3
mg/kg/day)

Species
Inhalation Oral
NA rat



Effect of Concern Reference Dose Uncertainty Factor
Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
NA; none observed ND 2E-1 NA 1000



Reference
Inhalation/Oral
U.S. EPA. 1987/
Kleckebusch
et al., 1960;
U.S. EPA. 1987
4-ChlorobenzotMfluorlde
subchronlc (RfOs)



chronic (RfO)



NA; 15 mg/kg/day by
gavage dally for 90
days

NA; IS mg/kg/day by
gavage dally for 90
days

NA rat



NA rat



NA; renal tubular ND 2E-1 NA 100
degeneration


NA; renal tubular ND 2E-2 NA 1000
degeneration


U.S. EPA. 1988/
Hooker Chemical
Co., 1981;
U.S. EPA. 1988
U.S. EPA. 1988/
Hooker Chemical
Co.. 1981;
U.S. EPA, 1988
2-Chloro-l ,3-butadlene
(Chloroprene)
subchronlc (RfDs)

chronic (RfD)


1-Chlorobutane
subchronlc (RfDs)


chronic (RfD)


2-Chlorobutane

Chlorocyclopentadlene
Chlorodlbromome thane
p-Chloro-m-cresol
subchronlc (RfDs)



10 ppm, 6 hours/day,
5 days/week for 2 years
(36 mg/m3); NA
10 ppm. 6 hours/day,
S days/week for 2 years
(36 mg/m3); NA

NA; 120 mg/kg, 5 days/
week for 13 weeks by
gavage (66 mg/kg/day)
NA; 60 mg/kg, 5 days/
week for 103 weeks by
gavage (43 mg/kg/day)



(see Dlbromochloromethane)

NA; 200 mg/kg/day for
2B days


rat NA


rat NA



NA rat


NA rat


DATA

DATA


NA rat



alopecia, retarded 1E-K4E-2) 2E-2M 100 NA
growth; NA

alopecia, retarded lE-l(4E-2) 2E-2°.1 100 NA
growth; NA


NA; CNS and ND 9E-1 NA 100
hematopoletlc
effects
NA; mortality. ND 4E-11 NA 100
CNS and hemato-
loglc effects
INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT'

INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT1


NA; decrease In ND 2E+0 NA 100
weight gain


Du Pont. 1985;
U.S. EPA. 1989/
U.S. EPA. 1989
Du Pont. 1985;
U.S. EPA. 1989/
U.S. EPA, 1989

U.S. EPA, 198B/
NTP. 1986;
U.S. EPA, 1988
U.S. EPA. 1988/
NTP. 1986;
U.S. EPA, 1988
U.S. EPA, 1988/
U.S. EPA. 1988
U.S. EPA, 1988


U.S. EPA, 1988/
Nadsen et al.,
1986; U.S. EPA.
1988
0059h
A-20
07/12/90

-------
Update: ne, 1990
Compound
chronic (RfO)
Chloroform
subchronlc (RfOs)
chronic (RfD)
m-Chloronl trobenzene
Chlorophenol, 3- and
2-Chlorophenol
subchronlc (RfDs)
chronic (RfD)
Exposure
Inhalation; Oral
NA; NA
NA; 15 mg/kg. 6 days/
week for 7.5 years
(12.9 mg/kg/day)
NA; 15 mg/kg. 6 days/
week for 7.5 years
(12.9 mg/kg/day)

4-
NA; 50 ppm In drinking
water from weaning
through birth of first
litter (5 mg/kg/day)
NA; 50 ppm In drinking
water from weaning
through birth of first
litter (5 mg/kg/day)
Species
Inhalation Oral
NA NA
NA dog
NA dog
DATA
DATA
NA rat
NA rat
Effect of Concern Reference Dose Uncertainty Factor
Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
NA; NA ND NO NA NA
NA; liver lesions ND 1E-2 NA 1000
NA; liver lesions ND 1E-23 NA 1000
(also see Table B)
INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA; reproductive ND 5E-3 NA 1000
effects
NA; reproductive ND 5E-3a NA 1000
effects
Reference
Inhalation/Oral
U.S. EPA, 1988/
U.S. EPA, 1988
U.S. EPA, 1988/
Hey wood et al..
1979; U.S. EPA.
1990
U.S. EPA. 1988/
Heywood et al.,
1979; U.S. EPA.
1990
U.S. EPA, 1985
U.S. EPA. 1987
U.S. EPA.
1987a,b/Exon and
Koeller. 1982;
U.S. EPA,
1987a.b. 1990
U.S. EPA.
1987a,b/Exon and
Koeller, 1982;
U.S. EPA,
1987a,b, 1990
Chloroprene (see 2-Chloro-l ,3-butacMene)
2-Chloropropane
subchronlc (RfDs)
chronic (RfD)
3-Chloropropene (see
250 ppm (803 mg/m3).
6 hours/day. 5 days/
weeks for 4 weeks
(91.4 mg/kg/day); NA
250 ppm (803 mg/m3).
6 hours/day. 5 days/
weeks for 4 weeks
(91.4 mg/kg/day); NA
Allyl chloride)
rat NA
rat NA

liver effects; NA 3E+0 (9E-1) ND 100 NA
liver effects; NA 3E-1 (9E-2) ND 1000 NA

Gage. 1970;
U.S. EPA, 19B7/
U.S. EPA, 1987
Gage. 1970;
U.S. EPA, 1987/
U.S. EPA, 1987

0059h
A-21
07/12/90

-------


Compound

Chlorotoluenes, m- and
o-Chlorotoluene
subchronlc



chronic (RfO)



Chlorpyrlfos
subchronlc (RfOs)



chronk (RfD)



Chlorpyrlfos -methyl
subchronlc (RfDs)



chronic (RfD)



Chlorthalonll
subchronlc (RfOs)



chronic (RfD)




Exposure
Inhalation; Oral

P-

NA; 20 mg/kg/day by
gavage for 103 or
104 days

NA; 20 mg/kg/day by
gavage for 103 or
104 days


NA; 0.03 mg/kg/day by
capsule for 20 days or
0.1 mg/kg/day for 9 days

NA; 0.03 mg/kg/day by
capsule for 20 days or
0.1 mg/kg/day for 9 days


NA; 3-generatlon study
In rats. 2-year study
In dogs

NA; 3-generatlon study
1n rats. 2-year study
In dogs


NA; 60 ppm In the diet
for 2 years (1.5 mg/kg/
day)

NA; 60 ppm In the diet
for 2 years (1.5 mg/kg/
day)

Update: M>. 1990
Species Effect of Concern Reference Dose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)) (mg/kg/day)
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT

NA rat NA; decreased body NA 2E-1 NA 100
weight gain


NA rat NA; decreased body NA 2E-2a NA 1000
weight gain



NA human NA; decreased ND 3E-3 NA 10
plasma cholln-
esterase

NA human NA; decreased ND 3E-3a NA 10
plasma cholln-
esterase


NA rat, NA; reduced ND 1E-2 NA TOO
dog fertility In
rats, liver
effects In dogs
NA rat, NA; reduced ND IE -29 NA 100
dog fertility In
rats, liver
effects In dogs

NA dog NA; kidney ND 1.5E-2 NA 100
lesions


NA dog NA; kidney ND 1.5E-23 NA 100
lesions
(also see Table B)


Reference
Inhalation/Oral

U.S. EPA. 1985

U.S. EPA, 1990/
Gibson et al..
1974; U.S. EPA
1990
U.S. EPA. 1990/
Gibson et al..
1974; U.S. EPA
1990

U.S. EPA, 1990/
Dow Chemical
Co.. T972; U.S.
EPA. T984. 1990
U.S. EPA. 1990/
Dow Chemical
Co., 1972; U.S.
EPA, 1984. 1990

U.S. EPA, 1984/
U.S. EPA, 1984


U.S. EPA. 19B4/
U.S. EPA. 1984



U.S. EPA. 1990/
Diamond Shamrock
Chem. Co., 1970;
U.S. EPA, 1990
U.S. EPA, 1990/
Diamond Shamrock
Chem. Co.. 1970;
U.S. EPA, 1990
0059h
A-22
07/12/90

-------
                           ML Ml III LIILI.IJ MJjLJjril HIO JUIII IHIt I  IMULU M. JOULimOHlL nl«U bllnunib lUAlClll iu.ni..> Ilinil I.ll»>.llll/Ul.»».» • I
                                                                      Update:     ne.  1990
      Compound
                              Exposure
                              Species
  Inhalation; Oral
                                                 Inhalation  Oral
        Effect  of  Concern
        Inhalation;  Oral
                           Reference Dose	  Uncertainty Factor     Reference
                                          Oral     Inhalation    Oral  Inhalation/Oral
    Inhalation          	
[mg/m3 (nig/kg/day)]  (mg/kg/day)
Chlorthlophos
  subchronlc (RfOs)
  chronic (RfO)
NA; 1.6 ppm In the diet   NA         rat      NA; no effect          ND
for 2 years (0.08 mg/                         on erthrocyte
kg/day)                                       chollnesterase


NA; 1.6 ppm 1n the diet   NA         rat      NA; no effect          ND
for 2 years (0.08 mg/                         on erthrocyte
kg/day)                                       chollnesterase
                                                  8E-4
                                                                                                               BE -4
                                                       NA       100    U.S. EPA. 1986/
                                                                       Worthing and
                                                                       Walker, 1983;
                                                                       U.S. EPA. 1986

                                                       NA       100    U.S. EPA, 1986/
                                                                       Worthing and
                                                                       Walker. 1983;
                                                                       U.S. EPA. 1986
Chromium (III)
  subchronlc (RfDs)
  chronic (RfO)
NA; 5X Cr203 In diet      NA
5 days/week for 90 days
(1400 mg Cr/kg/day)
NA; 5X Cr203 In diet
5 days/week for 600
feedings (1468 mg
Cr/kg/day)
                                                  NA
rat
NA; hepatotoxldty
                                                                     ND
rat      NA; hepatotoxldty     ND
                       1E*1          NA        100    U.S. EPA.  1984/
                                                     Ivankovlc  and
                                                     Preussman,  1975;
                                                     U.S. EPA,  1984

                       lE»Oa         NA       1000    U.S. EPA.  1984/
                                                     Ivankovlc  and
                                                     Preussman.  1975;
                                                     U.S. EPA,  1984.
                                                     1990
inromium \vi|
subchronlc (RfOs)
chronic (RfD)
Chrysene
Copper
subchronlc (RfDs)
chronic (RfD)
NA; 25 ppm Cr VI In NA
drinking water for 1
year (2.4 mg/kg/day)
NA; 25 ppm Cr VI In NA
drinking water for 1
year (2.4 mg/kg/day)

NA; 5.3 mg. single NA
dose
NA; NA NA
rat cancer; not defined ND 2E-2 NA
rat cancer (see ND 5E-3« NA
Table B); not
defined
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
human NA; local GI ND 1.3mg/lk NA
Irritation
human NA; local GI ND 1.3 mg/l* NA
Irritation1
100 U.S. EPA, 1984/
HacKenzle et
al., 1958; U.S.
EPA, 1984
500 U.S. EPA. 1984/
HacKenzle et
al.. 1958; U.S.
EPA, 1984, 1990
U.S. EPA, 1984
NA U.S. EPA, 1984/
U.S. EPA. 1987
NA U.S. EPA, 1984/
U.S. EPA, 1987
 0059h
                                                                              A-23
                                                                                                                                                   07/12/90

-------
                                                                   Update:   "me,
Compound
Copper cyanide
subchronlc (RfDs)


chronic (RfO)


m-Cresol
subchronlc (RfDs)




chronic (RfD)




o-Cresol
subchronlc (RfOs)




Exposure
Inhalation; Oral
NA; 5 mg/kg/day by
gavage for 90 days


NA; 5 mg/kg/day by
gavage for 90 days


NA; SO mg/kg/day
for 90 days




NA; 50 mg/kg/day
for 90 days




NA; 50 mg/kg/day
for 90 days




Soecles Effect of Concern Reference Dose Uncertainty Factor We ence
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral innaiation/urai
[mg/m3 (mg/kg/day)] (mg/kg/day)
NA rat NA; decreased body NO 5E-2 NA
and organ weights.
hlstopathologlc
alterations In liver
and kidney
NA rat NA; decreased body NO 5E-3a NA
and organ weights,
hlstopathologlc
alterations In liver
and kidney
NA rat NA; reduced body NO 5E-1 NA
weight gain, neuro-
toxlclty




NA rat NA; reduced body NO 5E-2a NA
weight gain, neuro-
toxlclty




NA rat NA; reduced body NO 5E-1 NA
weight gain, neuro-
toxlclty




100 NA/U.S. EPA.
1986. 1990


1000 NA/U.S. EPA.
1966. 1990


100 U.S. EPA. 1984,
1985/Nlcro-
blologlcal
Associates.
1986; Toxlclty
Research Labora-
tories. 1987;
U.S. EPA, 1990
1000 U.S. EPA, 1984.
1985/Hlcro-
blologlcal
Associates.
1986; Toxlclty
Research Labora-
tories. 1987;
U.S. EPA. 1990
100 U.S. EPA. 1984.
1985/Nlcro-
blologlcal
Associates,
1986; Toxlclty
Research Labora-
tories. 1987;
U.S. EPA, 1990
0059h
                                                                           A-24
                                                                                                                                               07/12/90

-------


Compound

chronic (RfD)







p-Cresol
subchronlc (RfDs)







chronic (RfD)







Cumene
subchronlc (RfOs)




chronic (RfO)






Exposure
Inhalation; Oral

NA; 50 mg/kg/day
for 90 days







NA; SO mg/kg/day
for 90 days






NA; 50 mg/kg/day
for 90 days







105.1 ppm (517 mg/m3)
for 6 hrs/day, 5
days/wk for 4 weeks;
110 mg/kg/day for
194 days
105.1 ppm (517 mg/m3)
for 6 hrs/day, 5
days/wk for 4 weeks;
110 mg/kg for 194 days


Update: e. 1990
Species Effect of Concern Reference Dose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
NA rat NA; reduced body NO 5E-2a NA 1000
weight gain, neuro-
toxlclty






NA rat NA; reduced body ND 5E-1 NA 100
weight gain, neuro-
toxlclty





NA rat NA; reduced body ND 5E-2a NA 1000
weight gain, neuro-
toxlclty






rat rat CNS Involvement, 9E-2 4E-1 1000 300
nasal Irritation;
renal


rat rat CNS Involvement, 9E-3J 4E-2* 10.000 3000
nasal Irritation;
renal




Reference
Inhalation/Oral

U.S. EPA. 1984,
1985/Hlcro-
blologlcal
Associates,
1986; Toxldty
Research Labora-
tories, 1987;
U.S. EPA. 1990

U.S. EPA. 1984.
1985/Mlcro-
blologlcal
Associates,
1986; Toxldty
Research Labora-
tories. 1987;
U.S. EPA, 1990
U.S. EPA. 1984.
1985/Mlcro-
blologlcal
Associates,
1986; Toxldty
Research Labora-
tories, 1987;
U.S. EPA, 1990

Honsanto Company
1986; U.S. EPA.
1987, 1990/
Wolfe, 1956;
U.S. EPA. 1990
Monsanto Company
1986; U.S. EPA,
1987. 1990/
Wolfe et al.,
1956; U.S.
EPA. 1987. 1990
0059h
A-25
07/12/90

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Compound
Cyanazlne
subchronlc (RfDs)


chronic (RfD)


Cyanide
subchronlc (RfDs)



chronic (RfD)


Cyanogen
subchronlc (RfDs)


chronic (RfD)



Cyanogen bromide
subchronlc (RfDs)




Exposure Species
Inhalation; Oral Inhalation Oral
NA; 25 ppm In the diet NA dog
for 1 year (0.625 g/kg/
day)


NA; 25 ppm In the diet NA dog
for 1 year (0.625 g/kg/
day)


NA; 10.8 mg CN/kg/day NA rat
for 104 weeks from
diet treated with HCN


NA; 10.8 mg CN/kg/day NA rat
for 104 weeks from
diet treated with HCN



NA; 10.8 mg/kg/day NA rat
fumigated cyanide In
food for 2 years
(21.6 mg Cyanogen/
kg/day)
NA; 10.8 mg/kg/day NA rat
fumigated cyanide In
food for 2 years
(21.6 mg Cyanogen/
kg/day)
NA; 10.8 mg/kg/day NA rat
fumigated cyanide In
food for 2 years
(4.4 mg Cyanogen
bromlde/kg/day)
Update- Tie. 1990
Effect of Concern Reference
Inhalation; Oral Inhalation
[mg/m3 (mg/kg/day)]
NA; body weight NO
loss, hemato-
loglc and clin-
ical chemistry
parameters
NA; body weight NO
loss, hemato-
loglc and clin-
ical chemistry
parameters
NA; weight loss. NO
thyroid effects and
myelln degeneration


NA; weight loss, ND
thyroid effects and
myelln degeneration*



NA; weight loss. ND
thyroid effects
myelln degeneration


NA; weight loss. ND
thyroid effects
myelln degeneration


NA; weight loss. ND
thyroid effects
myelln degeneration



Dose Uncertainty Factor
Oral Inhalation Oral
(mg/kg/day)
2E-3 NA 300


2E-3a NA 300


2E-2 NA 500



2£-2a NA 500



4E-2" NA 500


4£-2a-n NA 500



9E-2n NA 500




Reference
Inhalation/Oral
U.S. EPA, 1990/
Shell Chem. Co.,
1986; U.S. EPA.
1984. 1990

U.S. EPA. 1990/
Shell Chem. Co.,
1986; U.S. EPA,
1984, 1990

U.S. EPA. 19B4/
Howard and
Hanial, 1955;
U.S. EPA, 1984,
1990
U.S. EPA. 1984/
Howard and
Hanzal. 1955;
U.S. EPA. 1984,
1990

NA/Howard and
Hanzal. 1955;
Phllbrlck et
al.. 1979; U.S.
EPA, 1990
NA/Howard and
Hanzal. 1955;
Phllbrlck et
al.. 1979; U.S.
EPA, 1990
NA/Howard and
Hanzal. 1955;
Phllbrlck et
al.. 1979; U.S.
EPA. 1990
0059h

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                                           ftbbliiniim bUMMAKT lABLt A: bUblHKI'"''  AND IHKUN1C  IUXRIIY  (UIHtH  IHAN  CAKCINUGtNILI IY)
                                                                       Update:      >,  1990
Compound
chronic (RfD)
Cycloate
Cyclohexanol
Cyclohexylamlne
subchronlc (RfDs)
chronic
Cyclopentadlene
subchronlc (RfDs)
chronic (RfD)
Dae thai (DCPA)
subchronlc (RfDs)
chronic (RfD)
Oalapon (sodium salt)
subchronlc (RfDs)
Exposure
Inhalation; Oral
NA; 10.8 mg/kg/day
fumigated cyanide 1n
food for 2 years
(4.4 mg Cyanogen
bromlde/kg/day)


NA; 600 ppm cyclohexy-
lamlne-HCl In diet
for 90 days (30 mg/kg/
day cyclohexylamlne)
NA; 600 ppm cyclohexy-
lamlne.HCl In diet for
2 years (18 mg/kg/day
cyclohexylamlne)
250 ppm (676 mg/m3)
for 135. 7-hour expo-
sures In 194 days
(87.3 mg/kg/day); NA
NA; NA
NA; 1000 ppm In the
In the diet for 2
years (50 mg/kg/day)
NA; 1000 ppm In the
In the diet for 2
years (50 mg/kg/day)
NA; 15 mg/kg/day In the
diet for 2 years
Species
Inhalation Oral
NA rat
DATA
DATA
NA rat
NA rat
rat NA
NA NA
NA rat
NA rat
NA rat
Effect of Concern Reference Dose Uncertainty Factor
Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
NA; weight loss. NA 9E-2a>n NA 500
thyroid effects
myelln degeneration
INADEQUATE FOR QUANTITATIVE RISK ASSESSMENTS
INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA; reduced body NO 3E-1 NA 100
weight
NA; testlcular ND 2E-la NA 100
effects
liver and kidney 3E*0 (9E-1) NO 100 NA
lesions; NA
NA; NA ND ND NA NA
NA; kidney and NO 5E-1 NA 100
adrenal weights
NA; kidney and ND 5E-1« NA 100
adrenal weights
NA; Increased ND 3E-2 NA 300
relative kidney
weight
Reference
Inhalation/Oral
NA/Howard and
Hanzal, 1955;
Phllbrlck et
al.. 1979; U.S.
EPA. 1990
U.S. EPA. 1984
U.S. EPA. 1985
U.S. EPA, 1987/
Gaunt et al.,
1974; U.S. EPA.
1987
U.S. EPA. 1987/
Gaunt et al..
1976; U.S. EPA.
1987. 1990
Dow. 1987;
U.S. EPA. 1987/
U.S. EPA, 1987
U.S. EPA, 1987/
U.S. EPA. 1987
U.S. EPA, 1990/
Diamond Shamrock
Co.. 1963;
U.S. EPA. 1984.
1990
U.S. EPA, 1990/
Diamond Shamrock
Co.. 1963; U.S.
EPA, 1984. 1990
U.S. EPA. 1990/
Paynter et al..
1960; U.S. EPA.
1984, 1990
0059h
A-27
07/12/90

-------

Compound
chronic (RfD)

2.4-DB
subchronlc (RfOs)

chronic (RfD)


DOT
subchronlc (RfDs)


chronic (RfO)


Exoosure Species
Inhalation; Oral Inhalation Oral
NA; 15 mg/kg/day In the NA rat
diet for 2 years

NA; 8 mg/kg/day In the NA dog
diet for 90 days

NA; 8 mg/kg/day In the NA dog
diet for 90 days



NA; 1 ppm In diet for NA rat
27 weeks (0.05 mg/kg/day)

NA; 1 ppm In diet for NA rat
27 weeks (0.05 mg/kg/day)

Update: ne. 1990
Effect of Concern Reference Dose Uncertainty Factor
Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
NA; Increased ND 3E-2a NA 300
relative kidney
weight

NA; Internal ND 8E-2 NA 100
hemorrhage,
mortality

NA; Internal ND 8E-3a NA 1000
hemorrhage,
mortality


NA; liver lesions ND 5E-4 NA 100


NA; liver lesions NO 5E-4a NA 100
(also see Table B)


Reference
Inhalation/Oral
U.S. EPA. 1990/
Paynter et al..
1960; U.S. EPA,
1984. 1990
U.S. EPA, 1990/
Rhodla Inc.,
1969; U.S. EPA.
1984, 1990
U.S. EPA, 1990/
Rhodla Inc.,
1969; U.S. EPA.
1984, 1990

U.S. EPA, 1984/
Laug et al.,
1950; U.S. EPA,
1990
U.S. EPA. 19B4/
Laug et al.,
1950; U.S. EPA,
1988, 1990
Decabromodlphenyl ether
(Decabromodlphenyl
subchronlc (RfDs)





chronic (RfD)





oxide)
NA; 1.0 mg/kg/day In NA rat
the diet for 2 years





NA; 1.0 mg/kg/day In NA rat
the diet for 2 years




NA; liver ND 1E-2 NA 100
enlargement





NA; liver ND 1E-2* NA 100
enlargement (also
see Table B)



U.S. EPA, 1987/
Koclba et al..
1975; Norrls
et al., 1973,
1975; U.S. EPA,
1987; U.S. EPA,
1990
U.S. EPA. 1987/
Koclba et al..
1975; Norrls et
al., 1973, 1975;
U.S. EPA, 1987;
U.S. EPA. 1990
0059h
                                                                             A-28
                                                                                                                                                  07/12/90

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Compound

Dlazlnon
subchronlc (RfDs)




chronic (RfD)




Olbenzofuran
1.4-D1bromobenzene
subchronlc (RfDs)




chronic (RfD)




Dlbromochloromethane
subchronlc (RfDs)



chronic (RfO)



01-n-butyl phthalate
subchronlc (RfDs)




Exposure
Inhalation; Oral


NA; 1.0 ppm (0.09 mg/kg/
day) In the diet for
35-42 days


NA; 1.0 ppm (0.09 mg/kg/
day) 1n the diet for
35-42 days




NA; 10 mg/kg/day by
gavage for 45 or 90
days


NA; 10 mg/kg/day by
gavage for 45 or 90
days



NA; 30 mg/kg/day by
gavage. 5 days/week for
13 weeks (21 mg/kg/day)

NA; 30 mg/kg/day by
gavage, 5 days/week for
13 weeks (21 mg/kg/day)


NA; 0.25X of diet
for 52 weeks
(125 mg/kg/day)
(89 mg/kg/day)
Update: e. 1990
Species Effect of Concern Reference Dose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)

NA rat NA; Inhibition NO 9E-4 NA 100
of plasma chol-
Inesterase
activity

NA rat NA; Inhibition NO 9E-49 NA 100
of plasma chol-
Inesterase
activity

DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT1

NA rat NA; liver weight NO 1E-1 NA 100
and liver enzymes



NA rat NA; liver weight NO lE-2a NA 1000
and liver enzymes




NA rat NA; liver ND 2E-1 NA 100
lesions


NA rat NA; liver ND 2E-2a NA 1000
lesions

(also see Table B)

NA rat NA; mortality ND 1E+0 NA 100




Reference
Inhalation/Oral


U.S. EPA, 1984/
Davles and
Holub. 1979.
1980a.b;
U.S. EPA. 1984
U.S. EPA, 1984/
Davles and
Holub, 1979,
1980a,b;
U.S. EPA, 1984
U.S. EPA. 1987

U.S. EPA, 1990/
Carlson and
Tardlff. 1977;
U.S. EPA, 1984.
1990
U.S. EPA, 1990/
Carlson and
Tardlff, 1977;
U.S. EPA, 1984,
1990

U.S. EPA, 1990/
NTP. 1985;
U.S. EPA. 1985,
1989, 1990
U.S. EPA, 1990/
NTP. 1985;
U.S. EPA, 1985.
1989, 1990

U.S. EPA, 1987/
Smith. 1953;
U.S. EPA, 1987

0059h
A-29
07/12/90

-------


Compound
chronk (RfD)
1.2-Dkhlorobenzene
subchronk (RfDs)
chronk (RfD)

1.4-Dkhlorobenzene
(p-dkhlorobenzene)
subchronk (RfDs)
chronic (RfD)
Dkhlorobutenes
Dkhlorodlf luoromethane
subchronk (RfDs)
chronk (RfD)

Exposure Species
Inhalation; Oral Inhalation Oral
NA; 0.25X of diet NA rat
for 52 weeks
(125 mg/kg/day)
290 mg/m3 7 hours/day, rat rat
5 days/week for up to 7
months (44 mg/kg/day);
125 mg/kg/day. 5 days/
week for 13 weeks
290 mg/m3 7 hours/day. rat rat
5 days/week for up to 7
months (44 mg/kg/day);
125 mg/kg/day. 5 days/
week for 13 weeks
(89 mg/kg/day)

75 ppm (454.6 mg/m3) rat NA
5 hours/day. 5 days/week
for 76 weeks; NA
75 ppm (454.6 mg/m3) rat NA
5 hours/day. 5 days/week
for 76 weeks; NA
DATA
4136 mg/m3, 8 hours/ guinea dog
day. 5 days/week for pig
6 weeks (482.3 mg/kg/
day); 90 mg/kg/day
for 90 days
4136 mg/m3. 8 hours/ guinea rat
day. 5 days/week for pig
6 weeks (482.3 mg/kg/
day); 15 mg/kg/day
for 2 years
Update: 'e, 1990
Effect of Concern Reference Dose Uncertainty Factor
Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
NA; mortality! ND 1E-1* NA 1000
decreased body 2E*0 (4E-1) 9E-1 100 100
weight gain; liver
effects (also see
Table B)
decreased body 2E-1 (4E-2) 9E-23'1 1000 1000
weight gain;
liver effects
(also see
Table B)


liver and kidney 7E-1 ND 100 NA
effects; NA
liver and kidney 7E-ll NO 100 NA
effects (also see
Table B)
INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT (CANCER: SEE TABLE B)
lung and liver 2E»0 (5E-1) 9E-1 1000 100
lesions; none
lung and liver 2E-1 (5E-2) 2E-la 10.000 100
lesions; depressed
body weight gain

Reference
Inhalation/Oral
U.S. EPA, 1987/
Smith, 1953;
U.S. EPA, 1987
1990
Holllngsworth
et al.. 1958;
U.S. EPA. 1987/
NTP, 1985; U.S.
EPA. 1987, 1990
Holllngsworth
et al.. 1958;
U.S. EPA. 1987/
NTP. 1985: U.S.
EPA. 1987. 1990


R1ley et al..
1980/U.S. EPA.
1987
Rlley et al.,
1980/U.S. EPA.
1987
U.S. EPA, 1987
Prendergast
et al.. 1967;
U.S. EPA. 1987/
Clayton. 1967;
U.S. EPA, 1987
Prendergast
et al.. 1967;
U.S. EPA, 1987/
Sherman, 1974;
U.S. EPA. 1982.
1987. 1990
0059h
                                                                             A-30
                                                                                                                                                  07/12/90

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Exposure Species
Compound Inhalation; Oral Inhalation Oral
1,1-Dlchloroelhane
subchronlc (RfOs) 500 ppm (2025 mg/m3) cat rat
6 hours/day. 5 days/week
for 13 weeks (138 mg/kg/
day): 500 ppm (2025
mg/m3) 6 hours /day,
5 days/week for 13 weeks
chronic (RfD) 500 ppm (2025 mg/m3) cat rat
6 hours/day, 5 days/week
for 13 weeks (138 mg/kg/
day): 500 ppm (2025
mg/m3) 6 hours/day,
C riauc /unok fnr It uppkc
Update: 'e, 1990
Effect of Concern Reference Dose Uncertainty Factor
Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
kidney damage; none 5E»0 (1E+0) 1E+0 100 100
kidney damage; none 5E-1 (1E-1) 1E-19 1000 1000
(also see Table B)

Reference
Inhalation/Oral
Hofmann et al.,
1971; U.S. EPA,
1984/Hofmann
et al.. 1971;
U.S. EPA. 1983,
Hofmann et al.,
1971; U.S. EPA,
1984/Hofmann
et al.. 1971;
U.S. EPA. 1983,
1984
1.1-Dlchloroethylene
  subchronlc (RfDs)
                        (  mg/kg/day)
NA; 50 ppm In drinking
water for 2 years
(9 mg/kg/day)
NA
rat      NA;  liver lesions       ND
                                                            9E-3
NA      1000    U.S. EPA. 1984/
                Quasi et al.,
                1983; U.S.  EPA,
                1988, 1990
chronic (RfD)
1 ,2-c-Dlchloroelhylene
subchronlc (RfDs)
chronic (RfD)
1,2-t-Dlchloroethylene
subchronlc (RfDs)
chronic (RfO)
NA; 50 ppm In drinking NA
water for 2 years
(9 mg/kg/day)
NA; gavage for 90 days NA
(32 mg/kg/day)
NA; gavage for 90 days NA
(32 mg/kg/day)
NA; 0.1 mg/l In NA
drinking water for 90
days (17 mg/kg/day)
NA; 0.1 mg/t In NA
drinking water for 90
days (17 mg/kg/day)
rat NA; liver lesions ND
(also see Table B)
rat NA; decreased ND
hematocrlt and
hemoglobin
rat NA; decreased ND
hematocrlt and
hemoglobin
mouse NA; Increased ND
serum alkaline
phosphatase
mouse NA; Increased ND
serum alkaline
phosphatase
	 :— «i 	
9E-3Z NA 1000 U.S. EPA. 1984/
Quasi et al.,
1983; U.S. EPA,
1988. 1990
1E-1 NA 300 U.S. EPA. 1984/
HcCauley et al.,
n.d.; U.S. EPA,
1984, 1990
1E-2J NA 3000 U.S. EPA, 1984/
HcCauley et al.,
n.d.; U.S. EPA,
1984. 1990
2E-1 NA 100 U.S. EPA. 1984/
Barnes et al.,
1985; U.S. EPA,
1990
2E-2a NA 1000 U.S. EPA, 1984/
Barnes et al.,
1985; U.S. EPA.
1990
0059h

-------
                                                                     Update:    ae, 1990
Compound
2,4-D1chlorophenol
subchronlc (RfDg)
chronic (RfD)
Olchlorophenol. 2,3-
2.6-. 3.4- and 3.5-
2.4-D1chlorophenoxy
acetic acid (2.4-0)
subchronlc (RfOs)
chronic (RfO)
Olchloroprop
Dlchloropropanes (1,
1.3-01chloropropene
subchronlc (RfOs)
chronic (RfD)
Exposure Species
Inhalation; Oral Inhalation Oral
NA; 3 ppm In drinking NA rat
water for 2 generations
(0.3 mg/kg/day)
NA; 3 ppm In drinking NA rat
water for 2 generations
(0.3 mg/kg/day)
. 2.5-. DATA
NA; 1.0 mg/kg/day In NA rat
diet for 91 days
NA; 1.0 mg/kg/day In NA rat
diet for 91 days
DATA
1-. 1.2-. 1.3-. 2.2-) DATA
(Telone II)
10 ppm (45.4 mg/m3) rat rat
6 hours/day, 5 days/week
for 13 weeks; 3 mg/kg/
day In the diet for
90 days
10 ppm (45.4 mg/m3); rat rat
6 hours/day. 5 days/week
for 13 weeks; 3 mg/kg/day
In the diet for 90 days
Effect of Concern Reference Dose Uncertainty Factor
Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
NA; Inrnune function ND 3E-3 HA 100
NA; limune function ND 3E-3« NA 100
INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA; hematologlc NO 1E-2 NA 100
hepatic and renal
toxldty
NA; hematologlc ND 1E-2* NA 100
hepatic and renal
toxldty
INADEQUATE FOR QUANTITATIVE RISK ASSESSHENT9
INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT (also see Table B)
degeneration changes 1E-2 3E-3 100 1000
In nasal mucosa;
Increased organ weight
degenerative changes 1E-2 3E-4a 100 10.000
In nasal mucosa;
Increased organ
weights (also see
Table B)
Reference
Inhalation/Oral
U.S. EPA.
1987a.b/Exon and
Koller. 19B5;
U.S. EPA.
1987a.b. 1990
U.S. EPA.
1987a.b/Exon and
Koller. 1985;
U.S. EPA. 1986
1987a,b, 1990
U.S. EPA. 1987
NA/Dow Chemical
Co.. 1983; U.S.
EPA. 1990
NA/Dow Chemical
Co., 1983; U.S.
EPA. 1990
U.S. EPA. 1984
U.S. EPA, 1985
Stott et al..
1982; U.S. EPA.
1989/Dow
Chemical Co..
1973; U.S. EPA
1989. 1990
Stott et al..
1982; U.S. EPA
1989/Dow
Chemical Co.,
1973; U.S. EPA
1989. 1990
0059h
                                                                              A-32
                                                                                                                                                   07/12/90

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                                                                     Update:
                                                        •e.  1990
Compound
Exposure
Inhalation; Oral
Soecles
Inhalation Oral
Effect of Concern Reference Dose Uncertainty Factor
Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (nig/kg/day)] (mg/kg/day)
Reference
Inhalation/Oral
Olcyclopentadlene
  subchronlc (RfOs|
  chronic (RfD)
Oleldrln
  subchronlc (RfOs)
1 ppm (5.4 mg/m3).        rat
6 hours/day, 5 days/
week for 90 days (0.61
mg/kg/day); 690 ppm In
diet for 3 generations
(32 mg/kg/day for males)

1 ppm (5.4 mg/m3).        rat
6 hours/day. 5 days/
week for 90 days (0.61
mg/kg/day); 690 ppm In
diet for 3 generations
(32 mg/kg/day for males)
NA; 0.1 ppm In diet for   NA
2 years (0.005 mg/kg/day)
rat
kidney dysfunction;
none
2E-3 (6E-4)
                                                            rat
         kidney dysfunction;
         none
                       2E-4 (6E-5)
rat      NA; liver lesions      NO
3E-1        1000      100    Dodd et al..
                             1982; U.S.  EPA,
                             1987/LHton
                             Blonetlcs.  1980;
                             U.S. EPA. 1987
                  3E-2      10,000     1000    Dodd et  al.,
                                               1982;U.S.  EPA,
                                               1987/LHton
                                               Blonetlcs.  1980;
                                               U.S. EPA,  1987
                                         5E-5          NA      100     U.S.  EPA.  19B7/
                                                                      Walker  et  al..
                                                                      1969; U.S.  EPA.
                                                                      1990
chronic (RfD)
•
N.N-Dlethylanlllne
Dlethylene glycol
monoethyl ether
subchronlc (RfDs)
chronic (RfD)
Dlethylformamlde
subchronlc (RfDs)
NA; 0.1 ppm In diet for NA
2 years (0.005 mg/kg/day)

NA; diet provided 500 NA
mg/kg/day for 90 days
NA; 0.2X In drinking NA
water (200 mg/kg/day)
for 2 years
NA; 546 Pg/day (1.56 NA
mg/kg/day) In diet x
5 days/week for 73 weeks
rat NA; liver lesions ND 5E-5a
(Cancer: see
Table B)
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
rat NA; Impaired renal ND 5E+0
function. Increased
testes weight
rat NA; kidney hlsto- ND 2E*0
pathology
rat NA; no effect ND 1.1E-1
NA 100 U.S. EPA, 1987/
Walker et al.,
1969; U.S. EPA.
1990
U.S. EPA, 1987
NA 100 U.S. EPA. 1984/
Hall et al..
1966; U.S. EPA.
1984
NA 100 U.S. EPA, 1984/
Smyth et al.,
1964; U.S. EPA.
1984
NA 100 U.S. EPA. 1986/
Argus et al.,
1965; U.S. EPA.
1986
ni/19/an
0059h

-------
                                                                    Update:   "—. 1990
Compound
chronic (RfO)
l,2-D1ethylhydrai1ne
Dlethyl-p-nltrophenyl
phosphate
(paraoxon)
Dlethyl phthalate
subchrontc (RfDs)
chronic (RfD)
Olmethoate
subchronlc (RfDs)

chronic {RfD}

N.N-D1methylan111ne
subchronlc (RfDs)
chronic (RfD)
Exposure Species
Inhalation; Oral Inhalation Oral
NA; 546 wg/day (1.56 NA rat
mg/kg/day) In diet x
5 days/week for 73 weeks
DATA
DATA
NA; IX In diet for NA rat
16 weeks
(750 mg/kg/day)
NA; IX In diet for NA rat
16 weeks
(750 mg/kg/day)
NA; 1 ppm (0.05 mg/kg/ NA rat
day) In diet for 2 years

NA; 1 ppm (O.OS mg/kg/ NA rat
day) In diet for 2 years

NA; 31.25 mg/kg/day by NA rat
gavage x 5/7 days for
13 weeks
NA; 31.25 mg/kg/day by NA rat
gavage x 5/7 days for
13 weeks
Effect of Concern Reference Dose Uncertainty factor
Inhalation; Oral Inhalation Oral innaianon Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
NA; no effect NO 1.1E-1 MA 100
INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA; reduced ND 8E+0 NA 100
terminal body
weight
NA; reduced NO 8E-1« NA 1000
terminal body
weight1
NA; brain chol- ND 2E-4 NA 300
Inesterase
Inhibition

NA; brain chol- NO 2E-4* NA 300
Inesterase
Inhibition

NA; splenomegaly ND 2E-2 NA 1000
and splenic
hemoslderosls
NA; splenomegaly ND 2E-3* NA 10,000
and splenic
hemoslderosls
• it
Reference
Inna lat ion/ura i
U.S. EPA. 1986/
Argus et al.,
1965; U.S. EPA,
1986
U.S. EPA, 1984
U.S. EPA. 1989
U.S. EPA. 1987/
Brown et al.,
1978; U.S. EPA.
1987
U.S. EPA, 1987/
Brown et al.,
1978; U.S. EPA,
1967. 1990
U.S. EPA, 1985/
American
Cyanlmld Co.,
1986; U.S.
EPA, 1990
U.S. EPA. 1985/
American
Cyanlmld Co..
1986; U.S. EPA.
1990
U.S. EPA. 1986/
Abdo et al..
1984; U.S. EPA.
1990
U.S. EPA, 1986/
Abdo et al.,
1984; U.S. EPA.
1990
07/12/90
0059h

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                                                                     Update:     e. 1990
Compound
N.N-Dlmethylformamlde
subchronlc (RfDs)
chronic (RfD)
Exposure
Inhalation; Oral
NA; 540 ppm (96 mg/kg/
day) In diet for 119
days
NA; 540 ppm (96 mg/kg/
day) 1n diet for 119
days
Species Effect of Concern
Inhalation Oral Inhalation; Oral
NA mouse NA; Increased
liver weight
NA mouse NA; Increased
liver weight
Reference
Inhalation
[mg/m3 (nig/kg/day)]
NO
ND
Dose Uncertainty Factor
Oral Inhalation Oral
(mg/kg/day)
1E+0 NA 100
1E-1 NA 1000
Reference
Inhalation/Oral
U.S. EPA. 1986/
Beccl et al.,
1983; U.S. EPA.
1986
U.S. EPA, 1986/
Beccl et al.,
1983; U.S. EPA.
1986
Dlmethylphenols (2.3-. 2.5-)
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
             (Cancer:  see Table B)
                                                                                                                                             U.S.  EPA. 1986
1,4-uinieiny ipneno i
subchronlc (RfOs) NA; 50 mg/kg/day by NA
gavage for 90 days

chronic (RfD) NA; 50 mg/kg/day by NA
gavage for 90 days


2.6-D1methylphenol
subchronlc (RfDs) NA; 0.6 mg/kg/day for NA
8 months

chronic (RfO) NA; 0.6 mg/kg/day for NA
8 months



mouse NA; neurological ND
signs and hema to-
logical changes

mouse NA; neurological ND
signs and hema to-
logical changes


rat NA; effects on ND
blood pressure,
weight gain and
hlstologlcal appear-
ance of several organs
rat NA; effects on ND
blood pressure,
weight gain and
hlstologlcal appear-
ance of several organs
2E-1 NA 300 U.S. EPA. 1986/
American B1o-
genlcs, 1989;
U.S. EPA, 1986.
1990
2E-2J NA 3000 U.S. EPA, 1986/
American Blo-
genlcs. 1989;
U.S. EPA, 1986,
1990
6E-3 NA 100 U.S. EPA, 19B7/
Veldre and
Janes, 1979;
U.S. EPA. 1987.
1990
6E-4* NA 1000 U.S. EPA. 1987/
Veldre and
Janes, 1979;
U.S. EPA, 1987,
1990
0059h
                                                                             A-35
                                                                                                                                                  07/12/90

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Compound
3,4-Dlmethylphenol
subchronk (RfOs)
chronic (RfD)
Dimethyl phthalate
subchronk (RfOs)
chronic (RfD)
Dimethyl terephthalate
subchronk (RfDs)
chronic (RfD)
N.N-Olmethylurea
m-Dlnltrobenzene
subchronk (RfDs)
chronic (RfD)

Exposure
Inhalation; Oral
NA; 1.4 mg/kg/day
for 8 months
NA; 1.4 mg/kg/day
for 8 months
NA; 1000 mg/kg/day
In diet for 2 years
NA; 1000 mg/kg/day
In diet for 2 years
NA; 2500 ppm
(125 mg/kg/day) In
diet for 103 weeks
NA; 2500 ppm
(125 mg/kg/day) In
diet for 103 weeks

NA; 3 ppm (0.40 mg/kg/
day) In drinking water
for 16 weeks
NA; 3 ppm (0.40 mg/kg/
day) In drinking water
for 16 weeks

Species
Inhalation Oral
NA rat
NA rat
NA rat
NA rat
NA rat
NA rat
DATA
NA rat
NA rat
Update: e, 1990
Effect of Concern Reference Do
Inhalation; Oral Inhalation
[mg/m3 (mg/kg/day)]
NA; reduced growth. NO
Internal lesions
NA; reduced growth. NO
Internal lesions
NA; minor effect on NO
growth; some nephri-
tic Involvement
NA; minor effect on NO
growth; some nephri-
tic Involvement
NA; chronic NO
kidney Inflam-
mation
NA; chronic ND
kidney Inflam-
mation
INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA; Increased ND
splenic weight
NA; Increased ND
splenic weight

se Uncertainty Factor
Oral Inhalation Oral
(mg/kg/day)
1E-2 NA 100
1E-33 NA 1000
1E+0 NA 100
1E*09 NA 100
1E-1 NA 1000
1E-13 NA 1000

IE -3 NA 300
lE-4a NA 3000

Reference
Inhalation/Oral
U.S. EPA. 19B7/
Veldre and
Janes, 1979;
U.S. EPA, 1987.
1990
U.S. EPA. 1987/
Veldre and
Janes. 1979;
U.S. EPA. 1987,
1990
NA/Lehman, 1955;
U.S. EPA. 1987
NA/Lehman. 1955;
U.S. EPA, 1987
U.S. EPA. 1984/
NCI. 1979;
U.S. EPA. 1990
U.S. EPA, 1984/
NCI, 1979;
U.S. EPA. 1990
U.S. EPA, 1984
U.S. EPA. 1985/
Cody et al.,
1981; U.S. EPA,
1990
U.S. EPA, 1985/
Cody et al..
1981; U.S. EPA.
1990
0059h
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07/12/90

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•
Compound
Dlnltrobenzenes (o-.
subchronk (RfDs)
chronic (RfO)
2.6-Dlnltro-p-cresol
4.6-Dlnltro-o-cresol
2.4-Dlnltrophenol
subchronk (RfDs)
chronic (RfD)
Dlnltrophenols (2.3-;
Dlnltrotoluenes (2.3-
01-n-octyl phthalate
subchronk (RfOs)
chronic (RfD)
Olnoseb
subchronk (RfDs)

Exposure
Inhalation; Oral
P-)
NA; 3 ppm (0.40 mg/kg/
day) In drinking water
for 16 weeks
NA; 3 ppm (0.40 mg/kg/
day) In drinking water
for 16 weeks


NA; 2 mg/kg/day. thera-
peutic use
NA; 2 mg/kg/day. thera-
peutic use
2.5-; 2.6-; 3.5-)
; 2.4-; 2.5-; 2.6-; 3.4-)
NA; 175 mg/kg/day In
diet for 7-12 months
NA; 175 mg/kg/day In
diet for 7-12 months
NA; 1 mg/kg/day In diet
for 29 weeks
Update: e. 1990
Species Effect of Concern Reference Dose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
NA rat NA; Increased ND 4E-3 NA 100
splenic weight
NA rat NA; Increased ND 4E-4 NA 1000
splenic weight
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT^
NA human NA; cataract ND 2E-3 NA 1000
NA human NA; cataract ND 2E-3a NA 1000
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT (Cancer: see Table B)
NA rat NA; elevated kidney ND 2E-2 NA 1000
and liver weights;
Increased SGOT and
SGPT
NA rat NA; elevated kidney NO 2E-2 NA 1000
and liver weights;
Increased SGOT and
SGPT
NA rat NA; decreased ND lE-3bb NA 1000
fetal weight

Reference
Inhalation/Oral
U.S. EPA, 1985/
Cody et al.,
1981; U.S. EPA,
1985
U.S. EPA, 1985/
Cody et al.,
1981; U.S. EPA,
1985
U.S. EPA, 1984
U.S. EPA. 1986/
U.S. EPA, 1986
U.S. EPA. 1990/
Homer, 1942;
U.S. EPA. 1984,
1990
U.S. EPA. 1990/
Homer, 1942;
U.S. EPA, 1984.
1990
U.S. EPA. 1984
U.S. EPA. 1986
NA/Plekacz.
1971; U.S. EPA,
1987
NA/Plekacz.
1971; U.S. EPA,
1987
U.S. EPA, 1984/
Dow Chemical
Co., 1981;
U.S. EPA. 1990
0059h
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07/12/90

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                           HtALIH mtllb ASbtbbMLNIb  SUMMARY  lABLt A: SUBCHKONIC AND CHRONIC 10X1CIIY (OIHLR 1HAN CARCINOGENICIIY)
                                                                     Update:      e.  1990
Exposure Species Effect of Concern Reference Dose Uncertainty Factor Reference
Compound Inhalation; Oral Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral Inhalation/Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
chronic (RfD) NA; 1 mg/kg/day In diet NA
for 29 weeks
I.N-Dlphenylamlne
subchronlc (RfDs) NA: 0.0170 (2.5 mg/kg/ NA
day) 1n diet for 2 years
chronic (RfD) NA: 0.0170 (2.5 mg/kg/ NA
day) In diet for 2 years
rat NA; decreased ND
fetal weight
dog NA; decreased ND
body weight
gain and
Increased liver
and kidney
weights
dog NA; decreased ND
body weight
gain and
Increased liver
1E.3a,l.bb NA 1000 U.S. EPA, 1984/
Dow Chemical
Co.. 1981;
U.S. EPA, 1990
2.5E-2 NA 100 U.S. EPA, 19B5/
Thomas et al..
1967; U.S. EPA,
1990
2.5E-23 NA 100 U.S. EPA. 1985/
Thomas et al.,
1967; U.S. EPA,
1990
Direct Llghtfast Blue

Olsulfoton
  subchronlc (RfDs)
  chronic (RfD)
Endosulfan
  subchronlc (RfDs)
  chronic (RfD)
NA; 0.8 ppm In diet for   NA
2 years (0.04 mg/kg/day)
NA; 0.8 ppm In diet for   NA
2 years (0.04 mg/kg/day)
NA; 3 ppm 1n diet In      NA
2-generaUon reproduc-
tive study
(0.15 mg/kg/day)
NA; 3 ppm In diet In      NA
2-generatlon reproduc-
tive study
(0.15 mg/kg/day)
                                             and kidney
                                             weights  (also see
                                             Table B)

                                     DATA  INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
rat      NA;  chollnesterase     ND
         Inhibition,  optic
         nerve degeneration
rat      NA;  chollnesterase     ND
         Inhibition,  optic
         nerve degeneration
rat      NA;  mild kidney        ND
         lesions
rat      NA; mild kidney        ND
         lesions
                                                                               U.S. EPA. 1987
4E-S          NA      1000    U.S.  EPA.  1990a/
                              Nobay chemical,
                               1985; U.S.  EPA.
                              1990a.b

4E-5a         NA      1000    U.S.  EPA.  1990a/
                              Nobay chemical,
                              1985; U.S.  EPA.
                              1990a.b
2E-4          NA      1000    U.S.  EPA,  1987/
                              Huntlngton
                              Research Center,
                              1984; U.S. EPA.
                              1987. 1990

5E-5a         NA      3000    U.S.  EPA.  1987/
                              Huntlngton
                              Research Center.
                              1984; U.S. EPA.
                              1987. 1990
0059h
                                                     A-38
                                                                                    07/12/90

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Update: ?. 1990
Compound
Endothall
subchronlc (RfDs)
chronic (RfO)
Endrln
subchronlc (RfDs)
chronic (RfO)
Eplchlorohydrln
subchronlc (RfOs)
chronic (RfO)
Exposure
Inhalation; Oral
NA; 100 ppm dlsodlum
endothall In the diet
for 2 years (2 mg
endothall lon/kg/day)
NA; 100 ppm dlsodlum
endothall In the diet
for 2 years (2 mg
endothall 1on/kg/day)
NA; 1 ppm In diet for
18 months
(0.045 mg/kg/day)
NA; 1 ppm In diet for
>2 years
(0.025 mg/kg/day)
5 ppm. 6 hours/day,
5 days/week for 87-88
days (HEC=0.25 mg/m3);
10 ppm (37.8 mg/m3).
6 hours/day, 5 days/week
for 136 weeks
5 ppm. 6 hours/day,
5 days/week for 87-88
days (HEC=0.25 mg/m3);
10 ppm (37.8 mg/m3).
6 hours/day. 5 days/week
for 136 weeks
Species Effect of Concern Reference Dose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
NA dog NA; stomach effect NO 2E-2 NA 100
NA dog NA; stomach effect ND 21-2* NA 100
NA dog NA; Increased ND 5E-4 NA 100
relative organ
weights
NA dog NA; convulsions ND 3E-4a NA 100
and liver lesions
mouse rat nasal turblnate 3E-3 2E-2 100 100
Injury; kidney damage
mouse rat nasal turblnate 3E-4J 2E-3a>b 1000 1000
Injury; kidney damage
(also see Table B)
Reference
Inhalation/Oral
U.S. EPA, 1989/
Keller. 1965;
Pennwalt Agchem,
n.d; U.S. EPA,
1989. 1990
U.S. EPA. 1989/
Keller, 1965;
Pennwalt Agchem,
n.d.; U.S. EPA,
1989, 1990
U.S. EPA, 1987/
Treon et al.,
1955; U.S. EPA,
1985, 1987.
1990
U.S. EPA, 1987/
CBI; U.S. EPA,
1985, 1987,
1990
Quast et al.,
1979/Laskln et
al., 1980; U.S.
EPA, 1984, 1990
Quast et al.,
1979/Laskln et
al., 1980; U.S.
EPA, 1984, 1990
EPTC (see S-Ethyl dlpropylthlocarbamate)
Ethoprop

DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
U.S. EPA. 1984
0059h
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07/12/90

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                           HtALIH imilS ASStSSMlNIS SUMMARY 1ABLE A: SUBCHRO*"" AND CHRONIC 10XICIIY (OTHLR THAN CARCINOGENICITY)
                                                                      Update:       ,  1990
Exposure
Compound Inhalation; Oral
2-Ethoxyethanol
subchronlc (RfDs) 10 ppm (37 mg/m3)
6 hours/day on days 6-15
of gestation (6.B mg/kg/
day); SO ul (46.6 mg/kg/
day) on days 1-21 of
gestation
chronic (RfO) 100 ppm (369 mg/m3)
6 hours/day, 5 days/
week for 13 weeks
(49.9 mg/kg/day)
500 mg/kg 5 days/week
for 103 weeks (357
mg/kg/day)
2-Ethoxyethanol acetate
subchronlc (RfDs) NA; 50 ppm (30.1 mg/kg)
x 6 hours/day on gesta-
tlonal day 6-18
chronic (RfD) NA; 50 ppm (30.1 mg/kg)
x 6 hours/day on gesta-
tlonal day 6-18
2-Ethoxyethanol esters
2-ethoxyethanol acrylate,
2-ethoxyethyl methacrylate,
2-ethoxyethanol phosphated.
2-ethoxyethyl dodecanoate)
Ethyl acetate
subchronlc (RfDs) NA; 900 mg/kg/day by
gavage for 90 days
chronic (RfD) NA; 900 mg/kg/day by
gavage for 90 days
Species Effect of Concern Reference Dose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)) (mg/kg/day)
rat rat fetotoxlclty; 2E-1 (7E-2)bb 5E-lbb 100 100
fetotoxlclty
rat rat altered hemotology; 2E-1 (5E-2) 4E-1 1000 1000
reduced body weight
(also see Table B)
NA rat NA; decreased ND 3E-lb-bb NA 100
ossification
NA rat NA; decreased ND 3E-lb.bb NA 100
ossification
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA rat NA; mortality. ND 9E+0 NA 100
body weight
loss
NA rat NA; mortality, ND 9E-la NA 1000
body weight loss
(also see Table B)
Reference
Inhalation/Oral
Doe. 1984;
U.S. EPA, 1984/
Stenger et al..
1971; U.S. EPA.
1984
Bar bee et al..
1984; U.S. EPA,
1984/Nelnlck,
1984; U.S. EPA.
1985
U.S. EPA, 1985/
Union Carbide,
1984; U.S. EPA,
1985
U.S. EPA, 1985/
Union Carbide,
1984; U.S. EPA,
1985
U.S. EPA, 1985
U.S. EPA, 1990/
U.S. EPA,
1986a.b. 1990
U.S. EPA, 1990/
U.S. EPA,
1986a.b. 1990
0059h
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07/12/90

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Update: e. 1990
Compound
n-Ethylanlllne
Cthylbenzene
subchronlc (RfOs)
chronk (RfD)
Ethyl chloride
Exposure
Inhalation; Oral

NA; 136 mg/kg 5
days/week for 182
days (97.1 mg/kg/day)
NA; 136 mg/kg 5
days/week for 182
days (97.1 mg/kg/day)

S-Ethyl dlpropylthlocarbamate
subchronlc (RfDs) NA; SO ppm In diet for
2 generations (2.5 mg/
kg/day)
chronic (RfO)
Ethylene cyanohydrln
subchronlc (RfOs)
chronic (RfD)
NA; 50 ppm In diet for
2 generations (2.5 mg/
kg/day)
NA; 30 mg/kg/day In
drinking water for
90 days
NA; 30 mg/kg/day In
drinking water for
90 days
Species Effect of Concern Reference Dose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA rat NA; hepatotoxlclty ND 1E»0 NA 100
and nephrotoxlclty
NA rat NA; hepatotoxlclty ND 1E-13 NA 1000
and nephrotoxlclty1
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA rat NA; degenerative ND 2.5E-2 NA 100
cardlomyopathy
NA rat NA; degenerative ND 2.5E-23 NA 100
cardlomyopathy
NA rat NA; decreased heart ND 3E-1 NA 100
and brain weights
NA rat NA; decreased heart ND 3E-1 NA 100
and brain weights
Reference
Inhalation/Oral
U.S. EPA. 1986
U.S. EPA. 19B4/
Wolf et al..
1956; U.S. EPA,
1984, 1986, 1990
U.S. EPA. 1984/
Wolf et al.,
1956; U.S. EPA.
1984. 1986, 1990
U.S. EPA, 1987
U.S. EPA, 1984/
PPG Industries,
1986; U.S. EPA.
1984, 1990
U.S. EPA. 1984/
PPG Industries,
1986; U.S. EPA.
1984, 1990
U.S. EPA, 1988/
Sauerhoff
et al.. 1976;
U.S. EPA, 1988
U.S. EPA, 1988/
Sauerhoff
et al.. 1976;
U.S. EPA. 1988
0059h
                                                                              A-41
07/12/90

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Compound
Ethylenedlamlne
subchronk (RfOs)
chronic (RfD)
Ethylene glycol
subchronk (RfDs)
chronic (RfO)
Ethylene glycol
monobutyl ether
subchronk (RfDs)
chronk (RfD)
Ethylene thlourea

Exposure
Inhalation; Oral
59 ppm (145 mg/m3)
7 hours/day. 5 days/week
for 30 days (25.8 mg/kg/
day); 3-month dietary
study with 50 mg/kg/day
ctliylcncdlaniliie dtliydro-
chlorlde (22.6 mg
ethylenedlaml ne/kg/day )
NA; 3-month dietary
study with 50 mg/kg/day
ethylenedlamlne dlhydro-
chlorlde (22.6 mg
ethylenedlamlne/kg/day)
NA; 200 mg/kg/day In
developmental toxlclty
NA; 200 mg/kg/day In
2-year dietary study
25 ppm (121 mg/m3)
6 hours/day, 5 days/
week for 13 weeks
(16 mg/kg/day); NA
25 ppm (121 mg/m3)
6 hours/day. 5 days/
week for 13 weeks
(16 mg/kg/day); NA

Update: ' -, 1990
Species Effect of Concern Reference Dose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
rat rat death, kidney 1E»0 (3E-1) 2E-1 100 100
and liver
lesions; liver
and hematologlc
changes
NA rat NA; liver and NO 2E-2 NA 1000
hematologlc
changes
NA rat NA; fetotoxlclty ND 2E*oN> NA 100
NA rat NA; mortality, ND 2E*0» NA 100
liver and kidney
effects
rat NA altered hematology; 6E-1 (2E-1) ND 100 NA
NA
rat NA altered hematology; 6E-2 (2E-2) ND 1000 NA
NA
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENTS
(also see Table B)

Reference
Inhalation/Oral
Pozzanl and
Carpenter, 1954;
U.S. EPA, 19867
Yang et al.,
1983; U.S. EPA,
1988
U.S. EPA. 1988/
Yang et al.,
1983; U.S. EPA,
1988
U.S. EPA, 1987/
Maronpot
et al.. 1963;
U.S. EPA.
1987a. 1990
U.S. EPA. 1987/
DePass et al..
1986a; U.S. EPA,
1987a. 1990
Dodd et al..
19B3/U.S. EPA.
1984
Dodd et al..
1983/U.S. EPA.
1984
U.S. EPA, 1984
0059h
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                            IIIMI.MI LI i LIU  (ijjLjjni.ui a junriMKi  IrtOLt H.  jUUUIKUNH  ANU IHKUN1L  IUX1L1K  (UIHtK I HAN LAKl INUbtNlU11)
                                                                        Update:      >,  1990
Compound
Ethyl ether
subchronlc (RfOs)




chronic (RfD)




Ethyl methacrylate
subchronlc (RfDs)





chronic (RfO)





Ethy.l toluene (o-, p
4-Ethyl-o-xylene
Fluoranthene
subchronlc (RfDs)


chronic (RfO)


Exposure
Inhalation; Oral

NA; 500 mg/kg/day for
90 days



NA; 500 mg/kg/day for
90 days




NA; 65 ppm (7.5 mg/kg/
day) methyl methacrylate
x 114.5/100.13 (molec-
ular weight ratio) In
drinking water for 2
years
NA; 65 ppm (7.5 mg/kg/
day) methyl methacrylate
x 114.5/100.13 (molec-
ular weight ratio) In
drinking water for 2
years
. m-)


NA; 125 mg/kg/day by
gavage for 90 days

NA; 125 mg/kg/day by
gavage for 90 days

Species Effect of Concern Reference Dose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)

NA rat NA; liver effects NO 5E+0 NA 100




NA rat NA; liver effects NO 5E-lJ NA 1000





NA rat NA; Increased NO 9E-2 NA 100
kidney weight




NA rat NA; Increased ND 9E-29 NA 100
kidney weight
(also see Table B)



DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT

NA mouse NA; nephropathy. ND 4E-1 NA 300
liver weight changes
hematologlcal changes
NA mouse NA; nephropathy, ND 4E-2J NA 3000
liver weight changes.
hematologlcal changes
Reference
Inhalation/Oral

U.S. EPA, 19B7/
American
Blogenlcs Corp.,
1986; U.S. EPA,
19B7
U.S. EPA, 1987/
American
Blogenlcs Corp.,
19B6; U.S. EPA.
1987

U.S. EPA, 1986/
Borzelleca
et al., 1964;
U.S. EPA, 1986


U.S. EPA. 1986/
Borzelleca
et al.. 1964;
U.S. EPA, 1986


U.S. EPA. 1984
U.S. EPA, 1984

U.S. EPA, 1988


U.S. EPA. 1988


0059h
                                                                                A-43
07/12/90

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                                                                      Update:   " ->e.  1990
Compound
Fluorene
subchronk (RfOs)

chronic (RfD)

Fluorides
subchronk (RfOs)

chronic (RfOs)

Flurldone
subchronk (RfDs)


chronk (RfO)


Folpet
subchronk (RfDs)

Exposure Soecles
Inhalation; Oral Inhalation Oral
NA; 12S mg/kg/day by NA mouse
gavage for 13 weeks

NA; 125 mg/kg/day by NA mouse
gavage for 13 weeks

NA; 0.06 mg fluoride/kg/ NA human
day In drinking water

NA; 0.06 mg fluoride/kg/ NA human
day In drinking water

NA; 200 pptn In the diet NA rat
for 2 years (B mg/kg/
day)

NA; 200 ppm In the diet NA rat
for 2 years (8 mg/kg/
day)

NA; 10 mg/kg/day In NA dog
capsules for 1 year

Fffprt of Concern Reference Dose Uncertainty Factor
Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
NA; hematologlcal ND 4E-1 NA 300
changes (decreased
RBC)
NA; hematologlcal NO 4E-2J NA 3000
changes (decreased
RBC)
NA: dental fluorosls ND 6E-2 NA 1
at higher levels

NA: dental fluorosls ND 6E-2a NA 1
at higher levels

NA; kidney and testes ND 8E-2 NA 100


NA; kidney and ND 8E-2* NA 100
and testes


NA; body weight ND 1E-1 NA 100
gain, blood
chemistry

Reference
Inhalation/Oral
U.S. EPA. 1989

U.S. EPA, 1989

U.S. EPA. 19B9/
Hodge, 1950;
U.S. EPA. 1989,
1990
U.S. EPA. 1989/
Hodge, 1950;
U.S. EPA, 1989.
1990
U.S. EPA. 1990/
Ell Lilly and
Co., 1980;
U.S. EPA. 1984
1990
U.S. EPA. 1990/
Ell Lilly and
Co.. 1980;
U.S. EPA. 1984
1990
U.S. EPA, 1990/
Chevron Chemical
Corp., 1986;
U.S. EPA, 1984,
1990
0059h
                                                                              A-44
                                                                                                                                                    07/12/90

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                                                                     Update:
.  1990
Compound
chronic (RfO)
Formaldehyde cyanohydrln
Formic acid
subchronk (RfDs)
cljronlc (RfO)
Furan
subchronk (RfOs)
chronic (RfD)
Furfural
subchronk (RfDs)
chronic (RfD)
Exposure
Inhalation; Oral
NA; 10 mg/kg/day In
capsules for 1 year

NA; 0.2X In drinking
water (200 mg/kg/day),
several generation study
NA; 0.2% In drinking
water (200 mg/kg/day).
several goneiatton study
NA; 2 mg/kg. 5 days/week
for 13 weeks (1.4
mg/kg/day)
NA; 2 mg/kg, 5 days/week
for 13 weeks (1.4
mg/kg/day)
20 ppm (77 mg/m3), 6
hours/day. 5 days/week
for 13 weeks (13 mg/kg/
day); 11 mg/kg, 5 days/
week for 13 weeks
(7.9 mg/kg/day)
20 ppm (77 mg/m3), 6
hours/day, S days week
for 13 weeks (13 mg/kg/
day); 11 mg/kg. S days/
week for 13 weeks
(7.9 mg/kg/day)
Soecles Effect of Concern Reference Dose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
NA dog NA; body weight ND U-la NA 100
gain, blood
chemistry
(also see Table B)
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA rat NA; decreased growth ND 2E*0 NA 100
NA rat NA; decreased growth ND 2E+0* NA 100
NA mouse NA; hepatic lesions ND 1E-2 NA 100
NA mouse NA; hepatic lesions ND lE-3a NA 1000
hamster rat olfactory degenera- 5E-1 (1E-1) 3E-2 100 300
tlon; hepatotoxklty
hamster rat olfactory degenera- 5E-2 (1E-2) 3E-3» 1000 3000
tlon; hepatotoxklty
Reference
Inhalation/Oral
U.S. EPA. 1990/
Chevron Chemical
Corp., 1986;
U.S. EPA. 1984,
1990
U.S. EPA. 1988
N A/Hal or ny,
1969; U.S. EPA,
1990
N A/Hal or ny.
1969; U.S. EPA.
1990
U.S. EPA. 1987/
SRI. 1982;
U.S. EPA. 1987
U.S. EPA, 1987/
SRI. 1982; U.S.
EPA. 1987, 1990
Feron et al.,
1979; U.S. EPA,
1988/SRI. 1981;
U.S. EPA, 1990
Feron et al.,
1979; U.S. EPA.
1988/SRI. 1981;
U.S. EPA. 1990
0059h
                                                                             A-45
                                                                                                                                                 07/12/90

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L ML m LI i LIU
                                                       surm«K I  IMDLL M.  bUdl-MKUNll  ANU  LHKUNK IUX1UII (UIHtK I HAN LAKUNUlitNlll 1 1 )
                                                                       Update:      \ 1990
Compound
Glycldaldehyde
subchronlc (RfDs)
chronic (RfDs)
Heptachlor
subchronlc (RfOs)
chronic (RfD)
n-Heptane
Hexabromobenzene
subchronlc (RfDs)
chronic (RfD)
Hexachlorobenzene
subchronlc (RfDs)
Exposure
Inhalation; Oral
10 pptn (29 mg/m3). 4
hours/day. 5 days/week
for 12 weeks (HCC. 3.5
rag/m3); 1.1 mg/kg/day
10 ppm (29 mg/m3). 4
hours/day. 5 days/week
for 12 weeks (NEC. 3.5
mg/m3); 1.1 mg/kg/day
NA; 3 ppm In diet for
2 years (0.15 mg/kg/day)
NA; 3 ppm In diet for
2 years (0.15 mg/kg/day)

NA; 40 ppm In the diet
for 12 weeks
(2 mg/kg/day)
NA; 40 ppm In the diet
for 12 weeks
(2 mg/kg/day)
NA; 1.6 ppm 1n diet for
130 weeks (O.OB mg/kg/
day)
Species Effect of Concern Reference Dose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
rat rat decreased body weight 1E-2 4E-3 300 300
and kidney effects;
decreased body weight
and kidney effects
rat rat decreased body weight 1E-3 4E-4* 3000 3000
and kidney effects;
decreased body weight
and kidney effects
(also see Table B)
NA rat NA; Increased liver ND 5E-4 NA 300
weight
NA rat NA; Increased liver ND 5E-4* NA 300
weight (also see
Table B)
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSNENT
NA rat NA; Induced ND 2E-2 NA 100
carboxylesterase
activity
NA rat NA; Induced ND 2E-3a NA 1000
carboxylesterase
activity
NA rat NA; liver and hema- ND 8E-4 NA 100
tologlc effects
Reference
Inhalation/Oral
Nine et al..
1961; U.S. EPA,
1989/Hlne et
al.. 1961; U.S.
EPA. 1989, 1990
Nine et al..
1961; U.S. EPA.
1989/Hlne et
al., 1961; U.S.
EPA. 1989, 1990
U.S. EPA. 1987/
Velslcol
Chemical, 1955;
U.S. EPA, 1990
U.S. EPA, 1987/
Velslcol
Chemical. 1955;
U.S. EPA. 1990
U.S. EPA, 1989/
U.S. EPA, 1989
U.S. EPA, 1990/
Nendoza et al.,
1977; U.S. EPA,
1984. 1990
U.S. EPA. 1990/
Nendoza et al.,
1977; U.S. EPA,
1984, 1990
U.S. EPA. 1984/
Arnold et al.,
1985; U.S. EPA,
1990
0059h
                                                  A-46
07/12/90

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                                                                     Update:
*. 1990
Compound
chronic (RfD)
Hexachlorobutadlene
subchronlc (RfDs)

chronic (RfD)

Hexachlorocyclohexane,
gamma (Llndane)
subchronlc (RFDS)
chronic (RfD)

Exposure Species
Inhalation; Oral Inhalation Oral
NA; 1.6 ppm In diet for NA rat
130 weeks (0.08 mg/kg/
day)
NA; 2-year dietary NA rat
study (0.2 mg/kg/day)

NA; 2-year dietary NA rat
study (0.2 mg/kg/day)


NA; 4 ppm In diet for NA rat
12 weeks (0.33 mg/kg/
day)
NA; 4 ppm 1n diet for NA rat
12 weeks (0.33 mg/kg
day)

Hexachlorocyclopentadlene
subchronlc (RfDs) 0.15 ppm (1.67 mg/m3) rat rat
6 hours/day. 5 days/
week for 13 weeks (0.2


chronic (RfD)



mg/kg/day); 10 mg/kg,
S days/week for 13
weeks (7.1 mg/kg/day)

0.15 ppm (1.67 mg/m3) rat rat
6 hours/day. 5 days/
week for 13 weeks (0.2
mg/kg/day); 10 mg/kg.
5 days/week for 13
weeks (7.1 mg/kg/day)

Effect of Concern Reference Dose Uncertainty Factor
Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
NA; liver and hema- ND 8E-4« NA 100
tologlc effects
(also see Table B)
NA; kidney toxlclty ND 2E-3 NA 100

NA; kidney toxlclty ND 2E-3a NA 100
(Cancer: see
Table B)


NA; liver and ND 3E-3 NA 100
and kidney toxlclty
NA; liver and ND 3E-4' NA 1000
kidney toxlclty
(Cancer: see
Table B)
respiratory tract 7E-4 (2E-4) 7E-2 100 100
lesions; fore-
stomach lesions


respiratory tract 7E-5 (2E-5) 7E-3a 1,000 1,000
lesions; fore-
stomach lesions



Reference
Inhalation/Oral
U.S. EPA. 1984/
Arnold et al.,
1985; U.S. EPA,
1990
U.S. EPA, 1984/
Koclba et al..
1977; U.S. EPA.
1990
U.S. EPA, 1984/
Koclba et al.,
1977; U.S. EPA.
1990

U.S. EPA. 1984/
Zoecon Corp.,
1983; U.S. EPA.
1990
U.S. EPA, 1984/
Zoecon Corp.,
1983; U.S. EPA.
1990
Battelle
Northwest
Laboratories,
1984; U.S. EPA.
1984/SRI. 1981;
Abdo et al.,
1984; U.S. EPA,
1990
Battelle
Northwest
Laboratories,
1984; U.S. EPA,
1984/SRI, 1981;
* L J _ —1 * 1
Abdo et al.,
1984; U.S. EPA,
1990
07/1 9/Qn
0059h

-------


Compound
Hexachloroethane
subchronk (RfOs)
chronic (RfO)
Hexachlorophene
subchronk (RfDs)
chronk (RfO)
Hexamethylenedlamlne
N-Hexane
subchronk (RfDs)
chronk (RfD)
2-Hexanone
Hydrogen sulflde
subchronk (RfOs)

Exposure
Inhalation; Oral
NA; 16-week dietary
study (1 mg/kg/day)
NA; 16-week dietary
study (1 mg/kg/day)
NA; 30 ppm In the diet
for 13 weeks (0.75 ing/
kg/day)
NA; 30 ppm In the diet
for 13 weeks (0.75 ing/
kg/day)

73 mg/m3 TWA for 1-12
years (occupational);
570 mg/kg/day
73 mg/m3 TWA for 1-12
years (occupational);
570 mg/kg/day

NA; 3.1 mg/kg/day In
dried greens for 105
days
Update: , 1990
Species Effect of Concern Reference Dose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
NA rat NA; kidney degenera- NO 1E-2 HA 100
tlon
NA rat NA; kidney degenera- NO 1E-33 NA 1000
tlon (also see
Table B)
NA dog NA; nervous NO 3E-3 NA 300
system effects
(also see
Table B)
NA dog NA; nervous NO 3E-4« NA 3000
system effects
(also see
Table B)
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
human rat neurotoxlclty; 2E-1 6E-1 300 1000
neuropathy or
testlcular atrophy
human rat neurotoxlclty; 2E-lJ 6E-1 300 10,000
neuropathy or
testlcular atrophy
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA pig NA; GI disturbance NO 3E-2 NA 100

Reference
Inhalation/Oral
U.S. EPA, 1987/
Gorzlnskl et
al., 1985; U.S.
EPA, 1989. 1990
U.S. EPA. 1987/
Gorzlnskl et
al., 1985; U.S.
EPA, 1989. 1990
U.S. EPA, 1990/
Nationwide Chem.
Corp. 1974; U.S.
EPA. 1986. 1990
1990
U.S. EPA. 1990/
Nationwide Chem.
Corp. 1974; U.S.
EPA. 1986, 1990
U.S. EPA, 1985
Sanagl et al..
1980; U.S. EPA,
1990/Krasavage
et al.. 1980;
U.S. EPA. 1989
Sanagl et al.,
1980; U.S. EPA.
1990/Krasavage
et al.. 1980;
U.S. EPA. 1989
U.S. EPA. 1989
NA/Uatterau et
al.. 1964-1965;
U.S. EPA, 1990
0059h
                                                                             A-48
                                                                                                                                                  08/01/90

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                           IllAL III HH Lib ASStSSMtNIS  bUMMAKY  IABU A: SUBCHRr " AND CHRONIC 10XICIIY (01HER THAN CARCINOGENICI1Y)
                                                                     Update:      e,  1990
Compound
chronic (RfO)
p-Hydroqulnone
subchronk (RfOs)
chronic (RfO)
Iron
Isobutyl alcohol
suchronlc (RfOs)
chronic (RfD)
Exposure
Inhalation; Oral
NA; 3.1 mg/kg/day In
dried greens for 105
days
NA; 300 mg/day for 3-5
months (4.29 mg/kg/day)
NA; 300 mg/day for 3-5
months (4.29 mg/kg/day)

NA; 316 mg/kg/day In the
diet for 13 weeks
NA; 316 mg/kg/day In the
diet for 13 weeks
Species Effect of Concern Reference Dose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
NA pig NA; GI disturbance 9E-4J 3E-3a NA 1000
NA human NA; hematologlcal ND 4E-1 NA 10
effects
NA human NA; hematologlcal ND 4E-2 NA 100
effects
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA rat NA; hypoactlvlty ND 3E*0 NA 100
and ataxla
NA rat NA; hypoactlvlty ND 3E-la NA 1000
and ataxla
Reference
Inhalation/Oral
NA/Watterau et
al., 1964-1965;
U.S. EPA, 1990
U.S. EPA. 1987/
Carlson and
Brewer, 1953;
U.S. EPA. 1987
U.S. EPA. 1987/
Carlson and
Brewer, 1953;
U.S. EPA. 1987
U.S. EPA. 1984
U.S. EPA, 1986a/
U.S. EPA,
1986a,b, 1990
U.S. EPA. 1986a/
U.S. EPA,
1986a,b, 1990
Isophorone
  subchronk (RfDs)
  chronic (RfD)
Isopropalln
NA; 90-day oral
(capsules) study
(150 mg/kg/day)
NA; 90-day oral
(capsules) study
(150 mg/kg/day).
NA
NA
dog      NA; kidney lesions     ND
dog      NA; kidney lesions
         (Cancer: see
         Table B)
ND
2E+0          NA       100    U.S.  EPA.  1987/
                              Rohm and Haas.
                              1972; NTP.  1986;
                              U.S.  EPA.  1990

2E-la         NA      1000    U.S.  EPA,  1987/
                              Rohm and Haas,
                              1972; NTP,  1986;
                              U.S.  EPA.  1990
subchronk (RfDs)
NA; 250 ppm In the diet NA
for 90 days (15 mg/kg/
day)
rat NA; hematologlcal ND
effects, altered
organ weights
1.5E-1 NA 100 U.S. EPA. 1990/
Ell Lilly Co.,
1985; U.S. EPA.
1984. 1990
0059h
                                                                            A-49
                                                                                                                         07/24/90

-------
                                                                     Update:  '" -e.  1990
Exposure
Compound Inhalation; Oral
chronic (RfO) NA; 250 ppm In the diet
for 90 days (IS mg/kg/
day)
Lactonltrlle
Lead
subchronlc (RfDs) NA; NA
chronic (RfD) NA; NA
Lead alkyls: tetrabutyl.
tetraethyl. tetramethyl.
tetrapropyl. trlethyl.
trlmethyl. trlpropyl.
trlmethylethyl,
dlmethylethyl.
methyl trlethyl
subchronlc (RfDs) NA; 0.00017 mg/kg/day
by gavage for 20 weeks
chronic (RfD) NA; 0.00017 mg/kg/day
by gavage for 20 weeks
Species Effect of Concern Reference Dose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
NA rat NA; hematologlcal ND 1.5E-2* NA 1000
effects, altered
organ weights
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA NA NA; NA NDP NO NA NA
NA NA CNS effects; NDP ND<« NA NA
CNS effects
(also see Table B)
NA rat NA; liver and ND 1E-6 NA 1000
neuronal damage
NA rat NA; liver and ND 1E-7* NA 10.000
neuronal damage
Reference
Inhalation/Oral
U.S. EPA, 1990/
Ell Lilly Co..
1985; U.S. EPA.
1984. 1990
U.S. EPA. 1988
U.S. EPA, 1984.
1986/U.S. EPA,
1984. 1986
U.S. EPA, 1984.
1986/U.S. EPA.
1984, 1986
U.S. EPA. 1985/
Schepers, 1964;
U.S. EPA. 1985
U.S. EPA. 1985/
Schepers, 1964;
U.S. EPA, 1985
Llndane (see Hexachlorocyclohexane, gamma)
Llnuron
  subchronlc (RfDs)
  chronic (RfD)
NA; 25 ppm In the diet    NA
for 2 years (0.625 mg/
kg/day)
NA; 25 ppm In the diet    NA
for 2 years (0.625 mg/
kg/day)
dog      NA; hematologlcal       ND
dog      NA; hematologlcal
         (also see Table B)
                                                                                             ND
2E-3          NA       300    U.S.  EPA.  1990/
                              Du Pont de
                              Nemours and Co..
                              1962; U.S. EPA,
                              1984. 1990

2E-3a>u       NA       300    U.S.  EPA,  1990/
                              Du Pont de
                              Nemours and Co..
                              1962; U.S. EPA,
                              1984. 1990
0059h
                                                                             A-50
                                                                                                                                                 07/12/90

-------


Compound
Malathlon
subchronlc (RfDs)
chronic (RfD)
Nalelc anhydride
subchronlc (RfOs)
chronic (RfD)
Halelc hydrazlde
subchronlc (RfDs)
chronlc(RfD)

Exposure Species
Inhalation; Oral Inhalation Oral
NA; 16 ing/day In cap- NA human
sules for 47 days
(0.23 mg/kg/day)
NA; 16 mg/day In cap- NA human
sules for 47 days
(0.23 mg/kg/day)
NA; 10 mg/kg/day In the NA rat
diet for 2 years
NA; 10 mg/kg/day In the NA rat
diet for 2 years
NA; IX In diet for NA rat
28 months (500 mg/kg/
day)
NA; IX In diet for NA rat
28 months (500 mg/kg/
day)
Update: >e. 1990
Effect of Concern Reference Dose Uncertainty Factor
Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
NA; hematologlcal NO 2E-2 NA 10
NA; hematologlcal ND 2E-2a NA 10
NA; kidney lesions ND 1E-1 NA 100
NA; kidney lesions ND 1E-13 NA 100
(also see Table B)
NA; altered kidney ND 5E-1 NA 1000
function
NA; altered kidney ND 5E-la NA 1000
function

Reference
Inhalation/Oral
U.S. EPA, 1990/
Hoe Her and
Rider. 1962;
U.S. EPA, 1984,
1990
U.S. EPA, 1990/
Hoe Her and
Rider, 1962;
U.S. EPA, 1984.
1990
U.S. EPA. 1990/
Jessup et al.,
1982; Preache,
1983; U.S. EPA.
1986. 1990
U.S. EPA. 1990/
Jessup et al.,
1982; Preache,
1983; U.S. EPA,
1986, 1990
U.S. EPA. 1989/
Van der Haljden
et al., 1981;
U.S. EPA. 1989.
1990
U.S. EPA, 1989/
Van der Haljden
et al.. 1981;
U.S. EPA. 1989.
1990
0059h
                                                                             A-51
07/12/90

-------
                                                             ii tun i  i MUL i  M .  JU
Update:
                                                                                       MIIU  innuiiii IUAIIIII  (UIIILK  innii  \,MIVO IHUULHH, t i i I
                                                                                       e. 1990
Compound
Malononltrlle
subchronk (RfDs)
chronic (RfO)
Mancozeb
subchronk (RfOs)
chronic (RfD)
Haneb
subchronk (RfDs)
chronic (RfD)
Manganese
subchronk (RfOs)
Exposure
Inhalation; Oral
NA; 0.25 mg/kg/day by
gavage 6 days/week for
120 days
NA; 0.25 mg/kg/day by
gavage 6 days/week for
120 days
NA; 50 ppm In the diet
for 90 weeks (2.9 mg/kg
day)
NA; 50 ppm In the diet
for 90 weeks (2.9 mg/kg
day)
NA; 300 ppm In diet for
6 months (5 mg/kg/day)
NA; 300 ppm In diet for
6 months (5 mg/kg/day)
0.3 mg/n)3 occupational
(2.1 ing/day); 1050 ppm
Nn from Hn^ from
day 1 of gestation
through 224 days of age
(52.5 mg Hn/kg/day)
Species Effect of Concern Reference Dose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
NA rat NA; liver and NO 2E-4 NA 1000
spleen
NA rat NA; liver and NO 2E-51 NA 1000
spleen
(also see
Table B)
NA rat NA; goltrogenk NO 3E-2 NA 100
effects
NA rat NA; goltrogenk ND 3E-2 NA 100
effects
NA monkey NA; Increased ND 5E-2 NA 100
thyroid weight
NA monkey NA; Increased ND 5E-2a NA 100
thyroid weight
human rat CNS; reproductive lE-3(3E-4) 5E-1 100 100
Reference
Inhalation/Oral
U.S. EPA, 1986/
Panov et al.,
1972; U.S. EPA.
1986
U.S. EPA, 1986/
Panov et al.,
1972; U.S. EPA.
1986
U.S. EPA. 1984/
U.S. EPA. 1984
U.S. EPA. 1984/
U.S. EPA, 1984
U.S. EPA, 1984/
Rohm and Haas
Co.. 1977; Naneb
Data Task Force,
1986; U.S. EPA.
1984. 1990
U.S. EPA, 19B4/
Rohm and Haas
Co.. 1977; Naneb
Data Task Force.
1986; U.S. EPA,
1984, 1990
Sarlc et al.,
1977; U.S. EPA,
1984a,b/Laskey
et al.. 1982;
U.S. EPA.
1984a.b
0059h
                                                                                  A-52
                                                                                  07/12/90

-------
                                                                     Update:  '" -2
years (22 mg Mn/kg/day
day) 1n drinking water

Reference Dose Uncertainty Factor Reference
Inhalation Oral Inhalation Oral Inhalation/Oral
[mg/m3 (nig/kg/day)] (mg/kg/day)
1E-3J3E-4) 2E-lJ 100




100 Sarlc et al.,
1977; U.S. EPA,
1984/Leung
et al.. 1981;
Lai et al..
1982; U.S. EPA.
19B4a,b
HCPA (see 2-Hethyl-4-chlorophenoxyacet1c acid)

MCPB (see 4-(2-Hethyl-4-chlorophenoxy)butyr1c acid)

HCPP (see 2-(2-Hethyl-4-chlorophenoxy)prop1on1c acid)
Mephosfolan
  subchronlc (RfDs)
  chronic (RfO)
Mercury.  Inorganic
  subchronlc  (RfDs)
NA; 1.25 ppm In the diet  NA
for 17 weeks (0.09 mg/
kg/day)
NA; 1.25 ppm In the diet  NA
for 17 weeks (0.09 mg/
kg/day)
0.009 mg/m3, several
occupational studies;
several oral and
parenteral studies In
the Brown Norway rat
human
          rat      NA;  liver and kidney       NO
                  weights, reduced
                  plasma. RBC and
                  brain  chollnesterase
                  activities

          rat      NA;  liver and kidney       NO
                  weights, reduced
                  plasma, RBC and
                  brain  chollnesterase
                  activities
rat     neurotoxlclty;              3E-4
        kidney effects
                                                                                        9E-4
                                                                                                              9E-5
                                                                                         3E-4
                                                                  NA       100    U.S. EPA, 1984/
                                                                                  U.S. EPA. 1964
                                                                  NA      1000    U.S. EPA. 1984/
                                                                                  U.S. EPA, 1984
30      1000    Fawer et al..
                1987; Pakllvl
                and Toulonen,
                1989; P1kl1v1
                and Hannlnen,
                1989; Plkllvl..
                1989; U.S. EPA.
                19B4. 1990/
                Fltzhugh
                et al., 1950;
                Oru et al..
                1978; Bernaudln
                et al.. 1981;
                Andres. 1984;
                U.S. EPA. 1987
 0627h
                                                                             A-53
                                                                                                                                                  07/12/90

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Compound
chronic (RfD)









Nerphos
subchronlc (RfOs)

chronic (RfD)

Herphos oxide
subchronlc (RfDs)

chronic (RfD)


Exposure Species
Inhalation; Oral Inhalation Oral
0.009 mg/m3. several human rat
occupational studies;
several oral and
parenteral studies In
the Brown Norway rat









NA; 0.1 mg/kg/day In NA hen
capsules for 3 months

NA; 0.1 mg/kg/day In NA hen
capsules for 3 months

NA; 0.1 mg/kg/day In NA hen
capsules for 3 months

NA; 0.1 mg/kg/day In NA hen
capsules for 3 months

Update- 
-------

Compound
MethacrylonHrlle
subchronlc (RfDs)
chronic (RfD)
Methanol
subchronlc (RfDs)


chronic (RfD)


He t homy 1
subchronlc (RfOs)



chronic (RfD)


Exposure Species
Inhalation; Oral Inhalation Oral
3.2 ppm (9 mg/m3). 7 dog dog
hours/day. 5 days/week
for 90 days (0.63 mg/
kg/day): 3.2 ppm
(9 mg/m3) 7 hours/day
S days/week for 90 days
(0.32 mg/kg/day)
3.2 ppm (9 mg/m3). 7 dog dog
hours/day. 5 days/week
for 90 days (0.63 mg/
kg/day): 3.2 ppm
(9 mg/m3) 7 hours/day
5 days/week for 90 days
(0.32 mg/kg/day)
NA; 500 mg/kg/day by MA rat
gavage for 90 days


NA; 500 mg/kg/day by NA rat
gavage for 90 days


NA; 100 ppm In diet NA dog
(2.5 mg/kg/day) for
24 months

NA; 100 ppm In diet NA dog
(2.5 mg/kg/day) for
24 months

Effect of Concern Reference Dose Uncertainty Factor
Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
increased SCOT and 7E-3 (2E-3J™ 1E-3" 300 300
SGPT, loss of hind-
limb motor control,
brain lesions; In-
creased SGOT and
SGPT, loss of hind-
limb motor control,
brain lesions
increased SGOT and 7E-4 (2E-4)™ }l-<»>*> 3000 3000
SGPT, loss of hind-
limb motor control,
brain lesions; In-
creased SGOT and
SGPT. loss of hind-
limb motor control,
brain lesions
NA; Increased serum ND 5E*0 NA 100
alkaline phosphatase
and SGPT and
decreased brain
weight
NA; increased serum ND 5E-1* NA 1000
alkaline phosphatase
and SGPT and
decreased brain
weight
NA; kidney lesions ND 3E-2 NA 100



NA; kidney lesions ND 3E-2a NA 100


Reference

Pozzanl et al.,
1968; U.S. EPA,
1990/Pozzanl
et al., 1966;
U.S. EPA. 1990
Pozzanl et al..
1968; U.S. EPA.
1990/Pozzanl
et al., 1968;
U.S. EPA. 1990
NA/U.S. EPA.
1986, 1990


NA/U.S. EPA,
1986. 1990


U.S. EPA, 1988/
Kaplan and
Sherman. 1977;
U.S. EPA. 1988.
1990
U.S. EPA, 1988/
Kaplan and
Sherman, 1977;
U.S. EPA, 1988,
1990
0627h
                                                                             A-55
                                                                                                                                                  07/12/90

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                                                                     Updatr    'une, 1990
Compound
Methoxychlor
subchrontc (RfDs)


chronic (RfD)


2-Methoxyethanol
subchrontc (RfDs)







chronic (RfO)







Exposure
Inhalation; Oral

NA; 200 ppm (10 mg/kg/
day In diet during
gestation
NA; 200 ppm (10 mg/kg/
day) In diet during
gestation
10 ppm (31 mg/m3)
6 hours/day. 5 days/
week for 13 weeks
(2.9 mg/kg/day); 10
ppm (31 mg/m3) 6
hours/day, 5 days/week
for 13 weeks (1.47
mg/kg/day)
10 ppm (31 mg/m3)
6 hours/day, 5 days/
week for 13 weeks
(2.9 mg/kg/day); 10
ppm (31 mg/m3) 6
hours/day. 5 days/week
for 13 weeks (1.47
mg/kg/day)
Species Effect of Concern Reference Dose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)

NA rat NA; fetotoxlclty ND lE-lbb NA 100


NA rat NA; fetotoxlclty ND IE-IS*1'1* NA 100


rabbit rabbit fetotoxlclty and 1E-1 (3E-2)°>bb !E-2b>bb 100 100
testlcular effects;
fetotoxlclty and
.testlcular effects




rabbit rabbit fetotoxlclty and 1E-2 (3E-3)°>bb lE-3b>9.bb 1000 1000
testlcular effects;
fetotoxlclty and
testlcular effects




Reference
Inhalation/Oral

U.S. EPA. 19B4/
U.S. EPA, 1984

U.S. EPA. 1984/
U.S. EPA, 1984

Killer et al.,
1982; U.S. EPA,
1986/Nlller
et al., 1982;
U.S. EPA, 1986



Killer et al..
1982; U.S. EPA,
1986/Nlller
et al., 1982;
U.S. EPA. 1986



2-Methoxyethanol acetate
  subchronlc (RfDs)     NA; 10 ppm (31 mg/m3)
                        2-methoxyethanol x
                        18.13/76.09 (molecular
                        weight ratio) x 6 hours/
                        day x 5 days/week x 0.5
                        absorption factor for
                        13 weeks
                          NA
           rabbit   NA;  testlcular
                    degeneration
                                ND
                  2E-2b
  chronic (RfD)
NA; 10 ppm (31 mg/m3)
2-methoxyethanol x
18.13/76.09 (molecular
weight ratio) x 6 hours/
day x 5 days/week x 0.5
absorption factor for
13 weeks
NA
rabbit   NA; testlcular
         degeneration
ND
2E-3b
              NA       100    U.S.  EPA. 1987/
                              Killer et al.,
                              1982; U.S. EPA.
                              1987
NA      1000    U.S. EPA, 1987/
                Killer et al..
                1982; U.S. EPA,
                1987
0627h
                                                     A-56
                                                                                                07/12/90

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Compound
Methyl acetate
subchronlc (RfDs)
chronic (RfD)
Methyl acrylate
subchronlc (RfOs)
chronic (RfD)

Exposure Species
Inhalation; Oral Inhalation Oral
NR; 500 mg/kg/day NA rat
methanol by gavage for
90 days x 74.08/32.04
(molecular weight ratio)
NR; 500 mg/kg/day NA rat
methanol by gavage for
90 days x 74.08/32.04
(molecular weight ratio)
NA; 15 ppm (53 mg/m3) NA rat
x 6 hours/day x 5 days/
week for 2 years x 0.5
absorption factor
NA; 15 ppm (53 mg/m3) NA rat
x 6 hours/day x 5 days/
week for 2 years x 0.5
absorption factor
Update: M«. 1990
Effect of Concern Reference Dose Uncertainty Factor
Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
NA; liver NO 10 NA 100
damage
NA; liver ND 19 NA 1000
damage (also see
Table B)
NA; no effect ND 3E-2 NA 100
NA; no effect ND 3E-2 NA 100
(also see Table B)

Reference
Inhalation/Oral
U.S. EPA. 1986/
ToxIcHy
Research Labora-
tory. 1986;
U.S. EPA. 1986
U.S. EPA, 1986/
Toxlclty
Research Labora-
tory, 1986;
U.S. EPA, 1986
U.S. EPA, 1987/
Kllmlsch and
Relnlnghaus,
1984; U.S. EPA,
1987
U.S. EPA. 1987/
Kllmlsch and
Relnlnghaus.
1984; U.S. EPA.
1987
Methyl bromide (see Bromomethane)

Methyl chloride


Methyl chlorocarbonate

2-Methyl-4-chlorophenoxy-
DATA INADEQUATE FOR QUANTITATIVE  RISK ASSESSMENT
            (also see Table B)

DATA INADEQUATE FOR QUANTITATIVE  RISK ASSESSMENT
U.S. EPA. 1986


U.S. EPA. 1989
subchronlc (RfDs)




chronic (RfD)




NA; 6 ppm In the diet NA
for 52 weeks (0.15 mg/
kg/day)


NA; 6 ppm In the diet NA
for 52 weeks (0.15 mg/
kg/day)


dog NA; kidney and ND
and liver



dog NA; kidney and ND
and liver



5E-4 NA 300 U.S. EPA. 1990/
Industry Task
Force. 1986;
U.S. EPA. 1984.
1990
5E-4a NA 300 U.S. EPA, 1990/
Industry Task
Force. 1986;
U.S. EPA, 1984,
1990
0627h

-------
                                          nisi aani n i j ourinnn i  IMDLI  «.  iuoLtlKunn.  M«u LfiKunit  IUAH.III  luinun  innn (.nnbinuui.nii.iMj
                                                                     Update:     e.  1990
Compound
Exposure
Inhalation; Oral
4-(2-Hethyl-4-chlorophenoxy)-
buturlc acid (NCPB)
subchronlc (RfD«) NA; 12 mg/kg/day In the
diet for 13 weeks
chronic
NA; 12 mg/kg/day In the
diet for 13 weeks
Species
Inhalation Oral
NA rat,
dog
NA rat,
dog
Effect of Concern Reference Dose Uncertainty Factor
Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
NA; reproductive NO 1E-1 NA 100
toxldty In dogs,
liver and kidney
effects In rats
NA; reproductive NO 1E-2* NA 1000
toxldty In dogs,
liver and kidney
effects In rats
Reference
Inhalation/Oral
U.S. EPA. 1990/
Rhodla Inc..
19703. b;
U.S. EPA. 1984.
1990
U.S. EPA, 1990/
Rhodla Inc..
1970a, b;
U.S. EPA, 1984,
1990
2-(2-Methyl-4-chlorophenoxy)-
proplonlc acid (NCPP)
  subchronlc (RfDs)     NA; 50 ppm In the diet
                        for 90 days (3 mg/kg/
                        day)
  chronic (RfD)
Nethylcyclohexane

Hethylene bromide
  subchronlc (RfDs)
  chronic (RfD)
NA; 50 ppm In the diet
for 90 days (3 mg/kg/
day)
NA
                                                  NA
NA; 25 ppm (178 mg/m3)    NA
6 hours/day for 63 days
In a 90-day period, 0.5
absorption factor
(11.0 mg/kg/day)

NA; 25 ppm (178 mg/m3)    NA
6 hours/day for 63 days
In a 90-day period, 0.5
absorption factor
(11.0 mg/kg/day)
                                     rat      NA; kidney weight      NO
           rat      NA; kidney weight      ND
                                                             DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
                                                             rat      NA; Increased          ND
                                                                      carboxyhemoglobln
                                                             1E-2
                                                                                       IE -3*
                                     rat      NA; Increased
                                              carboxyhemoglobln
                                              (also see
                                              Table B)
                                                                                             ND
                                                                                       l£-lb
                                                                                       IE -2°
                                                                                                     NA
                                                                                                                             NA
                                                                           NA
                                                                                                                             NA
                                                                                                                                      300    U.S. EPA, 1990/
                                                                                                                                             BASF Akt.. 1985;
                                                                                                                                             U.S. EPA. 1984,
                                                                                                                                             1990

                                                                                                                                     3000    U.S. EPA. 1990/
                                                                                                                                             BASF Akt.. 1985;
                                                                                                                                             U.S. EPA, 1984.
                                                                                                                                             1990

                                                                                                                                             U.S. EPA, 1984
100    U.S. EPA. 1987/
       Keyes et al.,
       1982; U.S. EPA.
       1987
                                                                                   1000    U.S. EPA. 1987/
                                                                                           Keyes et al..
                                                                                           1982; U.S. EPA.
0627h
                                                                             A-58
                                                                                                                                                  07/12/90

-------
                                                                     Update:  ~-ne.  1990
      Compound
                              Exposure
  Inhalation;  Oral
                              Species
                                                 Inhalation   Oral
Effect of Concern
Inhalation;  Oral
                                                                                                Reference Dose
    Inhalation
[mg/m3 (nig/kg/day)]
   Oral
(mg/kg/day)
                                 Uncertainty  Factor
                                  Inhalation    Oral
                                   Reference
                                Inhalation/Oral
Methylene chloride
(dlchloromethane)
  subchronlc (RfDs)
  chronic (RfD)
200 ppm (694.B mg/m3)     rat        rat
6 hours/day. 5 days/week
for 2 years; 24-month
drinking water study
[S.B5 mg/kg/day (males)
6.47 mg/kg/day (females)]

200 ppm (694.8 mg/m3)     rat        rat
6 hours/day. 5 days/week
for 2 years; 24-month
drinking water study
[5.65 mg/kg/day (males)
6.47 mg/kg/day (females)]
 NA; liver toxlclty;
 NA; liver toxlclty;
 (Cancer: see
 Table B)
4.4'-Methylened1phenyl
Isocyanate
                          DATA INADEQUATE  FOR QUANTITATIVE  RISK  ASSESSMENT
                       6E-2         100       100    NHschke  et  al.,
                                                     198B/ National
                                                     Coffee Associa-
                                                     tion, 19B2;
                                                     U.S.  EPA. 19B9.
                                                     1990

                       6E-2a        100       100    NHschke  et  al..
                                                     19BB/Nat1onal
                                                     Coffee Associa-
                                                     tion. 1982;
                                                     U.S.  EPA. 1989.
                                                     1990

                                                     U.S.  EPA. 1985
Methyl ethyl benzenes (see Ethyltoluene)
netnyi einyi neione
subchronlc (RfDs)

chronic (RfD)


235 ppm (693 mg/m3) rat
7 hours/day. 5 days/
week for 12 weeks (92
mg/kg/day 1; 235 ppm
(693 mg/m3) 7 hours/
day, 5 days/week for
12 weeks (46 mg/kg/day)
235 ppm (693 mg/m3) rat
7 hours/day, 5 days/
week for 12 weeks (92
mg/kg/day); 235 ppm
(693 mg/m3) 7 hours/
day, 5 days/week for
12 weeks (46 mg/kg/day)
rat CNS; fetotoxlclty 3E-0(9E-1) 5E-lb-bb 100 100 LaBelle and
Brleger, 1955;
U.S. EPA, 1990/
LaBelle and
Brleger, 1955;
U.S. EPA, 1985,
1989. 1990
rat CNS; fetotoxlclty 3E-1 (9E-2)9 5E-2b.l.*,bb iQOO 1000 LaBelle and
Brleger. 1955;
U.S. EPA, 1990/
LaBelle and
Brleger, 1955;
U.S. EPA, 1985.
1AOO 1 AOft
1989, 1990
0627h
                                                                             A-59
                                                                                                                                                  07/12/90

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                                                                     Update:   "-me.  1990
Exposure Species
Compound Inhalation; Oral Inhalation Oral
Methyl Isobutyl ketone
subchronlc (RfDs) 50 ppm (205 mg/mj) rat rat
6 hours/day. 5 days/
week for 90 days
(23.3 mg/kg/day);
50 mg/kg/day by gavage
for 13 weeks
chronic (RfD) 50 ppm (205 mg/m3) rat rat
6 hours/day. 5 days/
week for 90 days
(23.3 mg/kg/day);
50 mg/kg/day by gavage
for 13 weeks
Effect of Concern Reference Dose Uncertainty Factor
Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
liver and kidney 8E-1 (2E-1) 5E-1 100 100
effects; liver and
kidney effects



liver and kidney 8E-2 (2E-2)9 5E-2a 1000 1000
effects; liver and
kidney effects


Reference
Innd idiion/urd i
Union Carbide
Corp.. 1983;
U.S. EPA. 1987/
Microbiological
Associates.
1986; U.S. EPA.
1987
Union Carbide
Corp., 1983;
U.S. EPA, 1987/
Microbiological
Associates.
1986; U.S. EPA,
1987, 1990
Methyl Isocyanate

Methyl mercury
  subchronlc (RfDs)
  chronic (RfD)
NA; 0.003 mg/kg/day       NA
In humans associated
with Hg 1n blood at
200 ng/ml
NA; 0.003 mg/kg/day       NA
In humans associated
with Hg In blood at
200 ng/ml
          DATA  INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT


          human   NA; CNS effects        NO                3E-4
                                                             human    NA;  CNS effects
                                                                     NO
                                                                                                               3E-4Z
                                                                                                                                            U.S. EPA, 1986
                                                      NA        10    U.S. EPA. 1990/
                                                                      Clarkson et al.,
                                                                      1976; Nordberg
                                                                      Strangart. 1976;
                                                                      WHO, 1976; U.S.
                                                                      EPA. 1980, 1984,
                                                                      1990

                                                      NA        10    U.S. EPA, 1990/
                                                                      Clarkson et al.,
                                                                      1976; Nordberg
                                                                      Strangart, 1976;
                                                                      WHO. 1976; U.S.
                                                                      EPA. 1980, 1984,
                                                                      1990
Methyl methacrylate
   subchronlc  (RfDs)
NA; 60 ppm for 4 months
then 70 ppm for 20
months In drinking water
(7.5 mg/kg/day)
NA
                                     rat
NA; Increased
relative kidney
weight
                                                                     ND
                                                                                       8E-2
NA       100    U.S. EPA, 1985/
                Borgelleca
                et al.. 1964;
                U.S. EPA. 1985
 0627h
                                                                             A-60
                                                                                                                                                  07/12/90

-------


Compound

chronic (RfD)




Methyl parathlon
subchronlc (RfDs)


chronic (RfD)



Methyl styrene
(Industrial mixture)
subchronlc (RfDs)





chronic





Methyl styrene, alpha
subchronlc (RfDs)





Exposure Species
Inhalation; Oral Inhalation Oral

NA; 60 ppm for 4 months NA rat
then 70 ppm for 20
months In drinking water
(7.5 mg/kg/day)

NA; 0.5 ppm (0.025 mg/ NA rat
kg/day) In diet for
2 years

NA; 0.5 ppm (0.025 mg/ NA rat
kg/day) In diet for
2 years


10 ppm (48.3 mg/m3) 6 mouse mouse
hours/day, 5 days/week
for 103 weeks (11.2 mg/
kg/day); 10 ppm (4B.3
mg/m3) 6 hours/day,
5 days/week for 103
weeks (5.6 mg/kg/day)
10 ppm (48.3 mg/m3) 6 mouse mouse
hours/day, 5 days/week
for 103 weeks (11.2 mg/
kg/day); 10 ppm (48.3
mg/m3) 6 hours/day,
5 days/week for 103
weeks (5.6 mg/kg/day)
970 mg/m3. 7.5 hours/ rat NA
day, 5 days/week for
200 days (69 mg/kg/day);
NA

Update: ^e, 1990
Effect of Concern Reference Dose Uncertainty Factor
Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
NA; Increased ND BE -29 NA 100
relative kidney
weight
(also see
Table B)
NA; reduced hemo- ND 2.5E-4 NA 100
globln, hematocrH
and RBCs. cholln-
esterase Inhibition
NA; reduced hemo- ND 2.5E-43 NA 100
globln, hematocrH
and RBCs, cholln-
esterase Inhibition

nasal lesions; 4E-2 (1E-2) 6E-3b 1000 1000
nasal lesions




nasal lesions; 4E-2 (1E-2) 6E-3& 1000 1000
nasal lesions




liver and kidney; ND 7E-lb NA 100
NA




Reference
Inhalation/Oral

U.S. EPA, 1985/
Borgelleca
et al.. 1964;
U.S. EPA, 1985

U.S. EPA. 19B4/
Monsanto Co.,
1983; U.S. EPA,
1990
U.S. EPA, 19B4/
Honsanto Co.,
1983; U.S. EPA,
1990

MRI. 1984a;
U.S. EPA, 1987/
MRI, 1984a;
U.S. EPA. 1987


NRI, 1984a;
U.S. EPA, 1987/
NRI, 1984a;
U.S. EPA, 1987


U.S. EPA, 1987;
Wolf et al..
1956/U.S. EPA.
1987; Wolf
et al., 1956
0627h
                                                                             A-61
07/12/90

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                                                                      Update-  " 
-------


Compound
Naphthalene
subchronk (RfDs)


chronic (RfD)
1,4-Naphthoqulnone
Nickel
subchronk (RfDs)

chronic (RfD)

E xposure
Inhalation; Oral
NA; 10-20 ing/day In
diet 6 days/week for
=700 days (41 mg/kg/
day)*
NA; 10-20 ing/day In diet
6 days/week for =700
days (41 mg/kg/day)s

NA; 100 ppm N1 from
nickel sulfate In diet
for 2 years
(5 mg N1 /kg/day)
NA; 100 ppm Nl from
nickel sulfate In
diet for 2 years
1C «.« UI/bn/Hlul
Update: 'e. 1990
Soecles Effect of Concern Reference Dose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral innaiation urai
[mg/m3 (mg/kg/day)J (mg/kg/day)
NA rat NA; ocular and NO 4E-3t NA 10.000
Internal lesions


NA rat NA; ocular and NO 4E-39.1.1 NA 10.000
Internal lesions
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA rat cancer; reduced ND 2E-2 NA 300
body and organ
weight

NA rat cancer (see Table NO 2E-2* NA 300
B); reduced body
and organ weight

Reference
Inhalation/Oral
U.S. EPA, 1988/
Schmahl. 1955;
U S EPA. 1988


U.S. EPA. 1988/
Schmahl. 1955;
U.S. EPA, 1986.
1988
U.S. EPA. 1986
U.S. EPA, 19B4/
Ambrose
et al.. 1976;
US EPA 1990

U.S. EPA. 1984/
Ambrose
et al.. 1976;
U.S. EPA. 1990
Nlcotlnonltrlle

Nitric oxide
  subchronk (RfOs)
  chronic (RfD)
Nitrite
  subchronk (RfDs)
NA; 10 ppm (10 mg/t)      NA
nitrate concentration
In Infant formula
(1.0 mg/kg/day)

NA; 10 ppm (10 mg/l)      NA
nitrate concentration
In Infant formula
(1.0 mg/kg/day)
NA; 10 ppm nitrate In     NA
drinking water
                                                             DATA  INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
human    NA; methemoglobin-      NA                1E-1          NA
         emla
human    NA; methemoglobln-     NA                H-la         MA
         emla
human    NA; methemoglobln-     ND                1E-1           NA
         emla
                                                                                                                    U.S.  EPA,  1987
10    NA/Walton,  1951;
      U.S.  EPA.  1990
10    NA/Walton.  1951;
      U.S. EPA, 1990
10    U.S. EPA, 1989/
      Walton, 1951;
      U.S. EPA, 1989.
      1990
 0627h
                                                                             A-63
                                                                                                                                                 07/12/90

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                                                                    Update:
,  1990
Compound
chronic (RfO)

Nltroanlllnes (o-, m
Nitrobenzene
subchronk (RfOs)





chronic (RfD)




Nltrofurantoln
Subchronk (RfDs)

chronic (RfD)


Nltrofurans, other:
Nitrogen dioxide
subchronk (RfDs)




Exposure
Inhalation; Oral
NA; 10 ppm nitrate In
drinking water

-, P-)
5 ppm (25 mg/m3)
6 hours/day. S days/
week for 90 days
(HEC=4.5 mg/m3);
5 ppm (25 mg/m3)
6 hours/day. 5 days/
week for 90 days
(4.64 mg/kg/day)
5 ppm (25 mg/m3)
6 hours/day. 5 days/
week for 90 days
(HEC=4.5 mg/m3);
S ppm (25 mg/m3)
6 hours/day, 5 days/
week for 90 days
(4.64 mg/kg/day)
NA; 300 ppm diet for
13 weeks (69.7 mg/kg/
day)
NA: 300 ppm diet for
13 weeks (69.7 mg/kg/
day)
see Table B
0.4 ppm (0.753 mg/m3)
continuous for up to
27 months (HEC=1.56
mg/m3); 10 ppm
nltrate-N In water
(1 mg nltrate-N/kg/day)

Species Effect of Concern Reference Dose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
NA human NA; methemoglobln- ND 1E-1Z NA 10
emla

DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
mouse mouse hematologlcal. 2E-2 5E-3b 300 1000
adrenal, renal and
hepatic lesions;
hematologlcal.
adrenal, renal and
hepatic lesions;


mouse mouse hematologlcal, 2E-3J 5E-4°.l.z 3000 10,000
adrenal, renal and
hepatic lesions;
hematologlcal,
adrenal, renal and
hepatic lesions;


NA mouse NA; testlcular ND 7E-1 NA 100
damage

NA mouse NA; testlcular ND 7E-2 NA 1000
damage


rat human proliferate 2E-2 1E*0 100 1
changes In lungs;
methemogloblnemla



Reference
Inhalation/Oral
U.S. EPA, 1989/
Walton. 1951;
U.S. EPA, 1989.
1990
U.S. EPA, 1985
CUT. 1984;
U.S. EPA. 1987/
CUT, 1984;
U.S. EPA, 1987




CUT. 1984;
U.S. EPA, 1987/
CUT, 1984;
U.S. EPA, 1985.
1987, 1990



U.S. EPA, 1987/
SRI, 1980;
U.S. EPA, 1987
U.S. EPA, 1987/
SRI, 1980;
U.S. EPA, 1987

Kubota et al.,
1987; Sagal and
Ichlnose, 1987;
Sagal et al.,
1984; U.S. EPA,
1990b/Ualton,
1951; U.S. EPA.
1990a.b
ni/19/an
0627h

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HtAMH til tUb
                                                      bUMMAK> IABU A: bUULHKUNIl ANU UIKUNU IUA1UIY IUIHLK  IHHN l«KUNUUlNil.l II)
                                                                      Update:      e.  1990
Compound
chronic (RfD)
Nitrogen oxides
Nltromethane
Nltrophenols
p-NI trosodlphenylamlne
Nltrotoluenes (o-. m-.
subchronlc (RfDs)
chronic (RfD)
Octamethylpyrophos-
phoramlne
subchronlc (RfOs)
chronic (RfD)
Exposure
Inhalation; Oral
0.4 ppm (0.753 mg/m3)
continuous for up to
27 months (HEC*1.56
mg/m3); 10 ppm
nltrate-N In water
(1 mg nltrate-N/kg/day)




P-)
NA; 200 mg/kg/day
o-nltrotoluene x
5 days/week by gavage
for 6 months
NA; 200 mg/kg/day
o-nHrotoluene x
5 days/week by gavage
for 6 months
NA; 1.5 mg/day for at
least 30 days (0.02
mg/kg/day)
NA; 1.5 mg/day for at
least 30 days (0.02
mg/kg/day)
Species Effect of Concern Reference Oose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation oral
[mg/m3 (mg/kg/day)) (mg/kg/day)
rat human proliferate 2E-29 lE+flMd 100 1
changes In lungs;
methemogloblnemla
RISK ASSESSMENT VALUES NOT DERIVED
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA rat NA; splenic lesions ND 1E-1 NA 1000
NA rat NA; splenic lesions ND 1E-2 NA 10.000
(also see Table B)
NA human NA; decreased blood ND 2E-3 NA 10
chollnesterase
activity
NA human NA; decreased blood ND 2E-39 NA 10
chollnesterase
activity
Reference
Inhalation/Oral
Kubota et al.,
1987; Sagal and
Ichlnose, 19B7;
Sagal et al..
1984; U.S. EPA,
1990b/Walton.
1951; U.S. EPA,
1990a,b
U.S. EPA. 1982
U.S. EPA, 1985
U.S. EPA, 1987
U.S. EPA, 1986
U.S. EPA, 1986;
Clss et al..
1980; U.S. EPA.
1986
U.S. EPA. 1986;
Clss et al.,
1980; U.S. EPA.
1986
U.S. EPA. 1989/
Rider et al..
1969; U.S. EPA.
1989
U.S. EPA. 1989/
Rider et al.,
1969; U.S. EPA,
1989
0627h
                                                                              A-65
                                                                                                                                                    07/12/90

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                            IILIII 111  LIILLIJ MJJLJJllllll j juillinni  IMULt «. iUOUmUrtlL  HI1U  Limimit, IUA111II JOIII4.B III Mil LMH*. U1UULI1111 I I |
                                                                       Update:
                                                          
-------
                                         i .. i.. njji JJM, i.i j  .juiiii/mi  inum  n. ouubiinunii. MIHU  iiinuiut.  IUAIIIII  \UIIILU  iniiii CMCVI.JKUULKH.III/
                                                                             Update:     ie, 1990
Exposure Species
Compound Inhalation; Oral Inhalation Oral
chronic (RfD) NA; 12.5 mg/kg/day. NA dog
7 days/week In capsules
for 2 years

Pentabromodlphenyl ether
subchronlc (RfOs) NA; 1 .8 mg/kg/day by NA rat
gavage for 90 days

chronic {RfD) NA; 1.8 mg/kg/day by NA rat
gavage for 90 days

Pentachlorobenzene
subchronlc (RfOs) NA; 83 mg/kg/day In NA rat
the diet for 100 days

chronic (RfD) NA; 83 mg/kg/day In NA rat
the diet for 100 days


Pentachlorocyclopentadlene DATA
Pentachloronl trobenzene
subchronlc (RfDs) NA; 30 ppm (0.75 mg/kg/ NA dog
day) In diet for 2 years


chronic (RfD) NA; 30 ppm (0.75 mg/kg/ NA dog
day) In diet for 2 years


Effect of Concern Reference Dose Uncertainty Factor
Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
NA; liver ND 4E-2« NA 300

NA; liver ND 2E-2 NA 100
enzymes

NA; liver ND 2E-3a NA 1000
enzymes

NA; liver and kidney NO 8E-3 NA 1000
toxlclty

NA; liver and kidney ND 8E-4a NA 10,000
toxlclty


INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT1
NA; liver toxlclty ND 3E-3 NA 300


NA; liver toxlclty ND 3E-3a NA 300
(Cancer: see
Table B)

Reference
Inhalation/Oral
U.S. EPA, 19907
American
Cyanlmld, 1979;
U.S. EPA. 1984.
1990
U.S. EPA, 1990/
Carlson, 1980;
U.S. EPA, 1983.
1990
U.S. EPA, 1990/
Carlson, 1980;
U.S. EPA, 1983.
1990
U.S. EPA, 1989/
Under. 1980;
U.S. EPA, 1989,
1990
U.S. EPA, 1989/
Under, 1980;
U.S. EPA, 1989,
1990
U.S. EPA, 1988
U.S. EPA, 1986/
Olln Corp.,
1968; U.S. EPA.
1990
U.S. EPA. 1986/
Olln Corp.,
1968; U.S. EPA,
1990
0627h
                                                                                     A-67
                                                                                                                                                                  07/12/90

-------
                                                                     Update:   '-me.  1990
Compound
Pentachlorophenol
subchronk (RfOg)
chronic (RfD)

Exposure
Inhalation; Oral
NA; 3 mg/kg/day by
gavage 62 days before
mating through gestation
NA; 3 mg/kg/day by
gavage for 22-24 months

1,1 ,2,3,3-Pentachloropropene
n-Pentane
Phenanthrene

Phenol
subchronk (RfDj)

chronic (RfD)

Phenylenedlamlnes (o-.
m-Phenylenedlamlne
subchronk (RfDs)


chronic (RfO)





NA; 60 mg/kg/day by
gavage during organo-
genesls

NA; 60 mg/kg/day by
gavage during organo-
genesls

P-)
NA; 6.0 mg/kg/day for
90 days


NA; 6.0 mg/kg/day for
90 days


Species Effect of Concern Reference Dose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)) (mg/kg/day)
NA rat NA; fetotoxldty ND 3E-2bb NA 100
NA rat NA; liver and ND 3E-2a NA 100
kidney pathology

DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
'
NA rat NA; reduced ND 6E-lbb NA 100
fetal body
weight

NA rat NA; reduced ND 6E-la.1-bb NA 100
fetal body
weight

DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT (Cancer: see Table B)
NA rat NA; liver lesions ND 6E-2 NA 100


NA rat NA; liver lesions ND 6E-3a NA 1000


Reference
Inhalation/Oral
U.S. EPA, 1984/
Schwetz et al..
1978; U.S. EPA,
1984, 1986, 1990
U.S. EPA, 1984/
Schwetz et al.,
1978; U.S. EPA,
1984. 1986, 1990
U.S. EPA. 1983
U.S. EPA. 1987
U.S. EPA, 1984,
1987

U.S. EPA, 1984/
Research
Triangle
Institute. 1983;
U.S. EPA, 1990
U.S. EPA. 1984/
Research
Triangle
Institute, 1983;
U.S. EPA, 1990
U.S. EPA. 1985
U.S. EPA, 1985/
Hofer and Hruby,
1982; U.S. EPA.
1990
U.S. EPA. 1985/
Hofer and Hruby.
1982; U.S. EPA.
1990
0627h
                                                                             A-68
                                                                                                                                                 07/12/90

-------
                           Ml ML I II  IIILLI3  MiiliiHLrtlJ  JUHnMK I  I HULl H.
                                                                     Update:
                                                         MNU IMKUNlt. IUA111II JUINLn lll«l» LHKCIWUUI«It I I I |
                                                         «,  1990
                              Exposure
      Compound
  Inhalation;  Oral
                              Species
                                                 Inhalation  Oral
                   Effect of Concern
                   Inhalation; Oral
                                                                                                Reference Dose
    Inhalation
[mg/m3 (mg/kg/day)]   (mg/kg/day)
	  Uncertainty Factor     Reference
Oral     Inhalation    Oral   Inhalation/Oral
Phenylmercurk acetate
  subchronlc (RfDs)     NA;  0.1  ppro mercury In
                        diet for 2 years
                        (0.0084  mg mecurlc
  chronic (RfD)
Phosgene
acetate/kg/day)ee

NA; 0.1 ppm mercury In
diet for 2 years
(0.0084 mg mecurlc
acetate/kg/day)ee
                          NA         rat      NA; renal damage       NO                BE-5          NA
NA         rat      NA;  renal  damage        ND                8E-5a         NA
                                                             DATA  INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
                                                                                   100    NA/FUzhugh et
                                                                                          al., 1950; U.S.
                                                                                          EPA, 1990
                                              100    NA/FUzhugh  et
                                                     al..  1950; U.S.
                                                     EPA.  1990
                                                                                                                    U.S. EPA, 1984
rnospnine
subchronlc (RfDs)
chronic (RfD)
Phthallc acid esters
Phthallc acids (o-.
p-Phthallc acid
subchronlc (RfDs)
chronic (RfD)
Phthallc anhydride
subchronlc (RfDs)
1 ppm (1.4 mg/m3) rat
34 hours/week for 24
weeks; 0.026 mg/kg/day
In the diet for 2 years
1 ppm (1.4 mg/m3) rat
34 hours/week for 24
weeks; 0.026 mg/kg/day
In the diet for 2 years
, selected (see Table B)
m-J
NA; 142 mg/kg/day In NA
diet for 2 years
NA; 142 mg/kg/day In NA
diet for 2 years
NA; 12.019 ppm (1562 NA
mg/kg/day) In diet for
104 weeks
rat renal effects; 3E-4 3E-4
no effect
rat renal effects; 3E-5 3E-4a
no effect

DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
rat NA; hyperplasla ND 1E+0
of bladder uro-
thellum
rat NA; hyperplasla ND 1E+0
of bladder uro-
t he 11 urn
mouse NA; lung and kidney ND . 2E»0
hlstopathology
1 100 Kllmmer, 1969;
U.S. EPA. 1989/
Hackenberg,
1972; U.S. EPA,
19B9
10 100 Kllmmer. 1969;
U.S. EPA. 1989/
Hackenberg,
1972; U.S. EPA,
1989
•
U.S. EPA. 1986
NA 100 U.S. EPA. 1986/
CUT, 1983;
Gross, 1974;
U.S. EPA, 1986
NA 100 U.S. EPA. 1986/
CUT. 1983;
Gross. 1974;
U.S. EPA, 1986
NA 1000 U.S. EPA, 1986/
NCI. 1979.
U.S. EPA. 1990
07/1 2/90
 0627h

-------
/\ibi
                                                               IABU A: SUULHKONIC ANU CHRONIC 10XICIIY (OlHtK 1HAN CARCINOGENICI1Y)
                                                                      Update:      e.  1990
Compound
chronic (RfD)


Polybromlnated
btphenyls
subchronlc (RfOs)



chronic (RfO)



Potassium cyanide
subchronlc (RfOs)




chronlr (RfO)




Exposure Species
Inhalation; Oral Inhalation Oral
NA; 12,019 ppm (1562 NA mouse
mg/kg/day) In diet for
104 weeks


NA; M remaster FF-1 NA rat
0.1 mg/kg by gavage.
5 days/week for 25 weeks
(0.07 mg/kg/day)
NA; F1 remaster FF-1 NA rat
0.1 mg/kg by gavage,
5 days/week for 25 weeks
(0.07 mg/kg/day)

NA; 10.8 mg/kg/day NA rat
fumigated cyanide In
food for 2 years
(27 mg/kg/day)

NA; 10.8 mg/kg/day NA rat
fumigated cyanide In
food for 2 years
(27 mg/kg/day)

Effect of Concern Reference Dose Uncertainty Factor
Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
NA; lung and kidney ND 2E»0* NA 1000
hlstopathology
(also see Table B)


NA; elevated liver ND 7E-5 NA 1000
weight and liver
lesions

NA; elevated liver ND 7E-6 NA 10.000
weight and liver
lesions
(also see Table B)

NA; weight loss, ND 5E-2 NA 500
thyroid effects, and
myelln degeneration


NA; weight loss. ND 5E-2a NA 500
thyroid effects, and
myelln degeneration


Reference
Inhalation/Oral
U.S. EPA, 1986/
NCI. 1979.
U.S. EPA. 1990


U.S. EPA, 1989/
NTP. 1983; U.S.
EPA. 1989

U.S. EPA, 1989/
NTP, 1983; U.S.
EPA. 1989


NA/Howard and
Hanzal. 1955;
Phllbrlck et
al.. 1979; U.S.
EPA, 1990
NA/Howard and
Hanzal. 1955;
Phllbrlck et
al., 1979; U.S.
EPA, 1990
Potassium silver cyanide
subchrontc (RfOs)





chronic (RfD)





NA; 10.8 mg/kg/day NA rat
fumigated cyanide In
food for 2 years
(equivalent to
potassium silver cyanide
at 82.7 mg/kg/day)
NA; 10.8 mg/kg/day NA rat
fumigated cyanide In
food for 2 years
(equivalent to
potassium silver cyanide
at 82.7 mg/kg/day)
NA; weight loss, ND 2E-ln NA 500
thyroid effects, and
myelln degeneration



NA; weight loss, ND 2E-la>" NA 500
thyroid effects, and
myelln degeneration



NA/Howard and
Hanzal. 1955;
Phllbrlck et
al.. 1979; U.S.
EPA. 1990

NA/Howard and
Hanzal, 1955;
Phllbrlck et
al., 1979; U.S.
EPA, 1990

0627h
                                  A-70
                                                                                                                                                  07/12/90

-------
..UMiiiini inULi H.  iUDLtlKUl"''  ANU LHKUN1L  IUXR1IY (UIHtH  I HAN IAKIINOGtNIClIY)
                Update:       ,  1990
Compound
Prof luralln
subchronk (RfDs)
chronic (RfO)
Pronamlde
subchronk (RfDs)
chronic (RfD)
Propachlor
subchronk (RfDs)
chronk (RfO)
Propazlne
subchronk (RfDs)
chronk (RfO)
2-Propenok acid (see
Proplonltrlle
n-Propyl alcohol
0627h
Exposure
Inhalation; Oral
NA; subchronk feeding
study; no details
provided
NA; subchronk feeding
study; no details
provided
NA; 300 ppm In diet for
2 years (7.5 mg/kg/day)
NA; 300 ppm In diet for
2 years (7.5 mg/kg/day)
NA; 13.3 mg/kg/day
In the diet for 90 days
NA; 13.3 mg/kg/day
In the diet for 90 days
NA; 100 ppm In the
diet for 2 years
(5 mg/kg/day)
NA; 100 ppm In the
diet for 2 years
(5 mg/kg/day)
Acrylic add)



Species
Inhalation Oral
NA rat
NA rat
NA dog
NA dog
NA rat
NA rat
NA rat
NA rat

DATA
DATA

Effect of Concern Reference Dose Uncertainty Factor
Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
NA; NA NO 6E-3 NA NA
NA; NA ND 6E-3 NA NA
NA; none observed ND 8E-2 NA 100
NA; none observed ND BE -2* NA 100
NA; decreased body ND 1.3E-1 NA 100
weight gain
NA; decreased body ND 1.3E-23 NA 1000
weight gain
NA; decreased body ND 2E-2 NA 300
weight gain
NA; decreased body ND 2E-2a NA 300
weight gain
(also see Table 8)
•
INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
A-71
Reference
Inhalation/Oral
U.S. EPA. 1984/
U.S. EPA. 1984
U.S. EPA. 1984/
U.S. EPA. 1984
NA/Rohm & Haas.
Co.. 1970; U.S.
EPA. 1990
NA/Rohm & Haas.
Co., 1970; U.S.
EPA, 1990
U.S. EPA, 1984/
Monsanto, 1964;
U.S. EPA. 1984,
1990
U.S. EPA, 1984/
Monsanto, 1964;
U.S. EPA, 1984,
1990
U.S. EPA, 1990/
Gelgy, 1980;
U.S. EPA. 1984,
1990
U.S. EPA. 1990/
Gelgy, 1980;
U.S. EPA, 1984,
1990

U.S. EPA. 1985
U.S. EPA, 1987
07/12/90

-------
                           ML /HI II LIILLI3
                                                  i,ii aunrmm  IAULI  «.  auouiKUHil. MWU tiiKunit. IUAIV.JII  IUIIILH IIIMII I.MI\I.IIIUULIII«.I • • .
                                             Update:
                                                                                 e,  1990
Compound
Exposure
Inhalation; Oral
Soec1es
Inhalation Oral
Effect of
Inhalation
Concern
; Oral

Reference
Inhalation
[mg/m3 (mg/kg/day)]
Dose
Oral
(mg/kg/day)
Uncertainty
Inhalation
Factor
Oral
Reference
Inhalation/Oral
Propylene glycol
  subchronlc (RfDs)
  chronic (RfD)
Propylene glycol
monoethyl ether
  subchronlc (RfDs)
  chronic (RfD)
170-350 mg/ro3 (mean:      rat        rat
260 mg/m3) contin-
uously for IB months
(166 mg/kg/day); 6X In
diet for 20 weeks
(3 g/kg/day)

170-350 mg/m3 (mean:      rat        dog
260 mg/m3) contin-
uously for 18 months
(166 mg/kg/day); 50,000
ppm In diet for 2 years
(2.1 g/kg/day)
NA; 30-day drinking       NA         rat
water (680 mg/kg/day)
NA; 30-day drinking       NA         rat
water (680 mg/kg/day)
none observed; renal
lesions
none observed; de-
crease In RBC,
hematocrU. hemo-
globin In dogs
NA; reduced weight
gain
NA; reduced weight
gain
6E*0 (2E*0)
                                                                                       3E»1
                                                                                             6E+0 (2E»0)
                                         2Efl
                                                                     NO
                                                                                             ND
                                         7E»0
                                                                                                               7E-1
100       100    Robertson. 1947;
                 U.S. EPA, 1987/
                 Guerrant et al..
                 1947; U.S. EPA.
                 1987
                               100       100    Robertson, 1947;
                                                U.S. EPA. 1987/
                                                Gaunt et al.,
                                                1972; U.S. EPA.
                                                1987
                                NA        100    U.S.  EPA.  1984/
                                                Smyth and
                                                Carpenter,  194B;
                                                U.S.  EPA,  1984

                                NA       1000    U.S.  EPA,  1984/
                                                Smyth and
                                                Carpenter.  1948;
                                                U.S.  EPA.  1984
Propylene glycol
nonomethyl ether
subchronlc (RfDs) 1000 ppm (3685 mg/mj) rat, rat
6 hours/day. 5 days/ rabbit
week for 13 weeks;
947 mg/kg. 5 days/week
for 35 days (676 mg/
kg/day) by gavage
chronic (RfD) 1000 ppm (3685 mg/m3) rat. rat
6 hours/day. 5 days/ rabbit
week for 13 weeks;
947 mg/kg. 5 days/week
for 35 days (676 mg/
kg/day) by gavage
mild CNS effects; 7E+0
liver and kidney
hlstopathology


mild CNS effects; 7E-ll
liver and kidney
hlstopathology


7E+0 100 100 Landrey et al.,
1983; Miller
et al.. 1984;
U.S. EPA, 1984/
Rnup pfc al
nuwc ci a • • »
1054- n c FPA
tjjmtf v • <9 • L r n f
1984
7E-1 1000 1000 Landrey et al..
1984; Miller
et al.. 1984;
U.S. EPA. 1984/
Rnup P t a 1
nuwc c i a i • i
1954- U S EPA
I 7 jt i u • 
-------


Compound
Pyrene
subchronlc (RfD$)
chronic (RfO)
Pyrldlne
subchronlc (RfDj)
chronic (RfO)
RDX (CyclonHe)
subchronlc (RfDg)
chronic (RfO)
Ronnel
subchronlc (RfD§)
chronic (RfO)
Selenlous acid
subchronlc (RfD$)

Exposure
Inhalation; Oral
NA; 75 mg/kg/day by
gavage for 13 weeks
NA; 75 mg/kg/day by
gavage for 13 weeks
NA; 1 mg/kg/day by
gavage for 90 days
NA; 1 mg/kg/day by
gavage for 90 days
NA; 0.3 mg/kg/day
for 105 weeks
NA; 0.3 mg/kg/day
for 105 weeks
NA; 5 mg/kg/day In
the diet for 2 years
NA; 5 mg/kg/day In
the diet for 2 years
NA; 3.2 mg/day from
diet of selenlferous
foodstuffs (0.046
mg/kg/day)
Update: ne. 1990
Species Effect of Concern Reference
Inhalation Oral Inhalation; Oral Inhalation
[mg/m3 (mg/kg/day)]
NA mouse NA; renal effects NO
NA mouse NA; renal effects ND
NA rat NA; Increased NO
liver weight
NA rat NA; Increased ND '
liver weight
NA rat NA; prostate Inflam- ND
nation, hemoslderosls
NA rat NA; prostate Inflam- ND
matlon, hemoslderosls
NA rat NA; liver and ND
effects
NA rat NA; liver and ND
effects
NA human ND; hair and nail ND
loss, dermatitis

Dose Uncertainty Factor
Oral Inhalation Oral
(mg/kg/day)
3E-1 NA 300
3E-2J NA 3000
1E-2 NA 100
1E-33 NA 1000
3E-3 NA 100
3E-3a NA 100
5E-2 NA 100
5E-29 NA 100
3E-3 NA 15

Reference
Inhalation/Oral
U.S. EPA. 1984/
U.S. EPA, 1989
U.S. EPA, 1984/
U.S. EPA. 1989
U.S. EPA. 1990/
U.S. EPA.
1986a.b. 1990
U.S. EPA, 1990/
U.S. EPA,
1986a.b, 1990
U.S. EPA, 1989/
Levlne et al.,
1984; U.S. EPA,
1989, 1990
U.S. EPA, 1989/
Levtne et al.,
1984; U.S. EPA,
1989, 1990
U.S. EPA. 1984/
HcColllster
et al.. 1959;
U.S. EPA, 1984
U.S. EPA. 1984/
McColllster
et al.. 1959;
U.S. EPA. 1984
U.S. EPA, 1989/
Yang et al.,
1983; U.S. EPA.
1989, 1990
0627h
                                                                             A-73
                                                                                                                                                  07/12/90

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                           in ML i ri  mtLli AbbtbbMtNIb MJMMAKY  IABLI A: SUBCHKONIC ANU CHRONIC IOX1C11Y (OlHtK IHAN CAKCINOGEN1CI1Y)
                                                                      Update:     le,  1990
      Compound
                              Exposure
   Inhalation; Oral
                              Species
Inhalation  Oral
        Effect of Concern
        Inhalation; Oral
                                                Reference  Dose
                                 Uncertainty Factor
                                 Reference
    Inhalation          Oral     Inhalation    Oral  Inhalation/Oral
[mg/n)3 (mg/kg/day)]  (mg/kg/day)
chronic (RfD)



Selenourea
subchronlc (RfOs)




chronic (RfD)




Silver
subchronlc (RfOs)











NA: 3.2 mg/day from NA human NO; hair and nail NO
diet of selenlferous loss, dermatitis
foodstuffs (0.046
mg/kg/day)

NA; 0.046 mg/kg/day. NA human NA; selenosls NO
exposure to selenium In
high-selenium areas,
converted to 0.072
mg selenourea/kg/day
NA; 0.046 mg/kg/day. NA human NA; selenosls ND
exposure to selenium In
high-selenium areas.
converted to 0.072
mg selenourea/kg/day

NA; 0.9-1.5 g silver NA human NA; argyrla NO
arsphenamlne by l.v. for
2-3 years (average.
0.0031 mg/kg/day); 6.4 g
total dosage silver
nitrate In 1 year
(0.077 mg/kg/day); -6.4 g
total dosage silver
acetate over 2.5 years
(0.004B mg/kg/day)
Average of 3 studies.
0.0052 mg/kg/day
3E-3J NA 15 U.S. EPA. 1989/
Yang et al..
1983; U.S. EPA,
1989, 1990

5E-3 NA 15 NA/Yang et al..
1983; U.S. EPA,
1990


5E-3Z NA 15 NA/Yang et al..
1983; U.S. EPA.
1990



3E-3 NA 2 NA/Gaul and
Staud. 1935;
Blumberg and
Carey. 1934;
East et al..
1980; U.S. EPA.
1990





  chronic (RfD)
NA; 0.9-1.5 g silver
arsphenamlne by l.v. for
2-3 years (average.
0.0031 mg/kg/day); 6.4 g
total dosage silver
nitrate In 1 year
(0.077 mg/kg/day); -6.4 g
total dosage silver
acetate over 2.5 years
(0.0048 mg/kg/day)
Average of 3 studies,
0.0052 mg/kg/day
 NA
human    NA; argyrla
     ND
3E-3a
NA
NA/Gaul and
Staud. 1935;
Blumberg and
Carey, 1934;
East et al.,
1980; U.S. EPA.
1990
0627h
                                                     A-74
                                                                                                07/12/90

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   Ill Ml I II |_ | I
                                                      aunrwKi iMdLt «. iUULHKUNIU ANU (.HKUNll lUXltllT (UIHtK IHAN CAKUNOGtNlCl IY)
                                                                      Update     me,  1990
Compound
Silver cyanide
subchronlc (RfDs)
chronic (RfD)
Exposure
Inhalation; Oral
NA; 10.B mg/kg/day
fumigated cyanide In
food for 2 years
(55.7 mg silver
cyanlde/kg/day)
NA; 10.8 mg/kg/day
fumigated cyanide In
food for 2 years
(55.7 mg silver
cyanide/kg/day)
Species Effect of Concern Reference Dose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
NA rat NA; weight loss, NO 1E-1" NA 500
thyroid effects and
myelln degeneration
NA rat NA; weight loss, ND !E-l*>n NA 500
thyroid effects and
myelln degeneration
Reference
Inhalation/Oral
NA/Howard and
Hanzal. 1955;
Phllbrlck et
al.. 1979; U.S.
EPA, 1990
NA/Howard and
Hanzal, 1955;
Phllbrlck et
al., 1979; U.S.
EPA. 1990
Slmazlne
  subchronlc (RfDs)
  chronic (RfO)
Sodium cyanide
  subchronlc (RfOs)
  chronic (RfD)
Sodium dlethyldlthlo-
carbamate
  subchronlc (RfDs)
NA; 0.52 mg/kg/day In     NA         rat
In the diet for 2 years
NA; 0.52 mg/kg/day In     NA         rat
In the diet for 2 years
NA; 10.8 mg CN/kg/day     NA         rat
from diet containing
HCN (equivalent to
NaCN at 20.4 mg/kg/day)

NA; 10.8 mg CN/kg/day     NA         rat
from diet containing
HCN (equivalent to
NaCN at 20.4 mg/kg/day)
NA; 30 mg/kg/day for      NA         rat
90 days
NA; decreased weight   ND
gain, hematologlcal
effects
NA; decreased weight   ND
gain, hematologlcal
effects
NA; CNS
NA; CNS
NA; decreased body
weight gain, renal
and hemotologlcal
effects
ND
ND
ND
                  2E-3
                  2E-3a
4E-2"
4E-2a«n
3E-1
              NA       300    U.S. EPA. 1984/
                              Clba-Gelgy
                              Corp.. 1988;
                              U.S. EPA, 1984,
                              1990

              NA       300    U.S. EPA, 19B4/
                              Clba-Gelgy
                              Corp., 1988;
                              U.S. EPA. 1984,
                              1990
NA       500    U.S. EPA. 1984/
                Howard and
                Hanzal, 1955;
                U.S. EPA. 1984

NA       500    U.S. EPA. 19B4/
                Howard and
                Hanzal. 1955;
                U.S. EPA. 1984.
                1990
NA       100    U.S. EPA. 198B/
                Sunderman
                et al., 1967;
                U.S. EPA, 1988
0627h
                                                     A-75
                                                                            07/12/90

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                           HtALIII mtCIS ASStSSHLNIS SUMMARY I ABLE A: SUBCHR^'C AND CHRONIC TOXICIIY (OTHER 1HAN CARCINOGENICI1Y)
                                                                      Update     ie,  1990
Compound
chronic (RfD)
Sodium metavanadate
subchronlc (RfDs)
chronic (RfD)
Strychnine
subchronlc (RfDs)
chronic (RfD)
Styrene
subchronlc (RfDs)
chronic (RfD)
Exposure
Inhalation; Oral
NA; 30 mg/kg/day for
90 days
NA; 10 ppm sodium
metavanadate In drink-
Ing water for 3 months
(1.32 mg sodium meta-
vanadate/kg/day)
NA; 10 ppm sodium
metavanadate In drink-
Ing water for 3 months
(1.32 mg sodium meta-
vanadate/kg/day)
NA; 2.5 mg/kg by
gavage for 28 days
NA; 2.5 mg/kg by
gavage for 28 days
NA; 200 mg/kg/day by
gavage for 19 months
NA; 200 mg/kg/day by
gavage for 19 months
Species Effect of Concern Reference Dose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
NA rat NA; cataracts and NO 3E-2a NA 1000
reduced body weight
In chronic study
(Cancer: see
Table B)
NA rat NA; Impaired kidney ND 1E-2 NA 100
function
NA rat NA; Impaired kidney ND 1E-3 NA 1000
function
NA rat NA; toxlclty ND 3E-3 NA 1000
hlstopathology
NA rat NA; toxlclty ND 3E-4« NA 10000
hlstopathology
NA dog NA; red blood cell ND 2E*0 NA 100
and liver effects
NA dog NA; red blood cell ND 2E-1Z NA 1000
and liver effects
(also see Table B)
Reference
Inhalation/Oral
U.S. EPA, 1988/
Sunderman
et al.. 1967;
U.S. EPA, 1988
1990
U.S. EPA, 1987/
Domingo
et al., 1985;
U.S. EPA, 1987
U.S. EPA. 1987/
Domingo
et al.. 1985;
U.S. EPA, 1987
NA/Seldl and
Zblnden, 1982;
U.S. EPA. 1990
NA/Seldl and
Zblnden. 1982;
U.S. EPA. 1990
U.S. EPA, 1990/
Quast et al..
1979; U.S. EPA,
1984, 1989, 1990
U.S. EPA. 1990/
Quast et al.,
1979; U.S. EPA.
1984. 1989. 1990
Stlrophos (see Tetrachlorvlnphos)
Succlnonltrlle

DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
U.S. EPA. 1987
0627h
                                                                             A-76
07/12/90

-------
Hint III IIILljItJ flouL^O
Exposure
Compound Inhalation; Oral
Sulfurlc acid
subchronlc (RfOs) 0.066-0.098 mg/m3
occupational; NA
chronic (RfD) 0.066-0.098 mg/m3
occupational; NA
Temephos
subchronlc (RfDs) NA; 200 ppm In the diet
for 99 days (11-24
mg/kg/day)
chronic (RfD) NA; 200 ppm In the diet
for 99 days (11-24
mg/kg/day)
Terbufos
subchronlc (RfDs) NA; 0.01 mg/kg/day In
the diet for 6 months
chronic (RfD) NA; 0.01 mg/kg/day In
the diet for 6 months
Terephthallc acid
1,2,4,5-Tetrachlorobenzene
subchronlc (RfDs) NA; 50 ppm In diet for
13 weeks (converted to
0.34 mg/kg/day by
authors)
chronic (RfO) NA; 50 ppm In diet for
13 weeks (converted to
0.34 mg/kg/day by
authors)
Tetrachloroazoxybenzene (TCAOB)
Tetrachlorocyclopentadlene

Species
Inhalation Oral
human NA
human NA
NA rat
NA rat
NA dog
NA dog
DATA
NA rat


NA rat


DATA
DATA
Update: \ 1990
Effect of Concern Reference Dose Uncertainty Factor
Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
respiratory; NA NDW NO NA NA
respiratory; NA NDW ND NA NA
NA; no effect ND 2E-1 NA 100
NA; no effect ND 2E-2 NA 1000
NA; no effect ND 1E-49 NA 100
NA; no effect NO IE -49 NA 100
INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA; kidney lesions ND 3E-3 NA 100


NA; kidney lesions ND 3E-48 NA 1000


INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT'

Reference
Inhalation/Oral
Carson et al.,
1981; U.S. EPA,
1984/NA
Carson et al.,
1981; U.S. EPA
1984/NA
U.S. EPA, 1984/
Galnes et al.,
1967; U.S. EPA,
1984
U.S. EPA. 1984/
Galnes et al.,
1967; U.S. EPA,
1984
U.S. EPA. 1984/
U.S. EPA. 1984
U.S. EPA. 1984/
U.S. EPA. 1984
U.S. EPA. 1984
NA/Chu et al..
1984; U.S. EPA.
loon
1990

NA/Chu et al..
1984; U.S. EPA,
loon
1990

U.S. EPA. 1985
U.S. EPA, 1988
0627h
                                                                             A-77
                                                                                                                                                  07/12/90

-------

Exposure
Compound Inhalation; Oral
Tetrachloroethylene
(perchloroethylene)
subchronlc (RfD$) NA; 20 rag/kg 5 days/week
for 6 weeks
(14 mg/kg/day)

chronic (RfD) NA; 20 rag/kg 5 days/week
for 6 weeks
(14 mg/kg/day)

Tet/achlorohydrazobenzene (TCHB)
2.3,4.6-Tetrachlorophenol
subchronlc (RfD$) NA; 25 mg/kg/day for
90 days
chronic (RfD) NA; 25 mg/kg/day for
90 days
Tetrachlorophenol. 2.3.4.5-.
2.3.5.6-
1.1.2.3-Tetrachloropropene
Tetrachlorovlnphos
(Stlrofos)
subchronlc (RfDs) NA; 125 ppm In the
diet for 2 years
(3.1 mg/kg/day)
chronic (RfD) NA; 125 ppm In the
diet for 2 years
(3.1 mg/kg/day)

Update: ~-ne, 1990
Species Effect of Concern Reference Dose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral innaianon oral
[mg/m3 (mg/kg/day)] (mg/kg/day)

NA mouse NA; hepatotoxlclty NO 1E-1 NA 100


NA mouse NA; hepatotoxlclty NO 1E-2* NA 1000
(Cancer: see
Table B)

DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA rat NA; Increased liver ND 3E-1 NA 100
weights and centrl-
lobular hypertrophy
NA rat NA; Increased liver ND 3E-2a NA 1000
weights and centrl-
lobular hypertrophy
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT

DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT

NA dog NA; Increased liver ND 3E-2 NA 100
and kidney weights,
reduced body
weight gain
NA dog NA; Increased liver ND 3E-2a NA 100
and kidney weights.
reduced body weight
gain (Cancer: see
Table B)

Reference
Inhalation/Oral

U.S. EPA, 19B8/
Buben and
O'Flaherty,
1965; U.S. EPA,
1990
U.S. EPA, 198B/
Buben and
O'Flaherty,
1985; U.S. EPA.
1990
U.S. EPA, 1985
U.S. EPA, 1987/
U.S. EPA, 1986,
1990
U.S. EPA, 1987/
U.S. EPA, 1986.
1990
U.S. EPA, 1987

U.S. EPA, 1983

U.S. EPA, 1990/
Shell Chem. Co.,
1968; U.S. EPA.
1984, 1990
U.S. EPA. 1990/
Shell Chem. Co.,
1968; U.S. EPA,
1984, 1990

0627h
                                                                             A-78
                                                                                                                                                  07/12/90

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                                                                     Update:
                                                                                    1990
Compound

Inhalation; Oral
Tetraethyl dlthlopyrophosphate
subchronlc (RfOs) NA; 10 ppm 1n diet
for 3 months (0.5
mg/kg/day)
chronic (RfD) NA; 10 ppm In diet
for 3 months (0.5
Species Effect of Concern
Inhalation Oral Inhalation; Oral
NA rat NA; depressed RBC
and plasma
chollnesterase
activity
NA rat NA; depressed RBC
and plasma
Reference Dose Uncertainty Factor
Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)} (mg/kg/day)
NO 5E-3 NA 100
NO 5E 4* NA 1000
Reference
Inhalat lon/ura i
NA/Klmmerle and
Kllmmer. 1974;
U.S. EPA, 1990
NA/Klmmerle and
Kllmmer. 1974;
U.S. EPA. 1990
                        mg/kg/day)
                                                                     activity
Tetraethyl lead
  subchronlc (RfDs)
  chronic (RfD)
Thalllc oxide
[Thallium!Ill) oxide]
  subchronlc (RfDs)
  chronic (RfD)
NA; 1.7 pg/kg/day In
peanut oil by gavage
for 20 weeks. 5 days/
week (1.2 vg/kg/day)

NA; 1.7 wg/kg/day In
peanut oil by gavage
for 20 weeks. 5 days/
week (1.2 pg/kg/day)
NA; 0.02 mg thallium/kg/
day (from thallium
sulfate) for 90 days

NA; 0.02 mg thallium/kg/
day (from thallium
sulfate) for 90 days
NA
                                                  NA
Thallium (In soluble salts)
  subchronlc (RfDs)     NA; 0.20 mg thallium/kg/
                        day (from thallium
                        sulfate) for 90 days
  chronic  (RfD)
 Thalllum(I) acetate
   subchronlc  (RfDs)
 0627h
 NA; 0.20 mg  thallium/kg/
 day (from  thallium
 sulfate) for  90  days
 NA;  0.20  mg  thallium/kg/
 day  (from thallium
 sulfate)  for  90  days
NA
                                                  NA
                          NA
                                                  NA
 NA
                                     rat
           rat
         NA;  hlstopathology
         of  liver  and  thymus
                                                                    NO
rat
           rat
           rat
                                     rat
                                     rat
         NA;  hlstopathology      NO
         of  liver  and  thymus
1E-7          NA    10,000    NA/Schepers.
                              1964;  U.S.  EPA,
                              1990
1E-7*         NA    10,000    NA/Schepers,
                              1964; U.S.  EPA.
                              1990
NA; Increased SCOT NO
and serum LOH
levels, alopecia
NA; Increased SCOT NO
and serum LDH
levels, alopecia
NA; Increased SGOT NO
and serum LDH
levels, alopecia
NA; Increased SGOT NO
and serum LOH
levels, alopecia
NA; Increased SGOT ND
and serum LDH
levels, alopecia

7E-4 NA 300 U.S. EPA. 1988/
HRI, 1986;
U.S. EPA, 1986
7E-5V NA 3000 U.S. EPA. 1988/
NRI. 1986;
U.S. EPA. 1986
7E-4 NA 300 U.S. EPA. 198B/
MRI. 1986;
U.S. EPA, 1986
7E-5 NA 3000 U.S. EPA. 1988/
NRI. 1986;
U.S. EPA, 1986
9E-4 NA 300 U.S. EPA. 19BB/
HRI. 1986;
U.S. EPA. 1986.
i o An
1990
                                                                             A-79

-------
mm m LI 1 1 10
                                                      &unnAK>  irtbLt A: bUUlHKUNIl ANU LHKUNIL  IUX111IY (UIHtK  IHAN CAKC1NOGENIC1 IV)
                                                                      Update:     \e.  1990
Compound
•
chronic (RfD)
Thallium! I) carbonate
subchronlc (RfDs)
chronic (RfO)
Thalllum(I) chloride
subchronlc (RfOs)
chronic (RfO)
Thallium! I) nitrate
subchronlc (RfDs)
chronic {RfD)
Exposure Species
Inhalation; Oral Inhalation Oral
NA; 0.20 mg thallium/kg/ NA rat
day (from thallium
sulfate) for 90 days
NA; 0.20 mg thallium/kg/ NA rat
day (from thallium
sulfate) for 90 days
NA; 0.20 mg thallium/kg/ NA rat
day (from thallium
sulfate) for 90 days
NA; 0.20 mg thallium/kg/ NA rat
day (from thallium
sulfate) for 90 days
NA; 0.20 mg thai Hum/kg/ NA rat
day (from thallium
sulfate) for 90 days
NA; 0.20 mg thallium/kg/ NA rat
day (from thallium
sulfate) for 90 days
NA; 0.20 mg thallium/kg/ NA rat
day (from thallium
sulfate) for 90 days
Thallium selenlte (Tl2Se)
subchronlc (RfDs) NA; 0.20 mg thallium/kg/ NA rat
day (from thallium
sulfate) for 90 days
Effect of Concern Reference
Inhalation; Oral Inhalation
[mg/m3 (mg/kg/day)]
NA; Increased SGOT NO
and serum LDH
levels, alopecia
NA; Increased SGOT NO
and serum LOH
levels, alopecia
NA; Increased SGOT NO
and serum LDH
levels, alopecia
NA; Increased SGOT ND
and serum LDH
levels, alopecia
NA; Increased SGOT ND
and serum LDH
levels, alopecia
NA; Increased SGOT ND
and serum LDH
levels, alopecia
NA; Increased SGOT ND
and serum LDH
levels, alopecia
NA; Increased SGOT ND
and serum LDH
levels, alopecia
Dose Uncertainty Factor
Oral Inhalation Oral
(mg/kg/day)
9E-5a NA 3000
8E-4 NA 300
8E-5a NA 3000
BE -4 NA 300
BE -5* NA 3000
9E-4 NA 300
9E-5a NA 3000
9E-4 NA 300
Reference
Inhalation/Oral
U.S. EPA, 19BB/
NRI, 19B6;
U.S. EPA, 19B6,
1990
U.S. EPA, 198B/
NRI. 1986;
U.S. EPA, 1986.
1990
U.S. EPA. 1988/
NRI, 1986;
U.S. EPA, 1986,
1990
U.S. EPA, 198B/
NRI. 1986;
U.S. EPA. 1986,
1990
U.S. EPA, 1988/
NRI, 1986;
U.S. EPA, 1986.
1990
U.S. EPA, 1988/
NRI. 1986;
U.S. EPA, 1986,
1990
U.S. EPA, 1988/
NRI. 1986;
U.S. EPA, 1986,
1990
U.S. EPA. 1988/
NRI. 1986;
U.S. EPA. 1986.
1990
0627h
                                                                             A-80
                                                                                                                       07/12/90

-------


Compound
chronic (RfD)
Thalllum(I) sulfate
subchronlc (RfDs)
chronic (RfO)
2-(Th1ocyanomethylth1o)-
benzothlazole (TCNTB)
subchronlc (RfDs)
chronic (RfD)
Thlofanox
subchronlc (RfOs)
chronic (RfD)
Thlram
subchronlc (RfDs)
chronic (RfD)

Exposure Species
Inhalation; Oral Inhalation Oral
NA; 0.20 mg thallium/kg/ NA rat
day (from thallium
sulfate) for 90 days
NA; 0.25 mg/kg/day for NA rat
90 days
NA; 0.25 mg/kg/day for NA rat
90 days
NA; 333 ppm In the diet NA rat
diet, subchronlc (25 mg/
kg/day)
NA; 333 ppm In the diet NA rat
diet, subchronlc (25 mg/
kg/day)
NA; 0.025 mg/kg/day NA dog
for 8 days
NA; 0.025 mg/kg/day NA dog
for 8 days
NA; 0.61 mg/kg/day NA ferret
for 24 weeks
NA; 0.61 mg/kg/day NA ferret
for 24 weeks
Update: ie, 1990
Effect of Concern Reference
Inhalation; Oral Inhalation
[ing/in3 (mg/kg/day)]
NA; Increased SGOT ND
and serum LOH
levels, alopecia
NA; Increased SGOT ND
and serum LDH
levels, alopecia
NA; Increased SGOT ND
and serum LOH
levels, alopecia
NA; stomach ND
lesions
NA; stomach ND
lesions
NA; chollnesterase ND
Inhibition
NA; chollnesterase ND
Inhibition
NA; Impaired ND
reproduction
NA; Impaired ND
reproduction

Dose Uncertainty Factor
Oral Inhalation Oral
(mg/kg/day)
9E-5Z NA 3000
8E-4 NA 300
8E-5a NA 3000
3E-1 NA 100
3E-2 NA 1000
3E-4 NA 100
3E-49 NA 100
6E-3 NA 100
6E-3a NA 100

Reference
Inhalation/Oral
U.S. EPA, 19B8/
NRI, 1986;
U.S. EPA. 1986,
1990
U.S. EPA. 1988/
NRI, 1986;
U.S. EPA, 1986.
1990
U.S. EPA. 1988/
NRI, 1986;
U.S. EPA, 1986.
1990
U.S. EPA. 1984/
U.S. EPA, 1984
U.S. EPA, 1984/
U.S. EPA. 1984
U.S. EPA, 1989/
U.S. EPA. 1989
U.S. EPA. 1989/
U.S. EPA. 1989
U.S. EPA. 1989/
Hornshaw et al..
1987; U.S. EPA.
1989, 1990
U.S. EPA, 1989/
Hornshaw et al.,
1987; U.S. EPA,
1989, 1990
0627h
A-81
07/12/90

-------

Exposure Species
Compound Inhalation; Oral Inhalation Oral
Tin and Compounds
subchronlc (RfDs) NA; 2000 ppm stannous NA rat
chloride In diet for 2
years (62 mg Sn/kg/day)
chronic (RfD) NA; 2000 ppm stannous NA rat
chloride In diet for 2
vears (62 mo Sn/ka/dav)
Update- 
-------
                                                  Wli  5Uriri«KI  IMOlt «: iUBLMKUNIL ANU LHKUMK  lUAiUlt \UIMIK I HAN lAKUNUbtNlLl I I)
                                                                     Update:    ic, 1990
Compound
m-Tolu1d1ne
Trlallate
subchronk (RfDs)
chronic (RfD)
1.2,4-Tr Ibromobenzene
subchronk (RfDs)
chronic (RfD)
Exposure
Inhalation; Oral

NA; 1.3 mg/kg/day In
the diet for 24 months
NA; 1.3 mg/kg/day In
the diet for 24 months
NA; 5 mg/kg/day In the
diet for 45 or 90 days
NA; 5 mg/kg/day In the
diet for 45 or 90 days
Species Effect of Concern Reference Dose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA dog NA; spleen and ND 1.3E-2 NA 100
and liver
NA dog NA; spleen and liver ND 1.3E-2a>aa NA 100
and liver
NA rat NA; liver weight ND 5E-2 NA 100
and enzyme
Induction
NA rat NA; liver weight ND 5E-3a NA 1000
and enzyme
Induction
Reference
Inhalation/Oral
U.S. EPA, 1984
U.S. EPA. 1990/
Monsanto Co..
1979; U.S. EPA.
1990
U.S. EPA, 1990/
Monsanto Co.,
1979; U.S. EPA.
1990
U.S. EPA, 1990/
Carlson and
Tardlff. 1977;
U.S. EPA. 1984,
1990
U.S. EPA, 1990/
Carlson and
Tardlff, 1977;
U.S. EPA. 1984.
1990
Trlbromomethane (see Bromoform)

1,2.4-Trlchlorobenzene
  subchronk (RfDs)     3 ppm (22 mg/m3) 6
                        hours/day. 5 days/
                        week for 3 months
                        (2.5 mg/kg/day);
                        20 mg/kg/day by
                        gavage for 90 days
  chronic (RfD)
3 ppm (22 mg/m3) 6
hours/day, 5 days/
week for 3 months
(2.5 mg/kg/day);
20 mg/kg/day by
gavage for 90 days
                          rat        rat      Increased  uropor-
                                              phyrln;  Increased
                                              llver-to-body
                                              weight  ratio
rat        rat      Increased uropor-
                    phyrln;  Increased
                    llver-to-body
                    weight ratio
                                           9E-2  (3E-2)        2E-1          100        100    Watanabe et al..
                                                                                          1978; U.S. EPA,
                                                                                          1987/Carlson and
                                                                                          Tardlff, 1976;
                                                                                          U.S. EPA.  1987
9E-3 (3E-3)       2E-2V       1000      1000    Uatanabe et al.,
                                                1978; U.S.  EPA.
                                                1987/Carlson and
                                                Tardlff, 1976;
                                                U.S. EPA, 1987
0627h
                                                                             A-83
                                                                                                                                                  07/12/90

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                          HtALIH tmUb AbbLSSMUm SUMMAKY IABU A: SUHCHKUNK ANU LHHONR lUXKllY  (UIHIK  IHAN  lAKUNUbtNlU 11)
                                                                     Update     me,  1990
Exposure
Compound Inhalation; Oral
Trlchlorocyclopentadlene
1,1,1-Trlchloroethane
subchronlc (RfDj) 500 ppm (2730 mg/m3)
7 hours/day, 5 days/
week for 6 months
(304 mg/kg/day); 500
ppm (2730 mg/m3) 7
hours/day for 6 months
(90 mg/kg/day )b
chronic (RfD) 500 ppm (2730 mg/m3)
7 hours/day, 5 days/
week for 6 months
(304 mg/kg/day); 500
ppm (2730 mg/m3) 7
hours/day for 6 months
(90 mg/kg/day )b
1,1,2-Trlchloroethane
subchronlc (RfD$) NA; 3.9 mg/kg/day by
drinking water for 90
days

Species Effect of Concern Reference Dose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT1
guinea guinea hepatotoxlclty; 1E*1 (3E*0)* 9E-lb 100 100
pig pig hepatotoxlclty


guinea guinea hepatotoxlclty; 1E+0 (3E-1)S 9E-2M 1000 1000
P'9 P^ hepatotoxlclty1


NA mouse NA; clinical NO 4E-2 NA 100
chemistry altera-
tions

Reference
Inhalation/Oral
U.S. EPA. 1988
Torkelson et
al.. 1958;
U.S. EPA, 1990/
Torkelson et
al., 1958;
U.S. EPA, 1990

Torkelson et
* 1 1OCQ .
al., 1958;
U.S. EPA. 1990/
Torkelson et
al.. 1958;
U.S. EPA, 1990

U.S. EPA. 1984/
White et al..
1985; Sanders
et al.. 1985;
U.S. EPA, 1990
  chronic (RfD)
NA; 3.9 mg/kg/day by
drinking water for 90
days
NA         mouse    NA;  clinical
                    chemistry altera-
                    tions  (Cancer:
                    see  Table B)
                                                                                            ND
4E-33         NA      1000    U.S.  EPA,  1984/
                              White et al..
                              1985; Sanders
                              et al..  1985;
                              U.S.  EPA,  1990
Trlchlorofluoromethane
(F-ll)
subchronlc (RfDg)
5600 mg/m3 contln- dog
uously for 90 days
(1940 mg/kg/day);
1000 mg/kg/day, 5
days/week for 6 weeks
(714.3 mg/kg/day)
rat elevated BUN, lung 7E+0 (2E+0) 7E-1
lesions; mortality
1000 1000 Jenkins et al.,
1970; U.S. EPA,
1987/NCI. 1978;
U.S. EPA. 1987
0627h
                                                                             A -84
                                                                                                                                                 07/12/90

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                              I II 111. I II LIILUIJ
                                                             omnium  i noc i  M.  juuiiinuiiit.  nnu Minuinii.  iuAit.il I  (UIIILH limn  initv.iiiuuLiiii.iii/
                                                                              Update-     ne,  1990
Compound
chronic (RfD)
Exposure
Inhalation; Oral
5600 mg/m3 contin-
uously for 90 days
(1940 mg/kg/day);
488 mg/kg/day. 5
days/week for 66 weeks
(348.6 mg/kg/day)
2,4,4'Trlchloro-
2'-hydroxyd1phenyl ether
subchronlc (RfDs) NA; 500 mg/kg. 6 days/
week for 4 weeks (429
mg/kg/day)
chronic (RfO)
TMchloromethane (see
Trtchlorophenol. 2.3.
2.3.6-. and 3.4.5-
2,4,5-Trlchlorophenol
subchronlc (RfO$)
chronic (RfO)
2,4.6-Trlchlorophenol
2.4.5-Trlchloro-
phenoxyacetlc acid
subchronlc (RfDs)
NA; NA
Chloroform)
4-. 2.3,5-.
NA; 1000 ppm of diet
for 98 days (100 rag/
kg/day)
NA; 1000 ppm of diet
for 98 days (100 mg/
kg/day)
- see Table B
NA; 10 mg/kg/day for
90 days
Species Effect of Concern Reference Dose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
dog rat elevated BUN. lung 7E-1 (2E-1) 3E-la 10,000 1000
lesions; mortality
NA rat NO; NO ND 4E+0 NA 100
NA NA ND; ND ND ND NA NA

DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA rat NA; hepatotoxlclty, ND 1E*0 NA 100
kidney effects
NA rat NA; hepatotoxlclty. ND lE-la NA 1000
kidney effects

NA rat NA; liver and ND 1E-1 NA 100
kidney weights
Reference
Inhalation/Oral
Jenkins et al..
1970; U.S. EPA,
19B7/NCI. 1978;
U.S. EPA. 1987.
1990
U.S. EPA. 1987/
Lyman and
Furla. 1969;
U.S. EPA, 1987
U.S. EPA, 1987/
U.S. EPA, 19B7

U.S. EPA. 1967
U.S. EPA. 1984.
1987/McCol lister
et al.. 1961;
U.S. EPA, 1984,
1987
U.S. EPA. 1984,
1987/McCol lister
et al., 1961;
U.S. EPA, 1984.
1987. 1990

U.S. EPA. 1989/
Gehrlng and
Betso. 1978;
U.S. EPA. 1989
0627h
                                                                                      A-85
07/12/90

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                           HtAMH IHILIS ASStbbMlNIb  SUMMARY  lABLt A:  SUBCHRO''" AND CHRONIC  IOX1CIIY (OIHLR 1HAN CARCINOGENICIIV)
                                                                     Update:     >. 1990
Compound
chronic (RfO)
Exposure
Inhalation; Oral
NA; 3 mg/kg/day
3-generatlon study
?(2.4.5-Tr1chlorophenoxy)
proplonlc acid (Sllvex)
subchronlc (RfOs) NA; 30 ppm In diet
for 2 years (0.75
mg/kg/day)
chronic (RfO)
1,1.1-Trlchloropropane
1.2,2-Trlchloropropane
1,1.2-Trlchloropropane
subchronlc (RfDs)
chronic (RfD)
1.2,3-Trlchloropropane
subchronlc (RfDs)
NA; 30 ppm In diet
for 2 years (0.7S
mg/kg/day)


NA; 100 mg/t In drinking
water for 13 weeks
(IS mg/kg/day)
NA; 100 mg/l In drinking
water for 13 weeks
(15 mg/kg/day)
NA; 8 mg/kg 5 days/week
for 120 days (5.7
mg/kg/day)
Species Effect of Concern Reference Dose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
NA rat NA; decreased NO lE-2a NA 300
survival
NA dog NA; hlstopathologlcal NO 8E-3 NA 100
changes In liver
NA dog NA; hlstopathologlcal ND 8E-3a NA 100
changes In liver
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA rat hlstopathologlcal ND 5E-2 NA 300
lesions In liver,
kidney and thyroid
NA rat hlstopathologlcal ND 5E-3a NA 3000
lesions In liver.
kidney and thyroid
NA rat NA; transient dint- ND 6E-2 NA 100
cal signs, liver
and kidney lesions,
decrease In RBC,
hematocrlt and
hemoglobin
Reference
Inhalation/Oral
U.S. EPA, 1989/
Koclba et al.,
1979; U.S. EPA,
1989. 1990
NA/Nulllson,
1966. Gehrlng
and Betso, 1978;
U.S. EPA, 1990
NA/Hulllson.
1966, Gehrlng
and Betso, 1978;
U.S. EPA. 1990
U.S. EPA. 1987/
U.S. EPA, 1987
U.S. EPA, 1987/
U.S. EPA, 1987
U.S. EPA. 1987/
Vlllaneuve
et al.. 1985;
U.S. EPA. 1990
U.S. EPA. 1987/
Vlllaneuve
et al.. 1985;
U.S. EPA, 1990
U.S. EPA, 1987/
NTP, 1983;
U.S. EPA, 1987
0627h
                                                                             A-86
07/12/90

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                                                                    Update:  ' ie. 1990

Compound
chronic (RfD)
1.2.3-Trkhloropropene
subchronk (RfOs)
chronic (RfD)
2.3.6-Trlchlorotoluene
subchronk (RfOs)
chronic (RfD)
a,2,6-Trkhloro-
toluene
subchronk (RfOs)
chronk (RfD)
l.l,?-lrkhloro-1.2.2-
trlfluoroethane
subchronk (RfDs)


Inhalation; Oral Inhalation Oral
NA; 6 mg/kg 5 days/week NA rat
for 120 days (5.7
mg/kg/day)
3 ppro (18 mg/m3). dog NA
6 hours/day. 5 days/week
for 66 weeks; NA
3 ppm (IB mg/m3). dog NA
6 hours/day. 5 days/week
for 66 weeks; NA
NA; 0.5 ppm In diet NA rat
(0.05 mg/kg/day) for
28 days
NA; NA NA NA
NA; 0.5 ppm 1n diet NA rat
(0.05 mg/kg/day) for
28 days
NA; NA NA NA
5358 mg/m3 occupational human NA
for 2.77 years (273
mg/kg/day); NA

Effect of Concern Reference
Inhalation; Oral Inhalation
[mg/m3 (mg/kg/day)]
NA; transient cllnl- NO
cal signs, liver
and kidney lesions,
decrease In RBC,
hematocrlt and
hemoglobin
eye Irritation; NO
NA
eye Irritation; ND
NA
NA; liver kidney, ND
thyroid lesions
NA; NA ND
NA; liver, kidney. ND
thyroid lesions
NA; NA ND
psychomotor Impair- ND
ment; NA
A-87
Dose Uncertainty Factor
Oral Inhalation Oral
(mg/kg/day)
6E-3a NA 1000
SE-3b NA 100
5E-3b NA 100
5E-5 NA 1000
ND NA NA
5E-5 NA 1000
ND NA NA
3E+1 NA 10

Reference
Inna lat lon/ura i
U.S. EPA. 1987/
NTP, 1983;
U.S. EPA. 1987.
1990
U.S. EPA, 1983/
NcKenna et al..
1978; U.S. EPA,
1983
U.S. EPA, 1983/
NcKenna et al.,
1978; U.S. EPA,
1983
U.S. EPA. 1987/
Chu et al.,
1984; U.S. EPA,
1987
U.S. EPA. 1987/
U.S. EPA, 1987
U.S. EPA. 1987/
Chu et al.,
1984; U.S. EPA,
1987
U.S. EPA. 19B7/
U.S. EPA, 1987
Imbus and
Adktns, 1972;
U.S. EPA. 1983.
1985/Imbus and
Adklns. 1972;
U.S. EPA, 1983.
1990
07/1 Z/9U
0627h

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                                                                  muLi  n. ouuv-imim»».  m«u uinuinit.  IUAILIII  IUIIILH  nmn  LHitt inuoLNik.1 i I /
                                                                          Update:    ne.  1990
Compound
chronic (RfO)
Trlfluralln
subchronk (Rf05)
chronic (RfO)
•
Trlmethylbenzenes
1.3,5-TMnltrobenzene
subchronk (RfDs)
chronic (RfO)
Trlnltrophenols
Vanadium
subchronk (RfDs)
Exposure Species
Inhalation; Oral Inhalation Oral
5338 mg/m3 occupational human NA
for 2.77 years (273
mg/kg/day); NA
NA; 30 ppm In the diet NA dog
for 12 months (0.75
mg/kg/day)
NA; 30 ppm 1n the diet NA dog
for 12 months (0.75
mg/kg/day)
DATA
NA; 3 ppm 1.3-dlnltro- NA rat
benzene In drinking water
for 16 weeks (0.4 mg/kg/
day equivalent to 0.51
mg/kg/day 1,3.5-trlnltro-
benzene)
NA; 3 ppm 1,3-dlnltro- NA rat
benzene In drinking water
for 16 weeks (0.4 mg/kg/
day equivalent to 0.51
mg/kg/day 1.3,5-trlnltro-
benzene)
DATA
NA; 5 ppm vanadium NA rat
from vanadyl sulfate
In drinking water for
lifetime (0.7 mg/kg/day)
Effect of Concern Reference Dose Uncertainty Factor
Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
psychomotor Impair- ND 3E»lb>z NA 10
ment; NA
NA; Increased liver ND 7.5E-3 NA 100
weight, me t nemo -
globlnemla
NA; Increased liver ND 7.5E-3a NA 100
weight, methemo-
globlnemla (Cancer:
see Table B)
INADEQUATE FOR QUANTITATIVE RISK ASSESSHENT
NA; Increased spleen ND 5E-4 NA 1000
weight
NA; Increased spleen ND 5E-5a NA 10.000
weight
INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA; none observed ND 7E-3 NA 100
Reference
Inhalation/Oral
Imbus and
Adklns, 1972;
U.S. EPA. 1983,
1985/Imbus and
Adklns. 1972;
U.S. EPA, 1983,
1990
U.S. EPA, 1990/
Hoechst. 1984;
U.S. EPA, 1984,
1990
U.S. EPA, 19907
Hoechst. 1984;
U.S. EPA. 1984,
1990
U.S. EPA. 1987
U.S. EPA, 1989/
Cody et al.,
1981; U.S. EPA,
1989, 1990
U.S. EPA, 1989/
Cody et al..
1981; U.S. EPA.
1989. 1990
U.S. EPA. 1984
U.S. EPA, 1987/
Schroeder
et al., 1970;
U.S. EPA, 1987
0627h
                                                                                  A-8B
07/12/90

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Compound
chronic (RfD)
Vanadium pentoxlde
subchronlc (RfDs)
chronic (RfD)
Vanadyl sulfate
subchronlc (RfDs)
chronic (RfD)
Vernolate
(Vernam)
subchronlc (RfDs)
chronic (RfD)
4-V1nyl-l-cyclohexene
0627h

Exposure
Inhalation; Oral
NA; 5 ppm vanadium
from vanadyl sulfate
In drinking water for
lifetime (0.7 mg/kg/day)
NA; 10 ppm vanadium
In diet from vanadium
pentoxlde for lifetime
(0.9 mg vanadium pent-
oxlde/kg/day)
NA; 10 ppm vanadium
In diet from vanadium
pentoxlde for lifetime
(0.9 mg vanadium pent-
oxlde/kg/day)
NA; 5 ppm vanadium from
vanadyl sulfate In
drinking water for life-
time (2.24 mg vanadyl
sulfate/kg/day)
NA; 5 ppm vanadium from
vanadyl sulfate In
drinking water for life-
time (2.24 mg vanadyl
sulfate/kg/day)
NA; 20 ppm In the diet
(1 mg/kg/day) reproduc-
tive
NA; 20 ppm In the diet
(1 mg/kg/day) reproduc-
tive


Update: ne, 1990
Species Effect of Concern Reference Dose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
NA rat NA; none observed ND 7E-3S NA 100
NA rat NA; none observed ND 9E-3 NA 100
NA rat NA; none observed ND 9E-3a NA 100
NA rat NA; none observed ND 2E-2 NA 100
NA rat NA; none observed ND 2E-2 NA 100
NA rat NA; decreased ND 1E-2 NA 100
body weight
NA rat NA; decreased ND lE-3a NA 1000
body weight
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
A-89

Reference
Inhalation/Oral
U.S. EPA, 19B7/
Schroeder et
al., 1970; U.S.
EPA, 1987. 1990
U.S. EPA, 19B7/
Stoklnger
et al., 1953;
U.S. EPA, 1987
U.S. EPA, 1987/
Stoklnger
et al., 1953;
U.S. EPA. 1987,
1990
U.S. EPA. 1987/
Schroeder
et al.. 1970;
U.S. EPA, 1987
U.S. EPA. 1987/
Schroeder
et al.. 1970;
U.S. EPA. 1987
U.S. EPA, 1983/
Stauffer Chem.
Co., 1983; U.S.
EPA, 1983, 1990
U.S. EPA, 1983/
Stauffer Chem.
Co., 1983; U.S.
EPA, 1983, 1990
U.S. EPA, 1983
07/12/90

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                           IIIMLMI LIILIIJ «iii
                                                      bunriHKi molt
                                            «. bUDLHKUMIL AMU CHKUN1L
                                              Update-     ne,  1990
                                                                                              IUA1LIII  (UIMLK IHMN lAKUNUbtNlU 1 1 I
      Compound
                              Exposure
  Inhalation; Oral
                              Species
Inhalation  Oral
Effect of Concern
Inhalation; Oral
                                                                                                 Reference Dose
    Inhalation
[mg/m3 (nig/kg/day)]
   Oral
(mg/kg/day)
                                                                        Uncertainty  Factor
                                                                        Inhalation     Oral
                                                        Reference
                                                     Inhalation/Oral
m-Xylene
  subchronlc (RfDs)
  chronic (RfO)
o-Xylene
  subchronlc (RfOs)
  chronic (RfO)
4750 mg/m3. 8 hours/      rat        rat
day. 7 days/week for
1 year (1009 mg/kg/
day)w; 500 mg/kg mixed
xylenes 5 days/week for
103 weeks (357 mg mixed
xylenes/kg/day)

4750 mg/m3, B hours/      rat        rat
day. 7 days/week for 1
year (1009 mg/kg/day)w;
250 mg/kg mixed xylenes
5 days/week for 103
weeks (179 mg mixed
xylenes/kg/day)


150 mg/m3 continuous      rat        rat
on days 7-14 of gesta-
tion (95.6 mg/kg/day);
500 mg/kg mixed xylenes
5 days/week by gavage
for 13 weeks (357 mg
mixed xylenes/kg/day)

4750 mg/m3, 8 hours/      rat        rat
day, 7 days/week for
1 year (1009 mg/kg/day);
250 mg/kg mixed xylenes
5 days/week for 103
weeks (179 mg mixed
xylenes/kg/day)
                     hepatomegaly;  none
                     observed
                     hepatomegaly;  hyper-
                     activity,  decreased
                     body weight.  In-
                     creased mortality
                     at  higher  dosage
                     fetotoxlclty;  none
                     observed
                     hepatomegaly;  hyper-
                     activity,  decreased
                     body weight.  In-
                     creased mortality at
                     higher  dosage
                        4E*0 (1E+0)       4E*0        1000       100    Tatral et al..
                                                                        1981; U.S. EPA,
                                                                        1989/NTP. 1986
                        7E-1 (2E-1)       2E+0        5000       100    Tatral et al..
                                                                        1981; U.S. EPA.
                                                                        1989/NTP, 1986;
                                                                        U.S. EPA. 1986
                        3E*0 (lE+0)bb     4E+0
                                    100       100    Ungvary et al..
                                                     1980; U.S. EPA.
                                                     1989/NTP, 1986
                        7E-1 (2E-1)       2E*0        5000       100    Tatral et al.,
                                                                        1981; U.S. EPA,
                                                                        1989/NTP, 1986;
                                                                        U.S. EPA. 1986
subchronlc (RfOs)
chronic (RfO)
20
for
NA
20
for
NA
ppm 7.5
5 days
ppm 7.5
5 days
hours/dav human rat
(27 mg/m3);
hours/dav human NA
(27 mg/m3);
CNS effects
and throat
tlon; NA
CNS
and
tlon
effects
throat
; NA
, nose 3E-1
Irrlta-
, nose 3E-1
Irrlta-
ND 100 NA Hake
1981
U.S.
U.S.
NO 100 NA U.S.
U.S.
et al
'EPA,
EPA,
EPA,
EPA.
• t
1989/
1989
1989/
1989
0627h
                                                                             A-90
                                                                                                                          07/12/90

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                                                                     Update-
                                                        ne. 1990
Compound
Xylenes. mixed
subchronlc (RfDs)







chronic (RfO)






Zinc
subchronlc (RfOs)





Exposure Species
Inhalation; Oral Inhalation Oral

20 ppm 7.5 hours/day human rat
for 5 days (27 mg/m3);
500 mg/kg mixed xylenes
5 days/week by gavage
for 13 weeks (357 mg
mixed xylenes/kg/day)


20 ppm 7.5 hours/dav human rat
for 5 days (27 mg/in*);
250 mg/kg mixed
xylenes 5 days/week for
103 weeks (179 mg mixed
xylenes/kg/day)


NA; 2.14 mg/kg/day NA human
therapeutic dosage




Effect of Concern Reference Dose Uncertainty Factor
Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)

CNS effects, nose 3E-1 4E*0 100 100
and throat Irrita-
tion; none observed





CNS effects, nose 3E-lJ 2E*Oa 100 100
and throat Irrita-
tion; hyperactlvlty.
decreased body
weight and Increased
mortality at
higher dosage1

NA; anemia NO 2E-1 NA 10





Reference
Inhalation/Oral

Hake et al..
1981;
Litton Blo-
netlcs. 1978;
U.S. EPA. 1989/
NTP. 1986;
U.S. EPA,
1990
Hake et al..
1981;
Carpenter et al.
1975; U.S. EPA,
1989/NTP. 1986;
U.S. EPA. 1989.
1990

U.S. EPA, 1984/
Porles et
al.. 1967;
Prasad et al..
1975; U.S. EPA.
1984
  chronic (RfD)
NA; 2.14 mg/kg/day
therapeutic dosage
NA
human    NA;  anemia
ND
2E-19         NA        10    U.S.  EPA,  1984/
                              Porles  et  al.,
                              1967; Prasad
                              et al.. 1975;
                              U.S.  EPA.  1984,
                              1990
Zinc cyanide
subchronlc (RfOs)




chronic (RfD)




NA; 10.8 mg/kg/day NA
fumigated cyanide In
food for 2 years
(67.5 mg zinc
cyanlde/kg/day)
NA; 10.8 mg/kg/day NA
fumigated cyanide In
food for 2 years
(67.5 mg zinc
cyanide/kg/day)
rat NA; weight loss, ND
thyroid effects and
myelln degeneration
•

rat NA; weight loss, ND
thyroid effects and
myelln degeneration


5E-2" NA 500 N A/Howard and
Hanzal, 1955;
Phllbrlck et
al.. 1979; U.S.
EPA. 1990
5E-2a>" NA 500 NA/Howard and
Hanzal, 1955;
Phllbrlck et
al.. 1979; U.S.
EPA. 1990
0627h
                                                     A-91
                                                                                               07/12/90

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Him 111 HHI.IJ
                                                      jurnuuii  inuLL »>.  auuuiKUNiL HWU umuitib iuMi.ni  IUIIIUH maw LHNLIMUUCHU,! 1 1
                                                                     Update:     ie.  1990
                                                                                                 Reference Dose
                                                                                              Uncertainty Factor
                                                                                                                                                Reference
Compound
Zinc phosphide
subchronlc (RfDs)
chronic (RfD)
Zlneb
subchrontc (RfOs)
chronic (Rfl))
Inhalation; Oral Inhalation Oral
NA; 50 ppm In diet NA rat
for 13 weeks, converted
to 3.4B mg/kg/day by
authors
NA; SO ppm In diet NA rat
for 13 weeks, converted
to 3.48 mg/kg/day by
authors
NA; 500 ppm In the diet NA rat
for 2 years (25 mg/kg/
day)
NA; 500 ppm In the diet NA rat
for 2 years (25 mg/kg/
day)
Inhalation; Oral Inhalation
[mg/m3 (mg/kg/day)]
NA; reduction of NO
food Intake and body
weight
NA; reduction of NO
food Intake and body
weight
NA; thyroid ND
hyperplasla
NA; thyroid ND
hyperplasla
Oral Inhalation Oral Inhalation/Oral
(mg/kg/day)
3E-3 NA 1000 NA/Bal et al.,
1980; U.S. EPA,
1990
3E-4* NA 10.000 NA/Bal et al..
1980; U.S. EPA.
1990
5E-2 NA 500 U.S. EPA. 1984/
Blackwell-Smlth
et al.. 1953;
U.S. EPA. 1984,
1990
5E-2a NA 500 U.S. EPA, 1984/
Blackwell-Smlth
et al.. 1953;
U.S. EPA, 1984.
1990
aVerified, available on IRIS
DBased on route-to-route extrapolation
cSpedf1cally related to organoleptlc threshold and potential for respiratory tract Irritation, not to systemic toxlclty
••Specifically related to organoleptlc threshold; safe concentration may be higher but data are Inadequate to assess.
"Inhalation study  with  antimony trloxlde  In  rats  (Watt,  1980.  1981. 1983; ASARCO. Inc.,  1980) provides  qualitative  evidence of lung cancer; cancer potency
 not estimated.
Calculated by analogy  to antimony by correcting for differences In molecular weight
QUnder review by RfD Work Group
"Because of background  dietary exposure, an RfDs for the oral route was not estimated.
^Verified 2 separate RfDs,  1E-3  for  food and  5E-4  for water.
^Verified; Workgroup concurrence on  final  data base file and  IRIS Input pending
0627h                                                                        A-92                                                                 08/01/90

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kCurrent  d,    ing water  standard of  1.3 mg/l;  Drinking  Water Criteria  Do,    .t  concluded toxlclty  data  were  Inadequate  for  calculation      n RfD  for
 copper.
'CRAVE-verlfled as a CAG Group D substance
""These values  differ  from those In  the HEED  (U.S.  EPA.  19B7a)  because the uncertainty factors  for deriving the Inhalation RfD values  presented  herein were
 changed to correspond to those used by IRIS (U.S. EPA. 19876) for generating the oral RfD from  the same (Inhalation)  study.
"Calculated by analogy to free cyanide by correcting for differences In molecular weight
°These values  differ  from those In  the HEA  (U.S.  EPA. 1984) because  the  study  chosen as the basis for the Inhalation RfD values was  changed  to conform to
 the Inhalation study chosen as the basis of the oral RfD derived In a more recent HEEP (U.S. EPA,  1986).
PFInal Draft of Air Quality Criteria Document (600/8-83-028F) declines to derive an air quality  criterion  for  lead.
iNot verified and further discussion not scheduled
rBased on RfD for methyl mercury
'These values  differ  from those 1n  the HEA  (U.S.  EPA. 1984) because  the  study  chosen as the basis for the Inhalation RfD values was  changed  to conform to
 the Inhalation study chosen as the basis of the oral RfD derived on IRIS.
1A minor calculation error In estimation of transformed dose In 1986 HEEP Is corrected here.
"Verified as a Group C carcinogen; no quantitative estimate available.
Reported effects occurred  at  portal of entry; estimates  of rag/day reference doses are  Inappropriate  because  effects at portal of entry  depend on concen-
 tration In air.  An acceptable air concentration of 0.07 mg/m3 was estimated by Carson et al. (1981) from available data.
Experiment performed with o-xylene
"From toxlclty data on tetraethyl lead
VW1Indrawn from IRIS
zThe oral RfD, while still available on IRIS. Is being reconsidered by the RfD Workgroup.
aaThe verified RfD appears on IRIS as 1.3E-3 because of a typographical error.
^Developmental effects have been used as the basis of calculation.
ccBased on arsenic equivalents
ddTh1s value for nitrogen dloxIde-N Is based on analogy to nitrate.
eeCalculated by analogy to mercury by correcting for differences In molecular weight.
ffA new RfD verified and the old number on IRIS will be changed.
NA = Not applicable or not available; ND = not determined
Notes:  To estimate acceptable water concentrations from oral RfOs/RfD, multiply by 70 and divide by 2 ft.
  If exposure occurs by both oral and Inhalation routes, the route-specific RfD$/RfD must  be proportionally reduced.

0627h                                                                        A-93                                                                 07/12/90

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Update: «, 1990
EPA Group/Unit Risk
Exposure Species Tumor Site [Slope Factor!
Compound


Acephate




Acroleln


Acrylamlde




Acrylonltrlle






Alachlor

Aldrln










Inhalation: Oral Inhalation Oral Inhalation Oral Inhalation
( iiO/m*' ) ~ '
[(mg/kg/day)-l]
NA; 2-year dietary NA mouse NA liver ND
(also see Table A)




NA; NA NA NA NA NA C/NDa
(also see Table A)

NA; 2-year drinking NA rat NA CNS, mammary B2/1.3E-3
water (also see and thyroid [4.5E*0)a'D
Table A) glands,
uterus, oral
cavity
occupational; three human rat lung multiple B1/6.8E-5
drinking water [2.4E-1]3
studies





NA; NA NA NA NA NA B2/NDf
(also see Table A)

three dietary mouse mouse liver liver B2/4.9E-3
studies; three (also see Table A) [1.7E*l]a«b
dietary studies








Oral
(vg/ft)-1
[(mg/kg/dayj-l]
C/2.5E-7
[8.7E-3]8




C/NDa


B2/1.3E-4
[4.5E+OJa



B1/1.5E-5
[5.4E-1]3






B2/2.3E-6
[8.1E-2]f

B2/4.9E-4
[1.7E*l]a









Reference
Inhalation/Oral


U.S. EPA, 1990/
Chevron Chemical
Company, 1982;
U.S. EPA, 1984;
U.S. EPA, 1990;
U.S. EPA, 1988, 1990
U.S. EPA. 1987,
1990/U.S. EPA, 1987.
1990
U.S. EPA. 1990/
Johnson et al..
1986; U.S. EPA.
1985, 1990

O'Berg. 1980;
U.S. EPA. 1983,
1987a,b/Quast
et al.. 1980;
Bio/dynamics,
Inc.. 1980a.b;
U.S. EPA, 1983,
1987. 1990
U.S. EPA. 1984.
1988/U.S. EPA.
1984. 1988
NCI. 1977; Davis
and FUzhugh. 1962;
Epstein. 1975;
Davis, 1965; U.S.
EPA, 1986, 1987b/
NCI. 1977; Davis
and FUzhugh, 1962;
Epstein, 1975;
Davis, 1965; U.S.
EPA, 1986. 1987.
1990
0625h
B-l
07/12/90

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                                                                     Update:    ne, 1990
Compound
Allyl chloride

Aniline

Aramlte


Arsenic





Asbestos
Azobenzene

Benzene







Exposure
Inhalation; Oral
NA; NA

NA; 2-year dietary

NA; 400 ppm In diet
for 104 weeks (20
mg/kg/day)


100-5000 ug/n)3
continuous;
0.01-1.8 mg/i In
drinking water




occupational;
dietary
NA; 2-year dietary

occupational;
occupational







Species Tumor Site
Inhalation Oral Inhalation Oral
NA NA NA NA
(also see Table A)

NA rat NA spleen

NA rat Increased Increased
Incidence Incidence
of liver of liver
tumors tumors
(also see Table A)
human human respiratory skin
tract
(also see Table A)




human rat lung and large
mesothelloma Intestine
NA rat NA abdominal
cavity

human human leukemia leukemia







EPA Group/Unit Risk
rSlooe Factor]
Inhalation
(pg/mj)-' ,
[(mg/kg/day)-!]
C/Nflf

B2/ND

B2/7.1E-6
[2.5E-2]0


A/4.3E-3
[5.0E+l]a'P





A/2.3E-1
(fibers/ml)-1 m
B2/3.1E-5
[l.lE-l]a«b

A/8.3E-6
[2.9E-2]a







Oral
(tiQ/t)-' .
[(mg/kg/day)-']
C/NDf

B2/1.6E-7
[5.7E-3]3

B2/7.1E-6
[2.5E-2]


A/NAk





A/NO
B2/3.1E-6
[l.lE-l]a

A/8.3E-7
[2.9E-2]a'b







Reference
Inhalation/Oral
U.S. EPA, 1983,
1989/U.S. EPA,
1983. 1989
U.S. EPA, 1987/
CUT. 1982;
U.S. EPA, 1985, 1989
1990/ U.S. EPA. 1989;
Popper et al., 1960;
Oser and Oser, 1962


Brown and Chu.
1983a,b,c; Lee-
Feldsteln, 1983;
Hlgglns, 1982;
Enterllne and
Harsh. 1982;
U.S. EPA. 1984a.b.
1990/U.S. EPA.
1990
U.S. EPA. 1986.
1987/NTP. 1985;
U.S. EPA. 1985. 1990
U.S. EPA. 1990/
NCI, 1979; U.S. EPA.
1986. 1990
Ott et al.. 1978;
Rlnsky et al., 1981;
Wong et al.. 1983;
U.S. EPA. 1985.
1987a. 1989/Ott et
al.. 1978; Rlnsky
et al.. 1981; Wong
et al., 1983; U.S.
EPA. 1985. 1987a,
1989, 1990
0625h
                                                                              B-2
                                                                                                                                                    07/12/90

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                                                 HIAL1H EFUC1S ASSESSMENTS SUMMARY TABLE B: CARCINOGENIC IIY
                                                                     Update    'une. "(990
Fxooture Soecles Tumor Site
Compound
Benzldlne


Benzo(a)anthracene
Benzo(a)pyrene

Benzol b)f luoranthene
Benzo(k)f luoranthene
Benzotrlchlorlde
Benzyl chloride
Beryllium



Inhalation; Oral Inhalation
occupational; human
occupational


NA; NA NA
2.2-9.5 mg/m3, 4.5 hamster
hours/day for <96.4
weeks; 1-250 ppm
diet for =110 days

NA;NA NA
NA; NA NA
NA; 0.26 mg/kg/day, mouse
2 days/week by gavage
for 25 weeks
NA; 0. 15. 30 mg/kg. NA
3 days/week by gavage
for 104 weeks
occupational; 5 ppm human
In drinking water
for lifetime



Oral Inhalation Oral
human urinary urinary
bladder bladder
(also see Table A)


NA NA NA
mouse respiratory stomach
tract

NA NA NA
NA NA NA
mouse lung lungs
rat NA thyroid
rat lung total
tumors
(also see Table A)



EPA Group/Unit Risk
TSlooe Factorl
Inhalation
[(mg/kg/day)-1]
A/6.7E-2
[2.3E*2]a


B2/NAM
B2/ND*>u

B2/NDf»u
B2/NOf."
B2/NA9
B2/ND
B2/2.4E-3
[8.4E+0]3



Oral
| [(mg/kg/day)-1
A/6.7E-3
[2.3E»2]a-b


B2/NDf'u
B2/NDa.u

B2/NDf.»
B2/NDf.»
B2/3.6E-4
[1.3E*l]f
82/4. 9E -6
[1.7E-l]a
82/1. 2E-4
[4.3E»OJa
,


Reference
Inhalation/Oral
]
Zavon et al.. 1973;
U.S. EPA. 1990Y
Zavon et al.. 1973;
U.S. EPA. 1980.
1986. 1987. 1990
U.S. EPA, 1990
Thyssen et al.,
1990; U.S. EPA,
1987/Neal and
Rlgdon, 1967;
U.S. EPA, 1980,
1990
U.S. EPA, 1990
U.S. EPA, 1987
U.S. EPA, 1989/
Fukuda et al.. 1978;
U.S. EPA. 1986, 1989
U.S. EPA. 19907
Lljlnskl, 1986;
U.S. EPA, 1986, 1990
Wagoner et al.,
1980; U.S. EPA.
1987. 1990/
Schroeder and
Nltchener. 1975;
U.S. EPA, 1986,
1993
0625h
                                                                              8-3
                                                                                                                                                     07/12/90

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                                                 HtAUH  EFflClS ASSESSMENTS SUMMARY TABLF B: CARC1NOGEN1CIIV
                                                                    Update:     e. 1990
Compound
B1s(2-chloroethyl)
ether



Bls(chloromethyl)-
ether
Exposure Species
Inhalation; Oral Inhalation Oral
560-day oral study; mouse mouse
560-day oral study



Inhalation 10-100 rat rat
days; Inhalation
10-100 days
B1s(2-chloro-l-methyl-
ethyl)ether 2-year gavage mouse mouse
studyb; 2-year
gavage study
B1s(2-ethylhexyl)
phthalate

Bromodlchloromethane

Bromoethene
(vinyl bromide)
Bromoform



NA; 103-week NA mouse
dietary study

NA; 102-week gavage NA mouse
study

2-year Inhalation rat NA
study; NA
NA; 103-week gavage NA rat
study



Tumor Site
Inhalation Oral
[
liver liver



respiratory ND
tract
liver, lung liver, lung
NA liver
(also see Table A)

NA liver
(also see Table A)

liver NA
NA adenoma tous
polyps or
adenocarclno-
mas In the
large Intestine
(also see Table
EPA Group/Unit Risk
FSloDC Factor!
Inhalation
(wg/ni-»)-'
(mg/kg/day)-']
B2/3.3E-4
[l.lE*0]a'D



A/6.2E-2
[2.2E»2]a
C/2E-5
[7E-2]°
B2/ND3

B2/NDf

B2/3.2E-5
[1.1E-1]
B2/1.1E-6
[3.9E-3]f


A)
Oral
(..g/i)-1 ,
[(mg/kg/day)-1]
B2/3.3E-5
[l.lE*OJa



A/6.2E-3
[2.2E+2Ja-b
C/2E-6
[7E-2]
B2/4E-7
[l.«E-2]a

B2/3.7E-6
[1.3E-l]f

B2/ND
B2/2.2E-7
[7.9E-3]f



Reference
Inhalation/Oral
Innes et al..
1969; U.S. EPA,
1980, 1990;/Innes
et al.. 1969;
U.S. EPA, 19BO
1987, 1990
Kuschner et al.,
1975; U.S. EPA,
1990/U.S. EPA.
1990
NTP. 1982;
U.S. EPA, 1987/
NTP 1982;
U.S. EPA, 1987
U.S. EPA. 1987/
NTP, 1982.
U.S. EPA. 1986.
1988, 1990
U.S. EPA, 1987.
1989, 1990/NTP,
1986; U.S. EPA,
1987, 1990
Benya et al., 1982;
U.S. EPA, 1984/
U.S. EPA. 1984
U.S. EPA, 1989,
1990/ NTP, 198B/
U.S. EPA. 1989.
1990


0625h
                                                                             B-4
                                                                                                                                                   07/12/90

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                                             WAITH  Em.cis ASSESSMENTS SUK   .  IABI.E  B: CARCINOGKNICMY
                                                                Update:  June.  1990
Compound
1.3-Butadlene

Butyl benzyl
phthalate
Cadmium


Captafol
Captan

Carbazole
Carbon tetrachlorlde







Chloranll
Exposure
Inhalation; Oral
two Inhalation
studies; NA

NA; NA
occupational; NA


NA; dietary study
(CBI)
NA; NA

NA; 96 -week dietary
study
several gavage
studies; several
gavage studies







NA; 82-week oral
study
Soecles Tumor Site
Inhalation Oral Inhalation
Oral
mouse, rat NA hematopoletlc NA
system.
Leydlg cell.
thyroid
NA NA NA
(also see
human NA respiratory
tract
(also see

NA mouse NA
(also see
NA NA NA
(also see

NA mouse NA
several several liver
(also see







NA mouse NA

NA
Table A)
NA
Table A)

lymphosarcoma
Table A)
NA
Table A)

liver
liver
Table A)







liver and
lung
EPA Group/Unit Risk
[Slope Factor]
Inhalation
d.g/mj) ' ,
[(mg/kg/day)-']
B2/2.8E-4
ll.8E*0]a-'

NA
B1/1.8E-3
[6.1E*0]a


C/NO
B2/ND1

B2/ND
B2/1.5E-5d
[1.3E-l]a-b







C/ND
Oral
(••g/i)-1 .
[(mg/kg/day)'1]
NO

C/NOa
NO/NDC


C/2.4E-7
18.6E 3]
B2/1.0E 7
[3.5E-3]'

B2/2.8E--7
[2E-2]
B2/3.7E-6
[1.3E l]a







C/1.1E-5
[4.03E-1]
Reference
Inhalation/Oral
Hazel ton Labs. 1981;
U.S. EPA. 1985.
1987. 1989; U.S
EPA. 1989. 1990
U.S. EPA. 1987.
1990/U.S. EPA.
1987. 1990
Thun et al.. 1985;
U.S. EPA. 1985.
1990/U.S. EPA. 1984.
1988
U.S. EPA, 1984/
U.S. EPA. 1984
U.S. EPA. 1984,
1988/U.S. EPA,
1984. 1988
U.S. EPA, 1986/
Tsuda et al., 1982;
U.S. EPA. 1986
Delia Porta et al.,
1961; Edwards
et al., 1942; NCI,
1976; U.S. EPA,
1984a,b, 1990/
Delia Porta et
al., 1961; Edwards
et al.. 1942;
NCI. 1976;
U.S. EPA. 1984.
1990
U.S. EPA, 1986/
BRL, 1968; U.S. EPA,
1986
0625h
                                                                          B-5
                                                                                                                                           06/19/90

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                                                HEALTH EFFECTS ASSESSMENTS SUMMARY 1ABLE B.  CARCINOGENICI1Y
                                                                    Update:  June. T990
Compound
Chlordane
Chlorodlbromoethane
Chloroethene
(see vinyl chloride)
Chloroform
Chloromethane
4- Chloro-2 methyl-
aniline
4 Chloro-2-2-methyl-
anlllne hydrochlorlde
Chlorumrthyl methyl
ether
Exoosure Species
Inhalation; Oral Inhalation Oral
two dietary bloassays; mouse mouse
two dietary bloassays
NA; 105-week gavage NA mouse
study

138-477 mg/kg/day; mouse rat
200-188 ppm in
drinking water for
104 weeks
24 month Inhalation mouse mouse
study; 24-month
inhalation study
NA; 0-4000 ppm In NA mouse
the diet for 18
months
NA; 9-4000 ppm In NA mouse
the diet for 18
months
NA; NA human NA
lumor Site
Inhalation Oral
liver liver
(also see Table A)
NA liver
(also see Table A)

liver kidney
(also see Table A)
kidney kidney
NA vascular
hemanglomas
and hemangio-
sarcomas
NA vascular
hemanglomas
and hemanglo-
sarcomas
lung NA
EPA Group/Unit Risk
ISlooe Factor]
Inhalation
[(mg/kg/day)-1)
B2/3.7E-4
[1.3E*0]a'b
B2/ND

B2/2.3E-5
[8.1E-2)a
C/1.8E-6
[6.3E-3]
B2/ND
B2/NO
A/NOa
Oral
[(rog/kg/day)-1)
B2/3.7E-5
ll.3E+0]a
B2/2.4E-6
18.4E-2)

B2/1.7E-7
[6.1E-3)a
C/3.7E-7
[1.3E-2)b
B2/1.6E-4
[5.8E-1]0
B2/1.3E-5
14.6E-I]
A/NOa
Reference
Inhalation/Oral
IRDC. 1973; NCI,
1977; U.S. EPA.
1986. 1990/1 ROC,
1973; NCI. 1977;
U.S. EPA. 1986
1988. 1990
U.S. EPA. 1987/
NTP. 1985;
U.S. EPA, 1987

NCI. 1976; U.S. EPA.
1985, 1988. 1990/
Jorgenson et al.,
1985; U.S. EPA.
1988, 1990
CUT. 1983; NIOSH,
1984; U.S. EPA.
1987/CIIT, 1983;
NIOSH. 1984; U.S.
EPA. 1986, 1987
U.S. EPA. 1986/
U.S. EPA, 1986;
Weisburger et al..
1978
U.S. EPA, 1986/
U.S. EPA, 1986;
Weisburger et al..
1978
U.S. EPA. 1987,
1990/U.S. EPA.
1990
062bh
                                                                              8-6
                                                                                                                                                   06/19/90

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                                                HIALTH imCTS ASSISSHINIS SUMHAKY FABLE B: CARCINOGIN1CIIY
                                                                    Update:  June. 1990
Compound
o Chloronltrobenzene
p Chloronltrobenzene
Chlorthalontl
Exposure Species
Inhalation; Oral Inhalation Oral
NA; 18-month NA mouse
dietary study
NA; 0-6000 ppm In NA mouse
the diet for 18
months
NA; 80-week dietary NA rat
study
lumor Site
Inhalation Oral
NA liver
NA vascular
tumors
NA kidney
(also see Table A)
EPA Group/Unit Risk
1 Slooe Factorl
Inhalation Oral
[(mg/kg/day)-1] [(mg/kg/day)- ']
B2/ND B2/3.5E-7
[2.5E-2]
B2/NO 82/5. 1E-7
[I.8E-2]
B2/ND B2/8.2E-8
[2.9E-3]f
Reference
Inhalation/Oral
U.S. EPA. 1985/
U.S. EPA, 1985;
Weisburger et al.,
1978
U.S. EPA, 1985/
U.S. EPA. 1985;
Weisburger et al..
1978
U.S. EPA, 1984/
NCI, 1978; U.S. EPA,
Chromium (VI)
occupational; NA
human        NA         lung           NA
                          (also see Table A)
                                                                                                    A/1.2E-2
                                                                                                NO/NDC
1984

Mancuso. 1975; U.S.
tPA. 19B4a.b.
1990/NA
Chrysene
Coal tars
Creosote
Cresol. o-. m-
dnd p-
C rot ond Idehyde
NA; NA NA
occupational. NA human
NA; NA NA
NA; NA NA
113-week drinking rat
water study;
113-week drinking
water study
NA NA NA
(also see (able A)
NA lung NA
NA NA NA
NA NA NA
(also see Table A)
rat liver liver
B2/N01 B2/NA'
ND/6.2E-4 ND/ND
[2.2E+OJe
Bl/N0a Bl/NDa
C/ND' C/ND'
C/5.4E-4 C/5.4E-5
[1.9E+0]b [1.9E»0]
U.S. EPA, 199Q
Redmond et al.,
1979; Hazumdar
et al.. 1975; U.S.
EPA. 1984/NA
U.S. EPA. 1990/
U.S. EPA. 1990
U.S. EPA. 1984.
1985. 1990/U.S.
EPA. 1984. 1985,
1990
U.S. EPA. 1989/
Chung et al. .
1986; U.S. EPA,
1989
OG2bh
                                                                              B /
                                                                                                                                                    06/19/90

-------
                                                 lit AIIH ItttCTS ASSESSMENTS SUMMARY TABLE B: CARClNOGtNICI IV
                                                                     Update:  *-ne, 1990
Compound
ODD
DDE
DDT
Decabromodlphenyl
oxide (Decabromo-
dlphenyl ether)
Dlallate
Dlbenzo(a.h)
anthracene
Dlbromochloromethane
l,2-Dlbromo-3-
chloropropane
1,2-Dlbromoethane
(ethylene dlbromlde)
1,4-Dlchlorobenzene
(p-dlchlorobenzene)
Exposure
Inhalation; Oral
NA; 250 ppm In diet
for 130 weeks
NA; doses of 0-1,000
ppm In diet In 3
studies
NA; several dietary
studies
NA; NA
NA; 19-month oral
study
NA; NA
NA; 105-week gavage
study
Inhalation study;
Studies Include
gavage and skin
application
88-103 week Inhala-
tion study; 49-week
gavage study
NA; 103-week gavage
study
Species Tumor Site
Inhalation Oral Inhalation
NA mouse NA
NA mouse, NA
hamster
mouse. mouse, liver
rat rat (also see
NA NA NA
(also see
NA mouse NA
(also see
NA NA NA
NA mouse NA
(also see
Oral
liver
liver
liver
Table A)
NA
Table A)
liver
Table A)
NA
hepatocellular
adenomas or
carcinomas
Table A)
rat, mouse rat, mouse lung, nasal forestomach,
cavity, mammary gland,
tongue, lung, skin
pharynx,
adrenal cortex
rat rat nasal cavity forestomach
NA mouse NA
(also see
	 R
liver
Table A)
a
EPA Group/Unit Risk
fSlooe Factor!
Inhalation
(pg/mj)-'
[(mg/kg/day)-')
B2/ND
B2/ND
B2/9.7E-5
[3.4E-lJa'b
C/NDa
B2/ND
B2/NDf."
C/NDf
B2/6.3E-3
[2.2E*1J
B2/2.2E-4
[7.6E-l]a
B2/ND
urai
[(mg/kg/day)-1]
B2/6.9E-6
[2.4E-1]3
82/9. 7E -6
[3.4E-l]a
B2/9.7E-6
[3.4E-l]a
C/NDa
B2/1.7E-6
[6.1E-2]
B2/NDf«u
C/2.4E-6
[8.4E-2]f
B2/6.3E-4
[2.2E*1]
B2/2.5E-3
[B.5E*l]a
B2/6.BE-7
[2.4E-2J9
Reference
inna iat ion/ura i
NA/Tomatls et al..
1974; U.S. EPA. 1990
NA/NCI, 1978; Tomat!s
et al.. 1974; Rossi et
al.. 1983; U.S. EPA.
1990
U.S. EPA. 1986,
1990/U.S. EPA.
1984. 1986. 1990
U.S. EPA. 1984.
1987. 1990/U.S.
EPA, 1984. 1987
1990
U.S. EPA. 1983/
BRL, 1968; Innes
et al.. 1969;
U.S. EPA. 1983
U.S. EPA. 1990
U.S. EPA. 1989/
NTP. 1985; U.S.
EPA, 1987, 19B9a,b
SRC. 1982; U.S. EPA.
1985. 1986/SRC 1982;
U.S. EPA, 1985. 1986
NTP. 1982; U.S. EPA.
1984, 1990/NCI,
1978; U.S. EPA,
1984, 1987, 1990
U.S. EPA, 1987/
NTP. 1986;
U.S. EPA. 1987
08/01/90
0625h

-------
                                                  HIAL1H  EFFECTS  ASSFSSNINTS  «" ""ARY  TABLE  B:  CARCINOGENICIIY
                                                                      Update       e,  1990
Compound
3,3'-D1chloro-
benzldlne


l,4-Dlchloro-2-
butene


1.1-Okhloroethane


1.2-Olchloroethane
(ethylene chloride)


1.1-Okhloroethylene
(vlnylldene chloride)




1 ,2-Dlchloropropane

1.3-Dlchloropropene


Exposure Species
Inhalation; Oral Inhalation Oral
NA; lifetime NA rat
dietary study


90-day Inhalation rat NA
study; NA


NA; gavage NA rat


gavage; gavage rat rat


10 and 25 ppm for mouse rat
12 months; gavage




NA; gavage NA mouse

2-year Inhalation mouse rat
bloassay; 104-week
gavage study

Tumor Site
Inhalation Oral
NA mammary



nasal NA
passages
(also see Table A)

NA hemanglo-
sarcoma
(also see Table A)
circulatory circulatory
system system


kidney adrenal
(also see Table A)




NA liver
(also see Table A)

EPA Group/Unit Risk
TSlope Factor]
Inhalation
d.g/n)J)-' .
[(mg/kg/day)-l]
B2/ND?



B2/2.6E-3
[9.3E+0]


C/NOf


B2/2.6E-5
[9.1E-2]a.°


C/5E-5
[1.2E»0]a.'




B2/ND

benign lung forestomach, B2/3.7E-5
tumors liver, adrenal, [1.3E-1]1
(also see thyroid
Table A)


Oral
(pg/i)-1 ,
[(mg/kg/day)-']
B2/1.3E-5
[4.5E-l]f


B2/ND



C/NDf


B2/2.6E-6
[9.1E-2]a


C/1.7E-5
[6E-1J*




B2/1.9E-6
[6.8E-2]9

B2/5.1E-6
[1.8E-1]1


Reference
Inhalation/Oral
U.S. EPA, 1988/
Stula et al.,
1975; U.S. EPA,
1988
El Oupont de
Nemours, 1986;
U.S. EPA, 1987/
U.S. EPA, 1987
U.S. EPA. 1984.
1990/NCI. 1978;
U.S. EPA, 1985, 1989
NCI. 1978; U.S. EPA,
1985. 1990/NCI.
1978; U.S. EPA,
1985, 1990
Naltonl et al..
1985; U.S. EPA,
1985, 1990/
NTP, 1982;
U.S. EPA. 1985,
1988, 1990
U.S. EPA, 1987/
NTP. 1986;
U.S. EPA. 1987
Lomax et al.. 1989;
U.S. EPA. 1989/
NTP. 1985;
U.S. EPA. 1985, 1989
06?5h
                                                                              B-9
07/24/90

-------
                                                 HEALTH EFFECTS ASSESSHEN      WARY TABLE B: CARCINOGENICITY
                                                                     Update.  June, 1990
EPA Group/Unit Risk
Exposure Species Tumor Site [Slope Factor]
Compound I
Dleldrln














Dlethylstllbesterol


3.3'-D1methoxybenz1(Mne



2,4-Dlmethylanlllne


2,4-DUnethylanlllne
hydrochlorlde

7,12-Dlmethylbenz(a)
anthracene
3,3'-01inethylbenz1d1ne


1,1-Dlmethylhydrazlne


nhalatton: Oral Inhalation Oral Inhalation Oral Inhalation
«pg/mj)-'
[{mg/kg/day)-l]
several dietary mouse mouse liver liver B2/4.6E-3
studies; several (also see Table A) [1.6E+l]a-b
dietary studies












Oral studies0; rat. mouse, rat, mammary gland, mammary gland, A/1.4E-1
Oral studies mouse uterus, cervix uterus, cervix [4.9E»2]D

NA; lifetime dietary NA hamster NA forestomach B2/ND
study


NA; 18-month dietary NA mouse NA lung C/ND
study with the HC1
salt •
NA; 18-month dietary NA mouse NA lung C/ND
study

Data Inadequate for Risk Assessment"

NA; 30-day gavage NA rat NA mammary B2/ND
study

NA; lifetime NA mouse NA vascular C/ND
drinking water study system

Oral
(wg/i)-' ,
t(mg/kg/day)-l]
B2/4.6E-4
[1.6E»l]a













A/1.4E-2
[4.9E+2]

B2/4E-7
[1-4E-2]


C/2.1E-5
[7.5E-1]

C/1.7E-5
[5.BE-1]



B2/2.6E-4
[9.2E+0]

C/2.5E-4
[8.7E»0]9

Reference
Inhalation/Oral
Thorpe and Walker,
1973; Davis, 1965;
Walker et al., 1972;
Tennekes et al.,
1981; Helerhenrey
et al.. 1983; NCI.
1978; U.S. EPA.
1990/Thorpe and
Walker, 1973; Davis,
1965; Walker et al..
1972; Tennekes
et al., 1981;
Helerhenrey et al..
1983; NCI. 1978;
U.S. EPA. 1987. 1990
SRC. 1983; U.S. EPA.
19B6D/SRC. 1983;
U.S. EPA, 1986
U.S. EPA, 19B7/
Sellakumar et al..
1969; OSHA/NIOSH,
1980; U.S. EPA, 1987
U.S. EPA, 1987/
Welsberger et al..
1978; U.S. EPA. 1987
U.S. EPA. 1987/
Welsberger et al..
1978; U.S. EPA. 1987


U.S. EPA. 1987/
Grlswold et al.,
1968; U.S. EPA. 1987
U.S. EPA, 1984/Toth,
1972, 1973;
U.S. EPA. 1984
062bh
B-IO
07/24/90

-------
                                                  HFAL1II  EIFLC1S  ASSISSMEN1S <="UMARY TABLE B:  CARCINOGENICI1Y
                                                                       Update     ie. 1990
Compound
1.2-D1methylhydraz1ne


Dimethyl sulfate


2,4-Dlnltrotoluene



2.6-D1n1trotoluene



1,4-Dloxane

1.2-Dlphenyl-
hydrazlne



Direct Black 38


Direct Blue 6


Direct Brown 95


Direct Sky Blue 6B

Exposure Species
Inhalation; Oral Inhalation Oral
NA; 73-week drinking NA mouse
water study

NA; NA NA NA


NA; 2-year dietary NA rat
study


NA; NA NA NA



NA; 0-530 mg/kg/day NA rat
for 110 weeks
2-year dietary rat rat
study0; 2-year
dietary study


NA; 190-1500 ppm In NA rat
diet for 93 days

NA; 190-1500 ppm In NA rat
diet for 91 days

NA; 190-1500 ppm In NA rat
diet for 91 days

NA; NA NA NA

Tumor Site
Inhalation Oral
NA vascular
system

NA NA


NA liver,
mammary
gland

NA NA



NA nasal cavity.
liver
liver 'liver




NA liver


NA liver


NA liver


NA NA

EPA Group/Unit Risk
fSlooe Factor!
Inhalation
[(mg/kg/day)-!]
Bl/ND


B2/NDa


B2/NDf



B2/NDf



B2/ND

B2/2.2E-4
[8.0E-l]a'°



A/ND


A/ND


A/ND


B2/ND

Oral
[{mg/kg/day H)
B1/4.0E-2
[1.4E»3]9

B2/NDa


B2/1.9E-5
[6.8E-l]f-n


B2/1.9E-5
[6.8E-l]f'n

X
B2/3.1E-7
[l.lE-2]a
B2/2.2E-5
[8.0E-1J9



A/2.4E-4
[8.7E*0]9

A/2.3E-4
[8.7E»0]9

A/2.6E-4
[9.3E+OJ9

B2/ND

Reference
Inhalation/Oral
U.S. EPA. 1984/Toth
and Wilson, 1971;
U.S. EPA, 1984
U.S. EPA, 1985,
1990/U.S. EPA, 1985,
1990
U.S. EPA, 1987.
1990/Ellls et al.,
1979; U.S. EPA,
1987, 1990
U.S. EPA, 1987.
1990/U..S. EPA,
1987, 1990

NA/NCI, 1978; U.S.
EPA, 1990
NCI, 1978;
U.S. EPA. 1980.
1990/NCI, 1978;
U.S. EPA. 1980.
1987, 1988, 1990
U.S. EPA. 1987/
NCI. 1978; U.S. EPA.
1987
U.S. EPA. 1987/
NCI. 1978; U.S. EPA.
1987
U.S. EPA, 1987/
NCI. 1978; U.S. EPA.
1987
U.S. EPA. 1987/
U.S. EPA. 1987
0625h
B-ll
                                                                                                                                                      07/24/90

-------
                                                  HFAL1H  IfFlClS  ASSESSMENTS SUMMARY 1ABLE B: CARCINOGtNICIlY
                                                                      Update:    )-'
[(mg/kg/day)-']
respiratory forestomach B2/1.2E-6
tract [4.2E-3]a
(also see Table A)
NA forestomach 82/ND

blood cells, NA B1/1E-4
brain [3.5E-119
NA thyroid B2/ND
NA digestive B2/ND
tract
nasal cavity nasal cavity B1/1.3E-5
[4.5E-2]3
NA mammary B2/ND
NA leukemia B2/ND
NA NA B2/ND
Oral
(wg/O-1 .
[(mg/kg/day)-l)
B2/2.8E-7
[9.9E-3J3
B2/1.4E-6
[4.BE-2J9

NO
B2/1E-6
[3.6E-2J9
B2/1E-7
[3.5E-3J3
B1/8.6E-7
[3.0E-2]
B2/1E-4
[3.8E+0]
B2/7.1E-4
[5.0E»1]
B2/NO
Reference
Inhalation/Oral
Laskln et al.. 1980;
U.S. EPA, 1984,
1985. 1990/Komlshl
et al., 1980;
U.S. EPA, 1984,
1985, 1990
U.S. EPA, 19B7/
NTP. 1986; U.S. EPA,
1987

Snel lings et al..
1981; U.S. EPA,
1985/U.S. EPA,
1985
U.S. EPA. 1984/
U.S. EPA, 1984
U.S. EPA, 1990/
Chevron Chemical
Company. 1982;
U.S. EPA. 1984. 1990
U.S. EPA. 1985.
1990/U.S. EPA, 1985,
1988a,b
U.S. EPA, 1987/
U.S. OHEW. 1976a,b;
U.S. EPA, 1987
U.S. EPA. 1987/
Cohen et al., 1970;
U.S. EPA. 1987
U.S. EPA. 1989/
U.S. EPA. 1989
0625h
                                                                              B-12
07/24/90

-------
                                                  HLAL1H EFFECTS ASSESSMENTS r   "ARY  TABLE  B:  CARCINOGENICIIY
                                                                      Update      e,  1990
Exposure Species Tumor Site
Compound Inhalation; Oral Inhalation Oral Inhalation Oral
Heptachlor dietary studies; mouse mouse liver liver
dietary studies (also see Table A)







Heptachlor epoxlde 0-10 ppm In diet for 2 mouse mouse liver liver
years"; 0-10 ppm In
diet for 2 years





Hexachlorobenzene diet; diet hamster hamster liver liver
(also see Table A)



Hexachlorobutadlene diet; diet rat rat kidney kidney
(also see Table A)




Hexachlorocyclohexane- NA; 24-week dietary NA mouse NA liver
alpha study

Hexachlorocyclohexane NA; 110-week dietary NA mouse NA liver
beta study


EPA Group/Unit Risk
[Slope Factor]
Inhalation
[(mg/kg/day)-l]
B2/1.3E-3
[4.5E*0]a'b







B2/2.6E-3
[9.1E+OJa'b






B2/4E-4
[1.6E*0]b-f



C/2.2E-5
[7.8E-2]a'b




B2/1.8E-3
[6.3E+OJa.b

C/5.3E-4
[1.8E*0]a.b


Oral
[(mg/kg/day)-M
B2/1.3E-4
[4.5E»OJa







B2/2.6E-4
[9.1E*0]a






B2/4E-5
[1.6EtO]f



C/2.2E-6
[7.8E-2]a




B2/1.BE-4
[6.3EfO]a

C/5.3E-5
[1.8E»0]a


Reference
Inhalation/Oral
Davis, 1965;
Epstein, 1976; NCI,
1977; Reuber, 1977;
U.S. EPA, 1986,
1990/Davls, 1965;
Epstein. 1976; NCI,
1977; Reuber, 1977;
U.S. EPA. 1986
1987. 1990
Davis, 1965;
Velstcol Chemical
Corp., 1973; U.S.
EPA. 1990/Oavls.
1965; Velslcol
Chemical Corp..
1973; U.S. EPA,
1990
Cabral et al., 1977;
U.S. EPA. 1984.
1989/Cabral et al..
1977; U.S. EPA.
1984. 1985
Koclba et al..
1977; U.S. EPA,
1990/Koclba et al..
et al.. 1977;
U.S. EPA. 1980,
1984, 1990
U.S. EPA, 1990/1 to
et al.. 1973;
U.S. EPA, 1987, 1990
U.S. EPA. 1990/
Thorpe and Walker,
1973; U.S. EPA,
1987. 1990
0625h
B-13
                                                                                                                                                    07/24/90

-------
                                                 HEAL III  EFFEC1S ASSESSMENTS SUMMARY 1ABLE B:  CARCINOGENIC! IY
                                                                    Update:    ic. 1990
Compound
Hexachlorocyclohexane -
delta
Hexachlorocyclohexane-
gamma (Undane)
Hexachlorocyclohexane-
epsllon
Hexachlorocyclohexane-
technkal
Hexachloroethane
Hydraz Ine/hydraz 1 ne
sulfate
Indeno(l,2,3-c,d)
pyrene
Isophorone
Lead
2-Hethoxy-5-nltro-
anlllne
Exposure Species
Inhalation; Oral Inhalation Oral
NA; 24-week dietary NA mouse.
study rat
NA; diet NA mouse
NA; mixture of NA mouse
delta and epsllon In
the diet for 26 weeks
NA; 6- to 20-month NA mouse
dietary study
90-week gavage study; mouse mouse
90-week gavage study
hydrazlne vapor rat mouse
Inhalation for
1 year; 25-week
exposure by gavage
to hydrazlne sulfate
NA; NA NA NA
NA; 2-year gavage NA rat
study
NA; NA NA NA
NA; 0.4X, 0.85C In NA rat
diet for 104 weeks
Tumor Site
Inhalation Oral
NA liver
NA liver
(also see Table A)
NA liver
NA liver
liver liver
(also see Table A)
nasal cavity liver
NA NA
NA kidney,
preputlal
gland
(also see Table A)
NA NA
(also see Table A)
NA skin
EPA Group/Unit Risk
[Slope Factor!
Inhalation
(gg/mJ)-'
[(nig/kg/day)-!]
D/ND
B2-C/ND
D/ND
B2/5.1E-4
[1.8E*0]a'b
C/4.0E-6
[1.4E-2]a.°
B2/4.9E-3
[17.1EtO]a
B2/NDf.u
C/NDf
B2/NDa
B2/ND
Oral
(ng/»)-' .
[(ing/kg/day Hi
D/NDa
B2-C/3.7E-5
[1.3E*0]9
D/NDa
B2/S.1E-S
[1.8E*0]a
C/4.0E-7
[1.4E-2]3
B2/B.5E-5
[3.0E*OJa
B2/NDf>u
C/1.1E-7
[3.9E-3J9
B2/NOa
B2/1.3E-6
[4.6E-2]
Reference
Inhalation/Oral
U.S. EPA. 1990/
Ito et al.. 1973.
1975; Nagasaki
et al.. 1972;
U.S. EPA. 1987, 1990
U.S. EPA, 19B4/
Thorpe and Walker.
1973; U.S. EPA,
19B4. 1990
U.S. EPA. 1986/
Goto et al., 1972;
U.S. EPA, 1987. 1990
U.S. EPA, 1990/
Munlr et al.. 1983;
U.S. EPA. 1987. 1990
NCI. 1978; U.S. EPA.
1990, 1989/NCI.
1978; U.S. EPA,
19803. 1987, 1989.
1990
NacEwen et al., 1981;
U.S. EPA. 1984. 1990/
Blanclflorl. 1970;
U.S. EPA. 1984. 1990
U.S. EPA. 1990
U.S. EPA. 1987. 1989/
NTP, 1986; U.S.
EPA, 1986, 1987. 1989
U.S. EPA. 1984.
1990/U.S. EPA.
1984. 1990
U.S. EPA, 1987/NCI,
1978; U.S. EPA, 1987
0625T
ITiT
                                                                                                                                                 07V24V90

-------
                                                  HEAL1H  EFFECTS  ASSESSMENTS  r   ->RY  TABLF  B:  CARCINOGENICIIY
                                                                      Update:     e.  1990
Compound
2-Methylanlllne
2-Methylanlllne
hydrochlorlde
Exposure
Inhalation; Oral
NA; 2-methylanlllne-
hydrochlorlde In
diet for 93 weeks
NA; 93-week dietary
study
Species Tumor Site
Inhalation Oral Inhalation Oral
NA rat NA skin
NA rat NA skin
EPA Group/Unit Risk
TSlope Factor!
Inhalation Oral
dig/in-1)-1 lug/I)'1 ,
[(nig/kg/day)-1) [(mg/kg/day)-']
B2/ND B2/6.9E-6
[2.4E-1]
B2/ND B2/6.0E-6
[1.8E-1]
Reference
Inhalation/Oral
U.S. EPA. 1987/
Hecht et al.. 1982;
U.S. EPA. 1987
U.S. EPA. 1987/
Hecht et al.. 1982;
U.S. EPA, 1987
Methyl chloride (see Chloromethane)
3-Methylchlol-
anthracene
4.4-Methylenebls
benzelamlne
4,4'-Methylene
bls(N.N'-dlmethyl)
aniline
Melhylene chloride
(dlchloromethane)
Methyl ethyl ketone
Hethylhydrazlne
2-Methyl-5-nltroan111ne
Mlrex
Niagara Blue 4B

NA; 2-year drinking
water
NA; In diet for
59 weeks
Inhalation study;
Inhalation and
drinking water
studies
NA; NA
NA; lifetime
oral study
NA; In diet for
98 weeks
NA; 2-year dietary
study
NA; NA
Data Inadequate for Risk Assessment"
NA rat NA liver
NA rat NA thyroid
mouse mouse lung, liver liver
(also see Table A)
NA NA NA NA
(also see Table A)
NA hamster NA liver
NA mouse NA liver
NA rat NA liver,
adrenal
(also see Table A)
NA NA NA NA

NO ND/7.1E-6
[2.5E-1]
B2a/ND B2a/1.3E-6
[4.6E-2]a
82/4. 1E-6 B2/2.1E-7
[1.4E-2]"1 [7.5E-3J1"
0/NOa D/NOa
NA/ND NA/3.1E-5
[1.1E+0]
C/ND C/9.4E-7
[3.3E-2]
B2/NO 82/5. IE -5
[l.BEtO]
B2/ND B2/NO

NA/NTP, 1983;
U.S. EPA. 1984
U.S. EPA, 1985/
NCI, 1979;
U.S. EPA. 1990
NTP, 1986; U.S. EPA.
1984, 1990/NTP,
1986; NCA. 1983;
U.S. EPA, 1985, 1990
U.S. EPA, 1985. 1988/
U.S. EPA, 1985, 1988
U.S. EPA. 1984/Toth
and Shlmlzu, 1973;
U.S. EPA. 1984
U.S. EPA. 1987/NCI.
1978; U.S. EPA, 1987
U.S. EPA. 1987/
NTP, 1987;
U.S. EPA. 1987
U.S. EPA. 19B7/
U.S. EPA. 1987
0625h
                                                                              B-15
                                                                                                                                                     07/24/90

-------
HtAUH IFFEC1S ASSFSSMFN1S S
                    Update:
                                                                                    TABLE  B:  CARCINOGENICI !Y
                                                                                ie.  1990
Compound
Nickel
Nltrofurazone
2-NUropropane
N-Nltrosodt-n-butyl-
amlne
Nltrosodlethanol-
amlne
N-Nltrosodlethyl-
amlne
N-Nltrosodlmethyl-
amlne
N-Nltrosodlphenyl-
amlne
Exposure Species
Inhalation; Oral Inhalation Oral
occupational; NA human NA
NA; 46-week dietary NA rat
study
22-month Inhalation rat, rat.
study; 22-month rabbit
Inhalation study
drinking water for mouse mouse
life; drinking
water for life
NA; 28 or 64 ppm In NA rat
drinking water for
100 weeks
drinking water rat rat
6 or 12 months;
drinking water
for 6 or 12 months
drinking water; rat rat
drinking water;
NA; 700-day dietary NA rat
study
Tumor Site
Inhalation Oral
respiratory NA
tract
(also see Table A)
NA mammary
liver liver
bladder bladder
esophagus esophagus
NA liver
liver liver
liver liver
NA urinary
bladder
EPA Group/Unit Risk
[Slope Factor 1
Inhalation
(wg/m->)-'
[(mg/kg/day)-1]
nickel
refinery dust: A/
2.4E-4 [8.4E-1]3
nickel subsulflde:
A/4.8E-4 [1.7E+0]3
B2/ND
B2/2.7E-3
[9.4E*0]9
B2/1.6E-3
[5.4E*0]a'b
B2a/N0
B2/4.3E-2
[1.5E+2]a'b
B2/1.4E-2
[5.1E*!]3-0
B2/NDa
Oral
(n9/l»-' ,
[(mg/kg/day)-']
NO/NO'
B2/4.3E-5
[1.5E+0]
2.7E-4
[9.5E*0]9
B2/1.6E-4
[5.4E+OJa
B2/8.0E-5
[2.8E*0]a
B2/4.3E-3
[1.5E+2]3
B2/1.4E-3
[5.1E»lJa
B2/1.4E-7
[4.9E-3]*
Reference
Inhalation/Oral
U.S. EPA, 1986;
Chovll et al..
1981; Enterllne and
Marsh. 1982; Magnus
et al.. 1982; Peto
et al.. 1984;
U.S. EPA. 1984/
U.S. EPA, 1990
U.S. EPA, 1987/
Erturk et al.,
1970; U.S. EPA,
1987
Lewis et al., 1979;
U.S. EPA, 1985/
U.S. EPA, 1985, 1986
Bertram and Craig,
1970; U.S. EPA, 1986,
1990/Bertram and
Craig, 1970; U.S.
EPA, 1986. 1990
U.S. EPA. 1986. 1990/
Lljlnsky and Kovatch,
1985; U.S. EPA. 1986,
1990
Peto et al.. 1984;
U.S. EPA. 1986. 1990/
Peto et al., 1984;
U.S. EPA, 1986, 1990
Peto et al.. 1984;
U.S. EPA. 1986. 1990/
Peto et al.. 1984;
U.S. EPA, 1986. 1990
U.S. EPA, 1987/
NCI. 1979; U.S.
EPA. 1980, 1986,
1987. 1990
0625h

-------
                                                  HIAL1H EFFECTS ASSFSSMFNTS «'""
-------
                                                 HEAUH EFFECTS ASSESSMENTS S""MARY TABLE B:  CARCINOGENICHY
                                                                     Update     IB, 1990
Compound
Polybromlnated
blphenyls





Polychlorlnated
blphenyls

Propylene oxide



RDX (Cyclonlte)




Qulnollne

Selenium sulflde


Slmazlne


Sodium dlethyldlthlo-
carbamate

Exposure Species
Inhalation; Oral Inhalation Oral
NA; F1 remaster FF-1 NA rat
by gavage for 25
weeks followed by
23-month observation



NA; Aroclor 1260 NA rat
In diet

2-year Inhalation mouse rat
study; 150-week
gavage study


NA; 2-year diet NA mouse
study




NA; 20-40-week NA rat
dietary study

NA; 2 -year oral NA rat,
study mouse

NA; NA NA NA


NA; diet NA mouse

Tumor Site
Inhalation Oral
NA hepa to-
cellular
carcinoma
and neo-
plastlc
nodules
(also see Table A)
NA liver

nasal cavity forestomach



NA liver
hepato-
cellular
carcinomas
and adenomas
(also see Table A)
NA liver

NA liver, lung


NA NA


NA hepatoma
(also see Table A)

EPA Group/Unit Risk
[Slope Factor!
Inhalation Oral
[(mg/kg/day)-1] [(mg/kg/day)-1]
B2/ND 82/2. 5E -4
[8.9E+0]





B2/ND B2/2.2E-4
[7.7E»0)a

B2/3.7E-6 B2/6.8E-6
[1.3E-2]* [2.4E-l]f



C/NDf C/3.1E-6'
[1.1E-1]'




C/NO C/3.5E-4
[1.2E*1]

82/NDf B2/NDf


C/NBf C/3.4E-6
[1.2E-1]'

C/ND C/7.7E-6
[2.7E-1]

Reference
Inhalation/Oral
U.S. EPA. 1989/
NTP. 1983; U.S.
EPA, 1989




U.S. EPA. 1984.
1990/Norback and
Weltman, 1985;
U.S. EPA. 1987, 1990
NTP, 1985; Renne
et al.. 1986; U.S.
EPA. 1985. 1990/
Dunkelberg. 1982;
U.S. EPA. 1985. 1990
U.S. EPA. 1988.
1989/Llsh et al..
1984; U.S. EPA.
1988. 1989


U.S. EPA. 1985/
Hlrao et al.. 1976;
U.S. EPA. 1985
U.S. EPA, 1989/
NCI/NTP, 1980;
U.S. EPA. 1989
U.S. EPA, 1984,
19B8/U.S. EPA, 1984,
1987
U.S. EPA, 1988/
BRL. 1968;
U.S. EPA, 1988
Stlrophos (see Tetrachlorvlnphos)
0625h
                                                                             B-18

-------
                                                 HIAL1H EFfECIS ASSESSHEMTS  S'~~MIY  TABLE B: CARCINOGENICIIY
                                                                     Update:      >.  1990
Compound
Styrene
2.3,7,8-TCDD
1,1.1,2-Tetrachloro-
ethane
1,1,2,2-Tetrachloro-
ethane
Telrachloroethy-
lene (perchloroe-
thylene)
p.a.a.o-Tetra-
chlorotoluene
Tetrachlorvlnphos
(stlrophos)
2.4-Toluenedlamlne
Exposure Species
Inhalation; Oral Inhalation Oral
20-month Inhalation rat mouse
study; gavage study
diet; diet rat rat
0-500 mg/kg/day In mouse mouse
corn oil by gavage 5
days/week for 103
weeks0; 0-500
mg/kg/day In corn oil
by gavage 5 days/week
for 103 weeks
gavage; gavage mouse mouse
Inhalation; gavage rat, mouse
mouse
gavage study; mouse mouse
gavage study
NA; 560 -day NA mouse
dietary study
NA; In the diet NA rat
for 103 weeks
EPA Group/Unit Risk
Tumor Site [Slope Factor 1
inhalation Oral Inhalation
dig/m-5)-1 .
[(mg/kg/day)-1 J
leukemia lung and B2/5.7E-7
bronchi [2.0E-3J9
(also see Table A)
several several B2l/3.3E-5s
(pg/m'H .
[1.5E*5]D'f
liver liver C/7.4E-6
[2.6E-2]3-0
liver liver C/5.8E-5
[2.0E-l]a«b
leukemia, liver B2/9.5E-7
liver [3.3E-3]
(also see Table A)
lung lung B2
NA liver C/ND
(also see Table A)
NA mammary gland B2/ND
Oral
(wg/i)-' .
[(mg/kg/day)-']
B2/8.6E-7
[3.0E-2J9
B2J/4.5E+0
[1.5E»5]f
C/7.4E-7
[2.6E-2J3
C/5.8E-6
[2.0E-1]3
B2/1.5E-6
[5.1E-2J9
82/5. 7E-4
[2.0E+1]
C/6.9E-7
[2.4E-2]
B2/9.1E-5
[3.2E+0]
Reference
Inhalation/Oral
Jersey et al.. 1978;
U.S. EPA. 1989/NCI.
1979; U.S. EPA.
1989a,b
Koclba et al..
1978; U.S. EPA,
1984/Koclba et al..
1978; U.S. EPA. 1984
19853. b
NTP, 1983; U.S. EPA,
1990/NTP, 1983; U.S.
EPA, 1990
NCI. 1978; U.S. EPA.
1980. 1986/NCI.
1978; U.S. EPA.
1980, 1990
NTP. 1986; U.S. EPA
1986, 1988/NCI,
1977; U.S. EPA.
1985. 1988
Fukada et al.. 1979;
U.S. EPA, 19B7/
Fukada et al.. 1979;
U.S. EPA, 1987
U.S. EPA. 19B4/
NCI. 1978; U.S. EPA.
1984
U.S. EPA, 1986/
NCI. 1979;
U.S. EPA, 1986
0625h
                                                                              B-19
                                                                                                                                                    07/24/90

-------
                                                 HtALlH EFFECTS ASSESSMENTS SUMMARY TABLF  B:  CARC1NOGEN1CITY
                                                                     Update:     ne, 1990
Compound
o-Toluldlne

p-Toluldlne
Toxaphene


2,4.6-Trlchloroanillne

2.4.6-Trlchloroanlllne
hydrochlorlde
1,1,2-Trlchloroethane


Trkhloroethylene



2.4.6-Trlchlorophenol



Exposure Species
Inhalation; Oral Inhalation Oral
NA; 511 -day NA rat
dietary study
with HC1 salt

NA; 6-12 month NA mouse
dietary study
with the HC1 salt
735-day dietary mouse mouse
study; 735-day
dietary study


NA; diet. HC1 salt NA mouse

NA; diet NA mouse
gavage; gavage mouse mouse


two Inhalation mouse mouse
studies; two
gavage studies


diet; diet mouse mouse



EPA Group/Unit Risk
Tumor Site fSlooe Factorl
Inhalation Oral Inhalation
(,,g/m->)-'
[ (mg/kg/day )-']
NA skin fibroma B2/ND

NA liver C/ND
liver liver B2/3.2E-4
[l.lE+0]a'b


NA unspecified C/ND
tumors of the
vascular system
NA unspecified C/ND
tumors of the
vascular system
liver liver C/1.6E-5
(also see Table A) [5.7E-2]a.°


lung liver B2/1.7E-6 ,
[1.7E-2]f.t



liver liver B2/3.1E-6
[l.lE-2]a



Oral
d.g/1)-' .
[ (mg/kg/day H]
B2/6.9E-6
[2.4E-1]

C/2.6E-5
[1.9E-1]
B2/3.2E-5
[l.lE*0]a


C/l.OE-6
[3.4E-2]

C/8.2E-7
[2.9E-2]
C/1.6E-6
[5.7E-2]3


B2/3.1E-7
[l.lE-2]f.1



B2/3.1E-7
[1.1E-2]3



Reference
Inhalation/Oral
U.S. EPA. 19B4/
Hecht et al..
1982; U.S. EPA.
19B4
U.S. EPA, 1984/
Welsburger et al..
1978; U.S. EPA, 1984
Litton Blonetlcs.
Inc.. 1978;
U.S. EPA.1990/
Litton Blonetlcs,
Inc. ,1978; U.S. EPA,
1980, 1987. 1990
U.S. EPA. 1987/
Welsburger et al..
1978; U.S. EPA, 1987
U.S. EPA. 1987/
Welsburger et al.,
1978; U.S. EPA, 1987
NCI. 1978; U.S. EPA,
1980. 1990/NCI.
1978; U.S. EPA.
1980, 1984, 1990
Mai ton 1 et al..
1986; Fukuda et.
al., 1983/
NCI, 1976; NTP.
1963; U.S. EPA.
1985, 1987, 1988
NCI, 1979; U.S.
EPA. 1980, 1990.
1987/NCI, 1979;
U.S. EPA, 1980.
1984, 1987, 1990
0625h
                                                                              B-20
                                                                                                                                                   07/24/90

-------
                                                 HtAUH EFFECTS ASSESSMENTS '""MARY TABLE B: CARCINOGENICITY
                                                                     Update     tie. 1990


Compound

Trlfluralln



Trlmethyl phosphate


Vinyl bromide
(see bromoethene)
VlnyT chloride






Exposure Species
Inhalation; Oral Inhalation Oral

NA; In the diet NA rat
for 2 years


NA; 10-week gavage NA mouse
study



1-year Inhalation rat rat
study; 10-50 ppm
diet



EPA Group/Unit Risk
Tumor Site [Slope Factor]
Inhalation Oral Inhalation Oral
(pg/m-J)-' (ug/1)-1 ,
t(mg/kg/day)-l] [(mg/kg/dayH J
NA kidney. C/ND C/2.2E-7
(also see bladder and [7.7E-3)a
Table A) thyroid

NA uterus B2/ND B2/1.1E-6
[3.7E-2]



liver lung A/4.2E-5 A/6.5E-S
[2.95E-l]'.f [2.3E+0]f





Reference
Inhalation/Oral

U.S. EPA, 1990/
Emmerson et al.,
19BO; U.S. EPA.
19B4. 1990
U.S. EPA. 1985/
NCI. 1978;
U.S. EPA, 19BS


Maltonl et al.,
1980. 1981; U.S.
EPA. 19B5b; ATSOR.
1988/Feron et al..
1981; U.S. EPA.
1984. 1985a
aVer1Med. available on IRIS
bBased on route-to-route extrapolation
cThere Is Inadequate evidence for carclnogenlclty of this compound by the  oral  route.
''incorporates an absorption factor of 0.4
eBased on occupational data for coke-oven workers
fVerified; Workgroup concurrence on final data base file and IRIS Input  pending
9Under review by CRAVE Workgroup
"Values removed from IRIS pending further review; new verified values are  pending  Input  Into  IRIS.
'Based on metabolized dose
Jfl2  classification  Is  for  2.3.7,8-TCDD alone.   Mixtures consisting of  phenoxy  herbicides  and/or chlorophenols  with 2,3,7,8-TCOD  as a  contaminant  are
 classified as Bl carcinogens.
kA unit risk of 5E-5 (ug/1)"1 has been proposed by the Risk Assessment Forum and  this  recommendation has been scheduled  for SAB review.
0625h
B-21
07/24/90

-------
^Slope fa     Is for Internal dose; ambient concentration was calculated by    jmtng an absorption factor  of 54X.
"•The slope factor, while still available on IRIS. Is being reconsidered by CRAVE  Workgroup.
"This value applies to the mixture of 2,4-  and 2,6-dlnltrotoluene Isomers
"Based on results with 4-chloro-2-methylan111ne hydrochloMde
PAn absorption factor of 30X Is used to calculate the unit risk from the slope factor.
QBased on results with the alpha Isomer
sAn absorption factor of 75X used to calculate the unit risk from the slope factor
*EPA group verified and available on IRIS; quantitative estimates, derived more recently than IRIS evaluation,  have not  been verified.
"For  RCRA activities only,  contact  Sue  Griffin  of Office  of Solid Waste  (FTS 382-639? or  (202)382-6392) for  RCRA-approved  numeric assessment for  this
 compound
 NA = Not applicable; NO = not determined
0625h                                                                         B-22                                                                  07/12/90

-------
           USER'S GUIDE:  RADIONUCLIDE CARCINOGENICITY

     The Health Effects Assessment Summary Table C summarizes the
cancer  slope   factors  and  unit   risk  values   for  selected
radionuclides of potential concern at Superfund sites contaminated
with radioactive materials.  These values  were  calculated by the
Office of Radiation Programs (ORP) and are  intended for use by EPA
risk assessors during  human health risk assessments conducted as
part of  the Superfund remedial investigation/feasibility  study
(RI/FS)  process.   HEAST  users  should  apply   these  values  as
specified by the radiation  risk assessment  guidance  provided in
this section and in Chapter  10 of the Risk Assessment Guidance for
Superfund;  Volume  I,  Human  Health  Evaluation  Manual,  Part  A
(EPA/540/1-89/002),  which  is  available  from  the  Center  for
Environmental Research Information  at  (513)  569-7562.   As risk
assessment methodologies are refined, slope factors and unit risk
values will be revised and updated in Table C.
     EPA classifies all radionuclides as Group A  carcinogens based
on  their property of  emitting ionizing  radiation  and on  the
extensive weight of evidence provided  by epidemiological studies
of radiation-induced cancers  in humans.   Data  derived from both
human studies and animal experiments are used by EPA to construct
mathematical  models of exposure,  dose,  and  risk to  estimate
radionuclide slope factor values.  These models  consider pathways
of exposure, the distinct  metabolic behavior of each element by
compound and the radiological characteristics of each nuclide of

                               C-l

-------
concern, the time and duration of  exposure,  the radiosensitivity
of each target organ  in the body,  the latency  period for cancer
expression in these organs, and the age and sex of individuals in
the exposed population.
     Similar to chemical risk models, radiation models extrapolate
cancer  risks at  low dose and  dose  rate  exposures  from  risks
observed at higher doses using non-threshold, linear dose-response
relationships.   Because of the  radiation risk  models employed,
slope factors for radionuclides are characterized as best estimates
(i.e., maximum likelihood estimates) of the age-averaged lifetime
total excess cancer risk per unit intake or exposure.  HEAST users
should consult Volume I  of  the Background Information  Document for
the Draft Environmental Impact Statement for Proposed NESHAPs for
Radionuclides  (EPA  520/1-89-005)  for  a  more detailed discussion
of EPA's current radiation risk assessment methodology.
     Quantitative carcinogenic estimates listed in Table C* include
the following:
     slope factor  =  risk  per  unit intake or exposure = risk per
     pCi inhaled or ingested or as risk per year per pCi/m due to
     external exposure.
  Slope factors and risk estimates are reported in Table C in units
of activity,  both  in the customary units of  picocuries  (1 pCi =
10"12 curies (Ci)  =  3.7xlO"2 nuclear transformations per second)  for
consistency with the system used for radionuclides  in the IRIS
database, and in the International System (SI)  units of becguerels
(1 Bq = 1 nuclear transformation per second;  approximately 27 pCi).
Users can calculate cancer risks using slope factors  expressed in
either  customary  units   or  SI  units  with  equivalent  results,
provided that they  also use air,  water and  soil concentration
values  in  the  same system  units.    For  simplicity,  examples
presented in text are shown in picocuries only.
                               C-2

-------
     pathway-specific unit risk  = risk per unit concentration in
     air, drinking water  or soil (external exposure)  - risk per
     pCi/m  (air), risk per pCi/L (water), risk per pCi/g (external
     exposure),  or risk pCi/g (soil ingestion).


     Unit  risk   estimates  for   air,  drinking  water,  and  soil

ingestion  pathways  provided  in  Table  C  were  calculated  by

multiplying the  appropriate inhalation and ingestion slope factors

by the inhalation rate (20 m3/day) , the water consumption rate

(2  L/day) ,  or  the soil  ingestion  rate*,  respectively, and by

multiplying all  values  by the total number of days  in 70  years

(i.e., by the lifetime exposure  = 365 days/yr  x 70 yrs = 25,550

days).  Hence,

     risk per pCi/m3  (air)     =     slope factor (risk per pCi
                                   inhaled) x 20 m /day
                                   x 25,550 days

     risk per pCi/L (water)   =    slope  factor   (risk  per  pCi
                                   ingested) x 2 L/day
                                   x 25,550 days

     risk per pCi/g (soil)    =    slope factor (risk per pCi
       (soil ingestion)            ingested) x [(0.2 g/day
                                   x 1,825 days) +  (0.1 g/day
                                   x 23,360 days)]

The  designations "D",  "W",  and  "Y"  presented under  the heading

"ICRP Lung Class" in Table C refer to the lung clearance times for
  Soil  ingestion rates of 0.2 gram per day for children aged 1 year
through  6  years  and 0.1 gram  per day for older age groups were
taken  from EPA's  Interim Final Guidance for Soil Ingestion Rates
(OSWER  Directive  9850.4;  January  27,  1989), available  from the
Office   of  Waste  Enforcement  Programs   at   (202)  382-4814.
Accordingly,  for  lifetime  exposures,   an  individual would  be
expected to consume 365 grams  of  soil  starting  at age 1 to age 6
(i.e., 0.2 g/day x 365 days/year x 5 years), plus 2,336 grams after
age 6 to age 70  (i.e., 0.1 g/day x 365 days x 64  years) for  a total
of approximately 2,700 grams.


                                C-3

-------
inhaled particulate radionuclides expressed as days (D) , weeks (W),
or years  (Y),  as recommended by the  International Commission on
Radiological Protection (ICRP).   Gaseous radionuclides, e.g.,
Rn-222, are assigned to class  "g".  MGI Absorption Factors, f," are
the fractional amounts of each  radionuclide that may be  absorbed
from the gastrointestinal (GI) tract into blood following an oral
intake.  The ICRP  lung clearance  rates and GI absorption factors
provided in Table C are default values used by the EPA to calculate
radionuclide slope factors for inhalation and  ingestion exposures,
respectively.  Application of values other  than those specified in
Table  C will  result in  slope  factors and unit  risk estimates
different  from those provided  in the table.   At this time, EPA
recommends that risk assessors should not replace or substitute for
the default values  listed.
     Values  listed  in  Table C for  external exposure  are best
estimates of the lifetime cancer risk due to the  irradiation of an
individual exposed to gamma-emitting radionuclides uniformly mixed
in soil.  Unit risk estimates for this pathway were calculated by
multiplying  the  appropriate ground surface slope factors by the
effective  surface density of  soil  (i.e., 143  kg/m2 - 0.10 m (soil
depth)  x 1.43X103  kg/m3  (soil density)),   and by multiplying all
values by  70 years  (i.e., by  the lifetime  exposure). Hence,

     risk  per pCi/g (soil)    =    slope factor  (risk  per year
                                    per pCi/mz) x 143 kg/mz
                                    x  10s (g/kg) x 70 years
                               C-4

-------
     External exposure factors do not  include contributions from
decay products, i.e., any radionuclides formed during radioactive
decay.  In some cases, these contributions can be substantial and
should be factored into the risk calculations.   For example,  to
estimate the total lifetime excess cancer risk due to continuous,
lifetime external exposure to soil  contaminated  with Cs-137 at a
level of  1  pCi/g,  risk values must be calculated  for Cs-137 and
Ba-137m in equilibrium concentrations of 1 pCi/g each (assuming
a uniformly mixed source in soil and using the values listed under
"External Exposure" in Table C as follows;

     Total risk =   Risk from Cs-137  +  Risk from Ba-137m
                     (pCi/g Cs-137 x Risk per pCi/g Cs-137)
                    +  (pCi/g Ba-137m x Risk per pCi/g Ba-137m)
                     (1 pCi/g x O.OE+00 risk per pCi/g Cs-137)
                    +  (1 pCi/g x 3.4E-04 risk per pCi/g Ba-137m)
                =   3.4 x 10"* total lifetime excess cancer  risk

     This calculation must be performed in this manner because the
external exposure risk from Cs-137 is due to the photon radiation
emitted by  Ba-137m,  its  immediate short-lived decay product.  In
the  same  manner, the  total lifetime  excess  cancer risk  due to
continuous external exposure to soil contaminated with Ra-226 and
progeny (assuming secular equilibrium)  should  be  calculated  as the
summation of the risks contributed by Ra-226 and each decay product
that emits photon radiation, such as Pb-214 and Bi-214.
                               C-5

-------
     To estimate risk-specific concentrations in air from the unit
risk in air as presented  in Table  C,  the specified level of risk
is divided by the unit risk for air.  Hence, the  air concentration
(in pCi/m3)  corresponding to  a  best  estimate  of  the  increased
lifetime cancer risk of IxlO"5  is calculated as  follows:
          pCi/m  in air
                                       IxlO"5
                              unit risk in (pCi/m3)"1
     Similarly, to estimate risk-specific concentrations  in water
and in soil  (ingestion exposure),  the specified level of risk  is
divided by  the unit risk  for drinking water  or soil ingestion.
Hence, the water concentration (in pCi/L) corresponding to a best
estimate  of the  increased  lifetime  cancer  risk  of IxlO*5   is
calculated as follows:
          pCi/L in water
                                        IxlO"5
                              unit risk in  (pCi/L)*1
and the  soil concentration  (in pCi/g)  corresponding  to a best
estimate  of  the  increased  lifetime  cancer  risk  of  IxlO*5   is
calculated as follows:

     pCi/g in soil                      IxlO*5
  (ingestion exposure)
                              unit risk in  (pCi/g)*1
                                (soil ingestion)
                               C-6

-------
     To estimate risk-specific concentrations in soil from the unit
risk from external exposure as presented in Table  C, the  specified
level of risk  is divided by the unit risk for soil.   Hence, the
soil concentration (in pCi/g) corresponding to a  best estimate of
the  increased  lifetime  cancer  risk  of  IxlO"5 is  calculated as
follows:

     pCi/g in soil                  IxlO"5
  (external exposure)
                            unit risk in  (pCi/g)"1
                             (external exposure)
                               C-7

-------
HEALTH EFFECTS ASSESSMENT SUMMARY TABLE C:  RADIONUCLIDE CARCINOGEHICITY   (Expressed in picocuries (pCi) )




Slope Factor
Pathway-Specific Unit Risk
Age-averaged lifetime excess total
cancer risk per unit intake or
exposure
Nuclide
Ac-225
Ac-227
Ac-228
Ara-241
Am-243
At-217
Ba-137ra
BI-210
Bi-211
81-212
Bi-213
BI-2H
C-14
Ce-144
Cm-243
Cm- 244
Co-60
ICRP"
Lung
Class
Y
Y
Y
W
U
D
D
U
U
W
W
U
g
Y
U
U
Y
Ol~
Absorption
Factor (f,)
1.0E-03
1.0E-03
1.0E-03
1.0E-03
1.0E-03
9.5E-01
1.0E-01
5.0E-02
5.0E-02
5.0E-02
5.0E-02
5.0E-02
9.5E-01
3.0E-04
1.0E-03
1.0E-03
3.0E-01
Inhalation
(PCI)'1
2.4E-09
8.3E-08
2.6E-11
4.0E-08
4.0E-08
5.6E-17
6.0E-16
8.1E-11
1.9E-13
6.9E-12
3.2E-13
2.2E-12
6.4E-15
3.4E-10
3. IE-OS
2.7E-08
1.6E-10
Ingestlon
-;
1.7E-11
3.5E-10
5.1E-13
3.1E-10
3.0E-10
4.SE-18
2.4E-1S
1.9E-12
1.2E-14
3.6E-13
2.3E-13
1.4E-13
9.1E-13
6.1E-12
2.3E-10
2.0E-10
1.5E-11
Ground
Surface
(yr/CpCi/nT))'1
9.4E-13
1.3E-14
5.1E-11
1.6E-12
3.6E-12
1.4E-14
3.4E-11
O.OE+00
2.8E-12
1.0E-11
8.1E-12
8.0E-11
O.OE+00
1.2E-12
8.2E-12
5.8E-14
1.3E-10
Age-averaged lifetime excess total
cancer risk per unit daily intake
or exposure for 70 years
A'r ,
(pCi/mV
1.2E-03
4.2E-02
1.3E-05
2.1E-02
2.1E-02
2.9E-11
3.0E-10
4.1E-05
9.7E-08
3.5E-06
1.6E-07
LIE -06
3.2E-09
1.7E-04
1.6E-02
1.4E-02
8. IE-OS
Drinking
Water
(pCi/L)'1
8.7E-07
1.8E-OS
2.6E-08
1.6E-05
1.5E-05
2.3E-13
1.2E-10
9.7E-08
6.1E-10
1.8E-08
1.2E-08
7.2E-09
4.7E-08
3.0E-07
1.2E-05
1.0E-OS
7.8E-07
External
Exposure
(pCi/gr
9.4E-06
1.3E-07
5.1E-04
1.6E-05
3.6E-05
1.4E-07
3.4E-04
O.OE+00
2.8E-05
1.0E-04
8.1E-05
8.0E-04
O.OE+00
1.2E-05
8.2E-05
5.9E-07
1.3E-03
Soil
Ingest ion
(pCi/g)''
4.6E-08
9.5E-07
1.4E-09
8.4E-07
8.1E-07
1.2E-14
6.5E-12
5.1E-09
3.2E-11
9.7E-10
6.2E-10
3.8E-10
2.5E-09
1.6E-08
6.2E-07
5.4E-07
4. IE-OS
                                      C-8

-------
HEALTH EFFECTS ASSESSMENT SUMMARY TABLE C:  RADIOMJCLIDE CARCINOGENICITT   (Expressed in picocuries (pCl) )




Slope Factor
Pathway-Specific Unit Risk
Age- averaged lifetime excess total
cancer risk per unit intake or
exposure
Nuclide
Cr-51
Cs-134
Cs-135
Cs-137
Eu-152
Eu-154
Fe-59
Fr-221
H-3
1-125
1-129
1-131
1-133
K-40
Hn-54
No-99
ICRP**
Lung
Class
Y
D
0
D
U
U
W
0
9
D
D
0
0
D
W
Y
Gl~
Absorption
Factor (f/)
1.0E-01
9.SE-01
9.5E-01
9.5E-01
1.0E-02
1.0E-02
1.0E-01
9.SE-01
9.5E-01
9.5E-01
9.SE-01
9.5E-01
9.5E-01
9.5E-01
1.0E-01
8.0E-01
Inhalation
(pCiT
3.0E-13
2.8E-11
2.7E-12
1.9E-11
1.2E-08
1.4E-10
9.8E-12
9.2E-13
7.8E-14
1.7E-11
1.2E-10
2.4E-11
1.2E-11
7.6E-12
5.3E-12
2.6E-12
Ingestion
(pCl)'1
4.2E-14
4.2E-11
4.0E-12
2.8E-11
2.1E-12
3.0E-12
2.8E-12
5.9E-14
5.5E-14
2.6E-11
1.9E-10
3.6E-11
2.1E-11
1.1E-11
1.1E-12
1.7E-12
Ground
Surface

-------
HEALTH EFFECTS ASSESSMENT SUMMARY TABLE C:  RADIONUCLIDE CARCINOGENICITY   (Expressed in picocuries (pCi) )
                               Slope Factor

                     Age-averaged lifetime  excess total
                     cancer risk  per  unit intake or
                     exposure
    Pathway-Specific Unit Risk

Age-averaged lifetime excess total
cancer risk per unit daily intake
or exposure for 70 years
Nuclide
Mb-94
Hi -59
Mi -63
HI -65
Up- 237
Mp- 239
P-32
Pa-231
Pa-233
Pa- 234
Pa-234m
Pb-209
Pb-210
Pb-211
Pb-212
Pb-214
Po-210
Po-212
Po-213
Po-214
Po-215
ICRP"
Lung
Class
Y
U
W
U
U
U
D
Y
Y
Y
Y
D
D
D
D
D
U
U
U
U
U
••C
Gl
Absorption
Factor (f/>
1.0E-02
5.0E-02
5.0E-02
5.0E-02
1.0E-03
1.0E-03
8.0E-01
1.0E-03
1.0E-03
1.0E-03
1.0E-03
2.0E-01
2.0E-01
2.0E-01
2.0E-01
2.0E-01
1.0E-01
1.0E-01
1.0E-01
1.0E-01
1.0E-01
Inhalation
(pCi)'1
2.1E-10
6.9E-13
1.7E-12
1.9E-13
3.6E-08
1.5E-12
3.0E-12
4.0E-08
8.7E-12
5.4E-13
1.6E-15
7.0E-14
1.7E-09
2.9E-12
4.7E-11
2.9E-12
2.7E-09
6.1E-22
B.OE-21
2.8E-19
5.7E-18
Ingest ion
(PCI)''
2.1E-12
8.7E-14
2.3E-13
2.6E-13
2.7E-10
9.3E-13
3.5E-12
1.9E-10
1.0E-12
6.8E-13
5.8E-15
8.5E-14
6.5E-10
1.8E-13
7.2E-12
1.8E-13
2.6E-10
2.2E-23
3.2E-22
1.0E-20
2.8E-19
Ground
Surface

-------
HEALTH EFFECTS ASSESSMENT SUMMARY TABLE C:  RADIONUCLIDE CARCINOGENIC1TT   (Expressed in picocuries (pCi) )
                               Slope Factor

                     Age-averaged  lifetime  excess total
                     cancer  risk per unit intake or
                     exposure
    Pathway-Specific Unit Risk

Age-averaged lifetime excess total
cancer risk per unit daily intake
or exposure for 70 years
Huclide
Pu-238
Pu-239
Pu-240
Pu-241
Pu-242
Ra-223
Ra-224
Ra-225
Ra-226
Ra-228
Rn-219
Rn-220
Rn-222
Ru-106
S-35
Sr-89
Sr-90
Tc-99
Tc-99m
ICRP"
Lung
Class
Y
Y
Y
Y
Y
U
U
W
U
U
g
g
9
Y
D
D
D
U
U
Gl™
Absorption
Factor (fj)
1.0E-03
1.0E-04
1.0E-04
1.0E-03
1.0E-04
2.0E-01
2.0E-01
2.0E-01
2.0E-01
2.0E-01
..
..
--
5.0E-02
8.0E-01
3.0E-01
3.0E-01
8.0E-01
8.0E-01
Inhalation
(pCi)'1
4.2E-08
4.1E-08
4.1E-08
2.9E-10
3.9E-08
3.1E-09
1.2E-09
1 .66-09
3.0E-09
6.5E-10
4.6E-14
1.2E-13
7.2E-13
4.4E-10
1.9E-13
2.9E-12
5.6E-11
8.3E-12
2.7E-14
Ingest ion
(pCi)'1
2.8E-10
3.1E-11
3.1E-11
4.8E-12
3.0E-11
8.0E-11
4.8E-11
6.6E-11
1.2E-10
1.0E-10
..
..
-•
9.6E-12
2.2E-13
3.0E-12
3.3E-11
1.3E-12
5.1E-14
Ground
Surface

-------
                              HEALTH EFFECTS ASSESSMEHT SUNWRT TABLE C:  RADIONUCLIDE CARCINOGEHICITT   (Expressed in picocuries  (pCl) )
MucUde
ICRP
Lung
Class
 GI
Absorption
Factor (fj)
                                                             Slope Factor

                                                   Age-averaged lifetime excess total
                                                   cancer risk per unit intake or
                                                   exposure
Inhalation       Ingestton
(pCt)';           (pel)'1
                 Ground
                 Surface
                 (yr/tpCi/n7))'1
                                                                                                          Pathway-Specific Unit Risk

                                                                                                     Age-averaged  lifetime excess total
                                                                                                     cancer  risk per unit daily  intake
                                                                                                     or  exposure for 70 years
                                                                                                           Air
                                         Drinking
                                         Water
                         (pCl/mV1        (pCi/L)'1
                                 External
                                 Exposure
                                 (DCi/g)'1
                                 Soil
                                 Ingestton
                                 (pCI/g)1
Th-227
Th-228
Th-229
Th-230
Th-231
Th-232
Th-234

Tl-207
Tl-208
Tl-209

U-233
U-234
U-235
U-238

Y-90
Y
Y
Y
Y
Y
Y
Y

D
D
D

Y
Y
Y
Y
2.0E-04
2.0E-04
2.0E-04
2.0E-04
2.0E-04
2.0E-04
2.0E-04

9.5E-01
9.SE-01
9.5E-01

2.0E-01
2.0E-01
2.0E-01
2.0E-01

1.0E-04
4.9E-09
7.7E-08
7.7E-08
3.1E-08
4.9E-13
3.1E-08
3.2E-11

4.5E-15
5.1E-15
4.3E-15

2.7E-08
2.7E-08
2.5E-08
2.4E-08

5.5E-12
4.8E-12
1.5E-11
3.9E-11
2.4E-11
4.0E-13
2.2E-11
4.0E-12
 .3E-14
 .8E-14
 .4E-14

 .4E-10
 .4E-10
 .3E-10
 .3E-10

3.2E-12
6.6E-12
1.6E-13
5.8E-12
5.9E-14
1.1E-12
4.6E-14
5.6E-13

1.2E-13
1.7E-10
1.IE-ID

3.2E-14
5.7E-14
9.6E-12
4.6E-14

O.OE+00
2.SE-03
3.9E-02
3.9E-02
1.6E-02
2.5E-07
1.6E-02
1.6E-OS

2.3E-09
2.6E-09
2.2E-09

1.4E-02
1.4E-02
1.3E-02
1.2E-02

2.8E-06
2.5E-07
7.7E-07
2.0E-06
1.2E-06
2.0E-08
1.1E-06
2.0E-07

6.6E-10
9.2E-10
7.2E-10

7.2E-06
7.2E-06
6.6E-06
6.6E-06

1.6E-07
6.6E-06
1.6E-06
5.8E-OS
5.9E-07
LIE-OS
4.5E-07
S.6E-06

1.2E-06
1.7E-03
1.1E-03

3.2E-07
5.6E-07
9.7E-05
4.5E-07

O.OE+00
1.3E-OB
4.IE-OS
1.1E-07
6.5E-08
1.1E-09
S.9E-08
1.IE-OS

3.5E-11
4.9E-11
3.BE-11

3.8E-07
3.8E-07
3.5E-07
3.5E-07

8.6E-09
*    A picocurie is a unit of activity equal to 3.7E-02 nuclear transformations per second:  1 pel = 1.0E-12 curies  (C<)  =  3.7E-02 becquerels  (Bq).
".   Lung clearance classifications recommended by the International Commission on Radiological Protection (ICRP); "D" (days),  "W" (weeks), "Y"  (years), "g"
     Gastrointestinal (GI) absorption factors, i.e. fractional uptake of a radionuclide from the gut into blood.
                                                                                                                                               (gas).
                                                                     C-12

-------
HEALTH EFFECTS ASSESSMENT SUMMARY TABLE C:  RADIONUCLIDE CARCINOGENICITT   (Expressed in Becquerels (Bq) )
Slope Factor
Age-averaged lifetime excess total
cancer risk per unit Intake or
exposure
Nucllde
Ac-225
Ac-227
Ac-228
Am-241
Am-243
At-217
Ba-137m
Bi-210
B1-211
Bi-212
B1-213
B1-214
C-U
Ce-144
Qn-243
Cm-244
Co-60
ICRP"
Lung
Class
Y
Y
Y
U
U
D
D
U
W
U
U
U
g
Y
U
U
Y
Gl~
Absorption
Factor 
-------
HEALTH EFFECTS ASSESSMENT SUMMARY TABLE C:  RADIONUCLIOE CARCINOGEHICITT   (Expressed in Becquerels (Bq) )




Slope Factor
Pathway-Specific Unit Risk
Age-averaged lifetime excess total
cancer risk per unit Intake or
exposure
Nucllde
Cr-51
Cs-134
Cs-135
Cs-137
Eu-152
Eu-154
Fe-59
Fr-221
H-3
1-125
1-129
1-131
1-133
K-40
Hn-54
Mo-99
ICRP"
Lung
Class
Y
D
D
D
U
U
U
D
9
D
0
D
0
0
U
Y
CI*M
Absorption
Factor (ff)
1.0E-01
9.5E-01
9.5E-01
9.5E-01
1.0E-02
1.0E-02
1.0E-01
9.5E-01
9.5E-01
9.5E-01
9.5E-01
9.5E-01
9.5E-01
9.5E-01
1.0E-01
B.OE-01
Inhalation
(Bq)-'
B.1E-12
7.6E-10
7.3E-11
5.1E-10
3.2E-07
3.8E-09
2.6E-10
2.5E-11
2.1E-12
4.6E-10
3.2E-09
6.SE-10
3.2E-10
2.1E-10
1.4E-10
7.0E-11
Ingest I on
(Bq)'1
1.1E-12
1.1E-09
1.1E-10
7.6E-10
5.7E-11
8.1E-11
7.6E-11
1.6E-12
1.SE-12
7.0E-10
5.1E-09
9.7E-10
5.7E-10
3.0E-10
3.0E-11
4.6E-11
Ground
Surface
(yr/(Bq/nOr
5.1E-11
2.4E-09
O.OE+00
O.OE+00
1.7E-09
1.8E-09
1.7E-09
5.1E-11
O.OE+00
4.6E-11
4.1E-11
7.BE-10
9.5E-10
2.1E-10
1.3E-09
2.4E-10
Age-averaged lifetime excess total
cancer risk per unit daily intake
or exposure for 70 years
*>rj I
(Bq/mV
4.1E-06
3.9E-04
3.7E-05
2.6E-04
1.7E-01
1.9E-03
1.3E-04
1.3E-05
1.1E-06
2.3E-04
1.6E-03
3.3E-04
1.7E-04
1.1E-04
7.2E-05
3.6E-05
Drinking
Water
(Bq/L)'1
5.6E-08
5.6E-05
5.6E-06
3.9E-OS
2.9E-06
4.1E-06
3.9E-06
8.1E-08
7.7E-08
3.6E-05
2.6E-04
5.0E-OS
2.9E-05
1.5E-05
1.5E-06
2.4E-06
External
Exposure
(Bq/g)J
5.1E-04
2.4E-02
O.OE+00
O.OE+00
1.7E-02
1.8E-02
1.7E-02
5.1E-04
O.OE+00
4.6E-04
4.1E-04
7.BE-03
9.5E-03
2.1E-03
1.3E-02
2.4E-03
Soil
Ingestion
(Bq/g)'1
3.0E-09
3.0E-06
3.0E-07
2.1E-06
1.5E-07
2.2E-07
2.1E-07
4.3E-09
4.1E-09
1.9E-06
1.4E-OS
2.6E-06
1.SE-06
8.1E-07
8.1E-08
1.2E-07
                                       C-1A

-------
HEALTH EFFECTS ASSESSMENT SUMMARY TABLE C:  RADIONUCLIDE  CARCIHOGEHICITT   (Expressed In Beoquerets (Bq)')
                              Slope Factor

                    Age-averaged lifetime excess total
                    cancer risk per unit intake or
                    exposure
    Pathway-Specific unit Risk

Age-averaged lifetime excess total
cancer risk per unit daily intake
or exposure for 70 years
Nucllde
Mb-94
Mi -59
Mi -63
Hi -65
Np-237
Hp- 239
P-32
Pa-231
Pa-233
Pa- 234
Pa-234m
Pb-209
Pb-210
Pb-211
Pb-212
Pb-2U
Po-210
Po-212
Po-213
Po-214
Po-215
ICRP"
Lung
Class
Y
U
U
U
U
U
D
V
Y
Y
Y
D
D
D
D
D
U
U
U
U
U
Gl'M
Absorption
Factor (fj)
1.0E-02
5.0E-02
5.0E-02
5.0E-02
1.0E-03
1.0E-03
8.0E-01
1.0E-03
1.0E-03
1.0E-03
1.0E-03
2.0E-01
2.0E-01
2.0E-01
2.0E-01
2.0E-01
1.0E-01
1.0E-01
1.0E-01
1.0E-01
1.0E-01
Inhalation
(Bq>-/
5.7E-09
1.9E-11
4.6E-11
5.1E-12
9.7E-07
4.1E-11
8.1E-11
1.1E-06
2.4E-10
1.5E-11
4.3E-14
1.9E-12
4.6E-08
7.8E-11
1.3E-09
7.8E-11
7.3E-11
1.6E-20
2.2E-19
7.6E-18
1.5E-16
Ingestion
(Bq)-'
5.7E-11
2.4E-12
6.2E-12
7.0E-12
7.3E-09
2.5E-11
9.5E-11
5.1E-09
2.7E-11
1.8E-11
1.6E-13
2.3E-12
1.8E-08
4.9E-12
1.9E-10
4.9E-12
7.0E-09
5.9E-22
8.6E-21
2.7E-19
7.6E-18
Ground
Surface
(yr/(Bq/fl6r
2.4E-09
9.2E-13
O.OE+00
7.6E-10
4.9E-11
3.0E-10
O.OE+00
5.4E-11
3.5E-10
3.0E-09
1.7E-11
O.OE+00
4.9E-12
7.8E-11
2.5E-10
4.2E-10
1.3E-14
O.OE+00
4.6E-14
1.3E-13
2.4E-13
Mrj 1
(Bq/nfV
2.9E-03
9.5E-06
2.3E-05
2.6E-06
5.0E-01
2.1E-05
4.1E-05
5.5E-01
1.2E-04
7.5E-06
2.2E-08
9.7E-07
2.4E-02
4.0E-05
6.5E-04
4.0E-05
3.7E-05
B.4E-15
1.1E-13
3.9E-12
7.9E-11
Drinking
Water
(Bo/LV1
2.9E-06
1.2E-07
3.2E-07
3.6E-07
3.7E-04
1.3E-06
4.9E-06
2.6E-04
1.4E-06
9.4E-07
8.0E-09
1.2E-07
9.2E-04
2.5E-07
9.9E-06
2.5E-07
3.6E-04
3.0E-17
4.4E-16
1.4E-14
3.9E-13
External
Exposure
(Bq/g)-;
2.4E-02
9.2E-06
O.OE+00
7.6E-03
4.9E-04
3.0E-03
O.OE+00
5.4E-04
3.5E-03
3.0E-02
1.7E-04
O.OE+00
4.9E-05
7.8E-04
2.5E-03
4.2E-03
1.3E-07
O.OE+00
4.6E-07
1.3E-06
2.4E-06
Soil
Ingestion
(Bq/g)''
1.5E-07
6.4E-09
1.7E-08
1.9E-08
2.0E-05
6.8E-08
2.6E-07
1.4E-05
7.3E-08
5.0E-08
4.2E-10
6.2E-09
4.9E-05
1.3E-08
5.3E-07
1.3E-08
1.9E-05
1.6E-18
2.3E-17
7.3E-16
2.0E-14
                                       C-15

-------
HEALTH EFFECTS ASSESSMENT SUMARV TABLE C:   RADIONUCLIDE CARCINOGENICITT   (Expressed in Becquerels (Bq) )
                              Slope Factor

                    Age-averaged lifetime excess total
                    cancer risk per unit intake or
                    exposure
    Pathway-Specific unit Risk

Age-averaged lifetime excess total
cancer risk per unit daily intake
or exposure for 70 years
Nuclide
Pu-238
Pu-239
Pu-240
Pu-241
Pu-242
Ra-223
Ra-224
Ra-225
Ra-226
Ra-228
Rn-219
Rn-220
Rn-222
Ru-106
S-35
Sr-89
Sr-90
Tc-99
Tc-99m
ICRP**
Lung
Class
T
Y
T
Y
Y
U
W
W
U
U
g
g
g
Y
D
D
D
U
W
el*"
Absorption
Factor (fj)
.OE-03
.OE-04
.OE-04
.OE-03
.OE-04
2.0E-01
2.0E-01
2.0E-01
2.0E-01
2.0E-01
— —
5.0E-02
8.0E-01
3.0E-01
3.0E-01
8.0E-01
8.0E-01
Inhalation
(Bq)-'
1.1E-06
1.1E-06
1.1E-06
7.8E-09
1.1E-06
8.4E-08
3.2E-08
4.3E-08
8.1E-08
1.8E-08
1.2E-12
3.2E-12
1.9E-11
1.2E-08
5.1E-12
7.8E-11
1.5E-09
2.2E-10
7.3E-13
Ingest ion
(Bq)J
7.6E-09
8.4E-10
8.4E-10
1.3E-10
8.1E-10
2.2E-09
1.3E-09
1.8E-09
3.2E-09
2.7E-09
"•
2.6E-10
5.9E-12
8.1E-11
8.9E-10
3.5E-11
1.4E-12
Ground
Surface
(yr/(Bq/nf))'
1.6E-12
7.0E-13
1.6E-12
O.OE+00
1.3E-12
2.3E-10
1.7E-11
2.2E-11
1.1E-11
1.5E-18
9.5E-11
B.1E-13
5.9E-13
O.OE+00
O.OE+00
2.1E-13
O.OE+00
9.2E-16
2.2E-10
*'[> I
(Bq/fflV
5.6E-01
5.6E-01
5.6E-01
4. OE-03
S.6E-01
4.3E-02
1.7E-02
2.2E-02
4.1E-02
9.2E-03
6.4E-07
1.7E-06
9.9E-06
6.1E-03
2.6E-06
4.0E-05
7.7E-04
1.1E-04
3.7E-07
Drinking
Water
(Bq/L)"1
3.9E-04
4.3E-05
4.3E-05
6.6E-06
4. IE-OS
1.1E-04
6.6E-OS
9. IE-OS
1.6E-04
1.4E-04
_.
1.3E-05
3.0E-07
4.1E-06
4.5E-05
1.8E-06
7.2E-08
External
Exposure
(Bq/g)-'
1.6E-05
7.0E-06
1.6E-OS
O.OE+00
1.3E-OS
2.3E-03
1.7E-04
2.2E-04
1.1E-04
1.SE-11
9.SE-04
8.1E-06
6.0E-06
O.OE+00
O.OE+00
2.1E-06
O.OE+00
9.2E-09
2.2E-03
Soil
Ingestion
(Bq/g)1
2. IE-OS
2.3E-06
2.3E-06
3.5E-07
2.2E-06
S.8E-06
3.5E-06
4.8E-06
B.6E-06
7.3E-06
• »
7.0E-07
1.6E-08
2.2E-07
2.4E-06
9.SE-08
3.8E-09
                                      C-16

-------
                              HEALTH EFFECTS ASSESSMENT SUMMARY TABLE C:  RADIONUCLIDE CARCINOGENICITT   (Expressed in Becquerels (Bq) )
                                                            Slope Factor

                                                  Age-averaged lifetime excess total
                                                  cancer risk per unit intake or
                                                  exposure
    Pathway-Specific Unit Risk

Age-averaged lifetime excess total
cancer risk per unit daily intake
or exposure for 70 years
Nuclide
Th-227
Th-228
Th-229
Th-230
Th-231
Th-232
Th-234
Tl-207
Tl-208
Tl-209
U-233
U-234
U-235
U-238
Y-90
ICRP"
Lung
Class
T
T
V
V
Y
Y
Y
D
D
0
Y
Y
Y
Y
Y
GI™
Absorption
Factor (f;)
2.0E-04
2.0E-04
2.0E-04
2.0E-04
2.0E-04
2.0E-04
2.0E-04
9.5E-01
9.5E-01
9.5E-01
2.0E-01
2.0E-01
2.0E-01
2.0E-01
1.0E-04
Inhalation
(Bqr
1.3E-07
2.1E-06
2.1E-06
8.4E-07
1.3E-11
8.4E-07
8.6E-10
1.2E-13
1.4E-13
1.2E-13
7.3E-07
7.3E-07
6.8E-07
6.5E-07
1.5E-10
Ingest ion
(Bq)''
1.3E-10
4.1E-10
1.1E-09
6.5E-10
1.1E-11
S.9E-10
1.1E-10
3.5E-13
4.9E-13
3.8E-13
3.8E-09
3.8E-09
3.5E-09
3.5E-09
8.6E-11
Ground
Surface
(yr/(Bq/mi))-l
1.8E-10
4.3E-12
1.6E-10
1.6E-12
3.0E-11
1.2E-12
1.5E-11
3.2E-12
4.6E-09
3.0E-09
8.6E-13
1.5E-12
2.6E-10
1.2E-12
O.OE+00
Air
(Bq/mV
6.8E-02
1.1E+00
1.1E+00
4.3E-01
6.8E-06
4.3E-01
4.4E-04
6.2E-08
7.0E-08
5.9E-08
3.7E-01
3.7E-01
3.5E-01
3.3E-01
7.6E-05
Drinking
Water
(Bq/L)-l
6.6E-06
2.1E-05
5.4E-05
3.3E-05
5.5E-07
3.0E-OS
5.5E-06
1.8E-08
2.5E-08
1.9E-08
1.9E-04
1.9E-04
1.8E-04
1.8E-04
4.4E-06
External
Exposure
(Bq/a)'
1.8E-03
4.3E-05
1.6E-03
1.6E-05
3.0E-04
1.2E-05
1.SE-04
3.2E-05
4.6E-02
3.0E-02
B.7E-06
1.5E-05
2.6E-03
1.2E-05
O.OE+00
Soil
Ingest I on
(Bq/gr
3.5E-07
1.1E-06
2.8E-06
1.8E-06
2.9E-08
1.6E-06
2.9E-07
9.5E-10
1.3E-09
1.0E-09
1.0E-05
1.0E-05
9.5E-06
9.5E-06
2.3E-07
'    A Becquerel is a unit  of activity equal  to one nuclear  transformation per second: 1 Bq » 2.7E-11 curies (Ci) = 27.027 picocuries  (pCi).
"    Lung clearance classifications recommended by the International Commission on Radiological Protection (ICRP); "D" (days).  "W"  (weeks). "Y" (years), "g"
'"   Gastrointestinal (GI)  absorption factors,  i.e.,  fractional uptake of a radionuclide from the gut into blood.
                                         (gas).
                                                                     C-17

-------
                                 REFERENCES

                    HEA SUMMARY  TABLE A: NONCARCIMOGENS

Acenaphthene
U.S. EPA.   1987.   Health  Effects  Assessment for  Acenaphthene.   Prepared by
the  Office  of  Health and  Environmental  Assessment.  Environmental  Criteria
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Remedial Response. Washington, DC.

U.S.  EPA.    1989.   Mouse  oral  subchronic  study  with acenaphthene.   Study
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Acenaphthylene
U.S. EPA.   1987.   Health  Effects Assessment for Acenaphthylene.  Prepared by
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Acephate
Chevron  Chemical  Company.   1987.  Confidential Business  Information;  unpub-
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U.S.  EPA.   1984.   Health  and  Environmental  Effects  Profile  for Acephate.
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U.S. EPA.   1989.   Integrated  Risk  Information System  (IRIS).  Reference Dose
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01/18/89.)   Office of Health  and  Environmental   Assessment,  Environmental
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Acetone
U.S.  EPA.    1986.   Ninety-day gavage  study  in albino  rats  using  acetone.
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U.S.  EPA.   1988.   Updated  Health  Effects  Assessment  for Acetone.  Prepared
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U.S.  EPA.   1990.    Integrated  Risk  Information  System  (IRIS).   Online.
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Acetone  cvanohydrin
Blank,  T.L.  and   D.C. Thake.   1984.   Three-Month  Inhalation  Toxicity of
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0121h                               0-1                              06/15/90

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Howard.  J.W.  and  R.F.  Hanzal.   1955.   Chronic  toxicity  for rats  oF  Food
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U.S. EPA.   1985a.   Drinking Water  Criteria Document  For Cyanide.   Prepared
by the OFFice  oF  Health and Environmental  Assessment, Environmental Criteria
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Washington, DC.  Final DraFt.

U.S.  EPA.    1985b.   Health  and  Environmental  EFFects  ProFile  For  Acetone
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U.S.  EPA.    1988.   Health and  Environmental   EFFects  Document For Cyano-
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Acetonitrile
Coate,  W.B.   1983.   90-Day subchronic toxicity study  oF acetonitrile  in
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U.S. EPA.   1987.   Health  EFFects Assessment  For Acetonitrile.  Prepared by
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U.S.  EPA.    1990.   Integrated   Risk  Information  System  (IRIS): Online.(RFD)
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Assessment OFFice, Cincinnati,  OH.

Acetophenone
Imasheva,  N.B.   1966.    Threshold  concentrations  oF   acetophenone  during
short- and  long-term  inhalation.  In:  AICE  Survey  oF  USSR  Air  Pollution
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eFFect  and  the  public   health  aspects  oF  atmospheric  pollutants,  M.Y.
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Hagan, E.C., W.H.  Hansen.  D.G. Fitzhugh, et al.   1967.   Food  Flavorings and
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U.S.  EPA.   1987.   Health  EFFects Assessment  For Acetophenone.  Prepared by
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Emergency  Response, Washington, DC.

U.S.   EPA.   1990.   Integrated   Risk   InFormation   System  (IRIS).    Online.
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Assessment  OFFice, Cincinnati,  OH.
0121h                               D-2                               06/14/90

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Acrolein
Costa, D.L., R.S.  Kutzman,  J.R.  Lehmann and R.T.  Drew.   1986.   Altered lung
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Kutzman,  R.S.,  E.A.  Popenoe.  M.  Schmaeler and  R.T.  Drew.   1985.  Changes in
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U.S.  EPA.   1987.   Health Effects  Assessment for  Acrolein.   Prepared by the
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Acrvlamide
Burek,  J.D.,  R.R. Albee, J.E.  Beyer,  et al.   1980.  Subchronic toxicity of
toxicity  of acrylamide  administered  to rats in  the drinking water followed
by up to  144 days of recovery.  J. Environ. Pathol Toxicol.  4:  157-182.

U.S.  EPA.   1985.   Health and Environmental  Effects Profile for Acrylamide.
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U.S.  EPA.   1990.   Integrated  Risk  Information  System   (IRIS).   Online.
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Acrylic acid
DePass  L.R.,  M.D. Woodside,  R.H.  Garman  and C.S.  Weil.   1983.  Subchronic
and  reproductive  toxicology studies on acrylic  acid  in drinking water of the
rat.  Drug  Chem. Toxicol.  6(1): 1-20.

U.S.  EPA.   1984.   Health  and  Environmental   Effects  Profile  for Acrylic
Acid.   Prepared   by   the  Office  of  Health  and  Environmental Assessment,
Environmental  Criteria and  Assessment Office,  Cincinnati,  OH for the Office
of Solid  Waste. Washington, DC.

U.S.  EPA.   1990.    Integrated  Risk   Information  System   (IRIS).   Online.
Office  of  Health and  Environmental  Assessment,  Environmental  Criteria and
Assessment Office, Cincinnati, OH.
 Oi21h                                D-3                               06/14/90

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Adlponltrlle
U.S.  EPA.   1987.   Health  Effects  Assessment for Adlponltrlle.   Prepared by
the  Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria
and  Assessment  Office.  Cincinnati.  OH  for  the  Office  of  Solid Waste  and
Emergency Response. Washington. DC.

Alachlor
Monsanto  Company.    1984.    Confidential  Business  Information;  unpublished
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U.S.  EPA.   1984.   Health   and  Environmental Effects  Profile  for  Alachlor.
Prepared by the Office of  Health and  Environmental  Assessment. Environmental
Criteria  and  Assessment  Office,   Cincinnati, OH  for  the  Office  of  Solid
Waste, Washington,  DC.

U.S.  EPA.   1989.    Integrated  Risk  Information  System  (IRIS).    Online.
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Assessment Office,  Cincinnati, OH.

Aldlcarb
U.S.  EPA.   1990.    Integrated  Risk  Information  System  (IRIS).    Online.
Office  of  Health  and  Environmental  Assessment,  Environmental Criteria  and
Assessment Office,  Cincinnati, OH.

Well, C.S. and  C.P.  Carpenter.   1968.   Temlk sulfoxlde.   Results of  feeding
1n  the  diet  of rats  for  six months  and   dogs  for  three months.   Mellon
Institute Report No. 31-141.  EPA  Pesticide  Petition No. 9F0798.

Aldrln
Fltzhugh,  O.G., A.A.  Nelson and M.L.  Qualfe.  1964.   Chronic  oral  toxlclty
of aldrln and dleldrln In rats and  dogs.   Food Cosmet.  Toxlcol.  2:  551-562.

U.S.  EPA.   1987.    Health  Effects  Assessment  for Aldrln.   Prepared  by  the
Office  of  Health  and  Environmental  Assessment,  Environmental Criteria  and
Assessment Office,  Cincinnati,  OH  for the  Office of  Emergency and  Remedial
Response,  Washington, DC.

U.S.  EPA.   1990.    Integrated  Risk  Information  System  (IRIS).    Online.
Office  of  Health  and  Environmental  Assessment,  Environmental Criteria  and
Assessment Office,  Cincinnati, OH.

Allldochlor
U.S.  EPA.  1984.   Health and Environmental   Effects  Profile  for Allldochlor.
Prepared by the Office of  Health and  Environmental  Assessment, Environmental
Criteria  and  Assessment  Office,   Cincinnati, OH  for  the  Office  of  Solid
Waste, Washington,  DC.
Ally! alcohol
Carpanlnl, F.M.B., I.F. Gaunt,  J.  Hardy,  et al.
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               1978.   Short-term toxldty
U.S.  EPA.   1985.    Health  and  Environmental   Effects  Profile  for  Allyl
Alcohol.   Prepared  by  the Office  of Health  and Environmental  Assessment,
Environmental Criteria  and  Assessment Office,  Cincinnati, OH  for  the Office
of Solid Waste and  Emergency Response, Washington, DC.
0121h
D-4
07/11/90

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U.S.  EPA.   1990.    Integrated  Risk  Information  System  (IRIS).   Online.
Office of  Health and  Environmental  Assessment,  Environmental Criteria  and
Assessment Office,  Cincinnati,  OH.
Ally! chloride (3-Chloropropene)
ACGIH  (American  Conference  of  Governmental
Documentation of  the  Threshold  Limit Values
Air, 4th ed.  Conclnnatl,  OH.  p.  12.
                         Industrial  HyglenUts).   1980.
                         for  Substances 1n the  Workroom
U.S.  EPA.    1983.   Health  and  Environmental   Effects   Profile  for  Chloro-
propenes.  Prepared  by the  Office of  Health  and  Environmental  Assessment,
Environmental Criteria and  Assessment  Office,  Cincinnati, OH  for  the Office
of Solid Waste,  Washington,  DC.

Aluminum
U.S. EPA.  1987.   Health  Effects  Assessment  for  Aluminum.  Prepared  by  the
Office  of  Health and  Environmental  Assessment,  Environmental Criteria  and
Assessment Office, Cincinnati,  OH for  the  Office of Emergency and Remedial
Response, Washington,  DC.

Aluminum phosphide
Hackenburg,  U.   1972.   Chronic  Ingestlon  by rats  of standard diet  treated
with aluminum phosphide.   Toxlcol.  Appl.  Pharmacol.  23(1):  147-158.

U.S.   EPA.   1990.    Integrated   Risk   Information  System (IRIS).   Online.
Office  of  Health and  Environmental  Assessment.  Environmental Criteria  and
Assessment Office, Cincinnati,  OH.
Ametryn
C1ba-Ge1gy.   1961.
MRID No. 00034843.
Confidential  Business  Information;  unpublished  study.
U.S.  EPA.   1984.   Health  and  Environmental  Effects  Profile  for  Ametryn.
Prepared by the Office of  Health  and  Environmental  Assessment, Environmental
Criteria  and  Assessment  Office.   Cincinnati.  OH  for  the  Office  of  Solid
Waste, Washington. DC.

U.S.  EPA.   1990.   Integrated   Risk   Information  System  (IRIS).    Online.
Office  of  Health and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office. Cincinnati,  OH.

l-Amlno-2-naphtol and l-Amlno-2-naphtol hydrochlorlde
U.S.  EPA.   1986.  Health  and  Environmental  Effects Profile  for  l-Am1no-2-
naphtol  and  l-Amlno-2-naphtol  hydrochlorlde.   Prepared  by  the  Office  of
Health  and  Environmental  Assessment,  Environmental  Criteria  and  Assessment
Office. Cincinnati,  OH  for the  Office  of Solid Waste. Washington. DC.

m-Amlnophenol
Re, T.A., R.F.  Loehr,  S.C. Rodriguez,  et  al.  1984.   Results of  teratogen-
1c1ty   testing   of   m-amlnophenol  In  Sprague-Dawley   rats.    Fund.   Appl.
Toxlcol.  4: 98-104.
0121h
               D-5
07/24/90

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U.S.  EPA.   1985.    Health
phenols.   Prepared  by  the
Environmental Criteria  and
of Solid Waste,  Washington,

o-Amlnophenol
U.S.  EPA.   1985.    Health
phenols.   Prepared  by  the
Environmental Criteria  and
of Solid Waste,  Washington.

p-Amlnophenol
U.S.  EPA.   1985.    Health
phenols.   Prepared  by  the
Environmental Criteria  and
of Solid Waste,  Washington,
 and  Environmental   Effects   Profile   for  Amlno-
 Offlce  of  Health and  Environmental   Assessment,
Assessment Office, Cincinnati,  OH for the Office
DC.
 and  Environmental   Effects   Profile   for  Amlno-
 Offlce  of  Health and  Environmental  Assessment,
Assessment Office. Cincinnati,  OH for the Office
DC.
 and  Environmental   Effects   Profile   for  Amlno-
 Offlce  of  Health and  Environmental  Assessment,
Assessment Office, Cincinnati,  OH for the Office
DC.
4-Am1nopyr1d1ne
Kohn, F.E.  1968.   Four-week  Subacute Oral Toxlclty of  Compound  1861  Hydro-
chloride  --  Albino  Rats.    (Unpublished   study).   Prepared  by  Industrial
Blotest  Laboratories,  Inc.  under  224-12.   Submitted  by  Phillips  Petroleum
Co.. Bartlesvllle. OK.  CDL: 229844-E.  (Cited In U.S.  EPA. 1980)

U.S.  EPA.   1980.   4  Amlnopyrldlne.   Avltrol  Pesticide  Registration  Stan-
dard.  OPTS, U.S. EPA, Washington, DC. NTIS PB84-209907.

U.S. EPA.   1989.  Health and  Environmental  Effects  Document for  4-Am1nopyr1-
dlne.   Prepared  by  the  Office  of  Health  and  Environmental  Assessment,
Environmental  Criteria  and  Assessment Office, Cincinnati,  OH  for  the  Office
of Solid Waste and Emergency Response, Washington, DC.

Ammonia
Campbell, C.L., R.K. Dawes, S. Deolalkar and  M.C.  MerrUt.  1958.   Effect of
certain  chemicals  In  water  on the  flavor  of  brewed coffee.   Food  Res.   23:
575-579.  (Cited 1n U.S. EPA,  1981)

Carson,  B.L.,  C.M.  Beall.  H.V.  Ellis.  Ill and L.H. Baker.   1981.   Ammonia
Health Effects.  Prepared by. Midwest  Research  Institute for Office  of  Mobile
Source  Air  Pollution  Control, Emission  Control  Technology  Division.  U.S.
EPA, Ann Arbor, MI.   EPA 460/3-81-027.

U.S.  EPA.   1981.   Ambient  Water  Quality   Criterion  for  the Protection  of
Human Health:  Ammonia.   Prepared  by  the Office of Health and Environmental
Assessment,  Environmental Criteria and Assessment  Office,  Cincinnati,  OH for
the Office of  Water  Regulations and  Standards, Washington, DC.

U.S. EPA.   1987.   Health Effects  Assessment  for  Ammonia.  Prepared  by the
Office  of  Health and  Environmental   Assessment.  Environmental Criteria and
Assessment  Office,  Cincinnati,  OH for the  Office of Emergency and  Remedial
Response, Washington,  DC.
WHO (World Health Organization).  1986.
Ammonia.  WHO, Geneva,  Switzerland.
              Environmental Health Criteria.  54.
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Anthracene
U.S.  EPA.   1987.  Health  and Environmental  Effects  Profile for Anthracene.
Prepared by  the Office of Health and Environmental Assessment. Environmental
Criteria and  Assessment  Office,  Cincinnati, OH for the Office of Solid Waste
and Emergency Response, Washington, DC.

U.S.  EPA.   1989.   Subchronic  toxicity  in  mice with  anthracene.   Final
Report.   Hazelton Laboratories  America,  Inc.   Prepared  for the  Office of
Solid Waste. Washington. DC.
Antimony and Compounds
ASARCO,  Inc.   1980.  TSCA  8(e)  submission  8EHQ-0580-0342.
antimony trioxide.  OTS, U.S. EPA, Washington, DC.
                                   Bio/tox  data on
Schroeder,  H.A.,  M. Kitchener  and  A.P.  Nason.   1970.   Zirconium, nioblium.
antimony and lead in rats: Life time studies.  J. Nutr.  100: 59-69.

U.S.  EPA.   1985.    Health  and  Environmental  Effects  Profile  for Antimony
Oxides.   Prepared  by   the  Office  of Health  and  Environmental  Assessment,
Environmental  Criteria  and  Assessment Office, Cincinnati,  OH  for the Office
of Solid Waste and Emergency Response, Washington, DC.

U.S.  EPA.   1987.    Health  Effects  Assessment  for  Antimony  and Compounds.
Prepared by  the  Office  of Health and Environmental Assessment, Environmental
Criteria  and Assessment Office,  Cincinnati,  OH  for  the  Office of Emergency
and Remedial Response,  Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health   and  Environmental  Assessment,  EnvironmentalCriteria  and
Assessment Office, Cincinnati, OH.

Watt,  W.D.    1980.   Chronic  inhalation  toxicity of  antimony  trioxide  and
validation  of  the TLV.   Progress report  —  Summary of  results.  TSCA 8(e)
submission  8#HQ-0980-0342.    Study  submitted  by  ASARCO.   Inc..  New  York.
Microfiche No. OTS0204846.

Watt,  W.D.    1981.    FYI  submission TY-OTS-00081  0121  regarding  pathology
report  on  rat  inhalation   study  on  antimony  trioxide.   OTS,  U.S.  EPA,
Washington.  DC.  (Cited in U.S. EPA, 1985)

Watt, W.D.   1983.   Chronic  inhalation toxicity of antimony trioxide: Valida-
tion  of  the threshold  limit  value.   Diss. Abstr. Int. B  1983.  44(3): 739-
740.

Aramite
Oser,  B.L.  and M.  Oser.
ethyl  sulfite  (aramite).
4: 70-88.
1962.  2-(p-tert-butylphenoxy)isopropyl  2-chloro-
 II.  Carcinogenicity.   Toxicol.  Appl.  Pharmacol.
Popper, H., S.S.  Sternberg,  B.L.  Oser and M.  Oser.   1960.
effect of aramite in rats.  Cancer.   13(5): 1035-1046.
                                  The carcinogenic
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U.S.  EPA.   1989.   Health  and  Environmental  Effects  Document  for  AramHe.
Prepared by the  Office  of  Health  and Environmental Assessment, Environmental
Criteria and Assessment Office, Cincinnati,  OH for the Office of Solid Waste
and Emergency Response, Washington, DC.

Arsenic
Tseng,  W.P.   1977.  Effects  and  Dose-response relationships  of  skin cancer
and blackfoot disease with arsenic.  Environ. Health Perspect.  19: 109-119.

U.S.  EPA.   1984.  Health  Effects Assessment  for  Arsenic.  Prepared  by  the
Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office,  Cincinnati,  OH for  the  Office of  Emergency  and  Remedial
Response, Washington, DC.

Atrazlne
C1ba-Ge1gy  Corporation.    1987.   Confidential  Business  Information;  unpub-
lished study.   MRID No. 40431303.

U.S.  EPA.   1984.   Health  and  Environmental  Effects  Profile  for  Atrazlne.
Prepared by the  Office  of  Health  and Environmental Assessment, Environmental
Criteria  and  Assessment  Office,   Cincinnati,  OH  for  the  Office of  Solid
Waste, Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

Barium
Perry, H.M., S.J.  Kopp, M.W.  Erlanger  and  E.F. Perry.   1983.  Cardiovascular
effects of  chronic barium 1ngest1on:  In.: Trace  Substances In Environmental
Health, XVII, D.D.  Hemphlll,  Ed.   Proc. Univ.  Missouri's  17th Ann.  Conf. on
Trace  Substances  In  Environmental  Health.   University  of Missouri  Press,
Columbia, MO.

Tarasenko, M.. 0.  Promln  and  A. Sllayev.  1977.   Barium compounds as Indus-
trial poisons  (an experimental  study).  J.  Hyg.  Epldem.  Mlcroblol.  Immunol.
21: 361.

U.S.  EPA.   1984.   Health  Effects Assessment  for Barium.   Prepared  by  the
Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office,  Cincinnati,  OH for  the  Office of  Emergency  and  Remedial
Response, Washington, DC.   EPA/540/1-86-021.

U.S. EPA.  1985.   Drinking  Water  Criteria Document for  Barium.   Prepared by
the  Office  of Health  and  Environmental  Assessment,   Environmental  Criteria
and Assessment  Office,  Cincinnati,  OH for  the  Office of  Drinking  Water,  6
shlngton,  DC.    External  Review  Draft.   Final  Draft  (on Public  Comment).
NTIS PB 86-118031/AS.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office. Cincinnati, OH.
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Barium cyanide
Perry. H.M., E.F. Perry, M.N.  Erlanger  and  S.J.  Kopp.  1983.  Cardiovascular
effects  of chronic  barium  Ingestlon.   IN:   Proc.   17th  Ann.  Conf.   Trace
Substances  In  Environmental  Health,  Vol. 17.  University  of Missouri  Press,
Columbia, MO.  p. 155-164.
U.S. EPA.   1990.
of   Health  and
Assessment Office,
Integrated Risk Information
Environmental   Assessment.
Cincinnati,  OH.
System (IRIS).
 Environmental
Online. Office
 Criteria   and
BenefIn
Ell  Lilly  and  Co.   1972.
study.  MRID No. 00037678.
           Confidential  Business  Information;  unpublished
U.S.  EPA.    1984.   Health  and  Environmental  Effects  Profile  for  Benefln.
Prepared by  the  Office  of  Health and  Environmental Assessment, Environmental
Criteria  and Assessment  Office,  Cincinnati,  OH  for  the  Office of  Solid
Waste. Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk   Information  System  (IRIS).   Online.
Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

Benzal chloride
U.S.  EPA.    1985.   Health  and   Environmental  Effects  Profile   for  Benzal
Chloride.   Prepared  by  the  Office of  Health  and Environmental  Assessment,
Environmental Criteria  and Assessment Office.  Cincinnati,  OH  for  the Office
of Solid Waste.  Washington. DC.

Benzaldehyde
Kluwe, W.M., C.A.  Montgomery,  H.D.  Giles and J.D. Prejeau.  1983.  Encepha-
lopathy  1n  rats  and  nephropathy  In  rats  and  mice  after subchronlc  oral
exposure to benzaldehyde.  Food Chem.  Toxlcol.   21: 245-250.

U.S.  EPA.    1985.   Health  and  Environmental   Effects  Profile  for  Benzal-
dehyde.   Prepared by  the  Office  of  Health  and  Environmental  Assessment,
Environmental Criteria  and Assessment Office.  Cincinnati.  OH  for  the Office
of Solid Waste and Emergency Response, Washington,  DC.

U.S. EPA.  1990   Integrated  Risk  Information System  (IRIS).  Online.   Office
of   Health  and   Environmental   Assessment,   Environmental  Criteria   and
Assessment Office. Cincinnati. OH.

Benzaldehyde cyanohydrln
U.S.   EPA.   1988.    Health   and   Environmental   Effects   Document   for
CyanohydMns.    Prepared   by  the  Office  of   Health   and   Environmental
Assessment, Environmental  Criteria  and Assessment  Office.  Cincinnati, OH  for
the Office of Solid Waste and Emergency Response,  Washington, DC.

Benz1d1ne
Llttlefleld. N.A.,  C.J.  Nelson  and  C.H.  Futh.   1983.   Benzldlne  dlhydro-
chloMde:  lexicological  assessments  1n mice  during  chronic  exposure.   J.
Toxlcol. Environ. Health.  12: 671-68.
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U.S.  EPA.   1987.   Health Effects Assessment  for  Benzldlne.   Prepared by the
Office  of  Health  and Environmental  Assessment,  Environmental  Criteria and
Assessment  Office,  Cincinnati.  OH for  the  Office of  Emergency  and Remedial
Response, Washington. DC.

U.S.  EPA.   1990.    Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health  and Environmental  Assessment,  Environmental  Criteria and
Assessment Office, Cincinnati, OH.

Benzole acid
FASEB  (Federation of  American  Societies for Experimental  Biology).    1973.
Evaluation of the  Health  Aspects  of  Benzole  Acid and Sodium Benzoate as Food
Ingredients.  Report  No. SCOGS-7 PB-223 837/6.  p. 17.

U.S.  EPA.    1987.   Health  and  Environmental Effects  Document  for  Benzole
Add.   Prepared  by  the  Office  of   Health  and  Environmental  Assessment,
Environmental Criteria  and Assessment Office, Cincinnati, OH  for the Office
of Emergency and Remedial Response, Washington, DC.

U.S.  EPA.   1990.    Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health  and Environmental  Assessment,  Environmental  Criteria and
Assessment Office, Cincinnati, OH.

Benzyl Alcohol
NTP  (National  Toxicology Program).   1988.    Toxicology and  carclnogenesls
studies of  benzyl  alcohol  (CAS No. 100-51-6)  In  F344/N rats  and B6C3F1 mice
(gdvage studies).  NTP Technical Report, NTP TR 343.   p. 1-161.

U.S.  EPA.    1989.   Health  and  Environmental  Effects  Document for  Benzyl
Alcohol.   Prepared by  the Office  of  Health and Environmental  Assessment.
Environmental Criteria  and Assessment Office, Cincinnati, OH  for the Office
of Solid Waste and Emergency Response, Washington, DC.

Beryllium
Schroeder, H.A. and H.  MHchner.   1975.  Life-time studies  In rats:  Effects
of aluminum, barium, beryllium and tungsten.   J.  Nutr.  105:  421-427.

U.S. EPA.   1987.   Health  Effects Assessment  for Beryllium.   Prepared  by the
Office  of  Health  and Environmental  Assessment,  Environmental  Criteria and
Assessment Office,  Cincinnati,  OH for  the  Office of  Emergency  and Remedial
Response, Washington,  DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).    Online.
Office  of  Health  and Environmental  Assessment,  Environmental  Criteria and
Assessment Office, Cincinnati. OH.
l.l'-Blphenvl
Ambrose, A.M., A.N.  Booth,  f.  De Eds and A.G.  Cos,  Jr.
leal study of blphenyl, a vltrous funglstat.  Food Res.
                      1960.  A toxlcolog-
                     25: 328-336.
U.S.  EPA.    1984.   Health  and  Environmental  Effects   Profile  for  1,1-BI-
phenyl.   Prepared  by  the  Office  of  Health  and Environmental  Assessment,
Environmental Criteria and  Assessment  Office, Cincinnati, OH  for  the Office
of Solid Waste,  Washington,  DC.
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U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

Bis (2-ch1oro-1sopropy1) ether
MltsumoM,  K.,  T.  Usul,  K.  Takahash!  and  Y.  Shlrasu.   1979.   Twenty-four
month chronic toxlclty  studies  of  dlchlorodllsopropyl  ether  In mice.  Nippon
NoYaku Gakkalshl.  4(3): 323-335.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office. Cincinnati. OH.
B1s(2-ethylhexyl) phthalate
Carpenter, C.P., C.S.  Well  and H.F. Smyth.
d1(2-ethylhexyl) phthalate  for  rats,  guinea
Occ. Med.  8: 219-226.
          1953.   Chronic
         pigs and  dogs.
oral toxlclty of
 Arch.  Ind. Hyg.
U.S.  EPA.   1987.   Health  Effects  Assessment  for  Selected Phthallc  Add
Esters.   Prepared  by  the  Office of  Health  and  Environmental  Assessment,
Environmental Criteria and  Assessment  Office, Cincinnati, OH for  the Office
of Emergency and Remedial Response, Washington, DC.

U.S.  EPA.   1990.    Integrated  Risk  Information  System  (IRIS).   Online.
Office  of Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office.  Cincinnati. OH.

Blsphenol A
NTP  (National  Toxicology Program).  1982.   CarcTnogenesIs Bloassay  of  Bls-
phenol  A  In F344  rats  and B6C3F1 mice  (feed study)  NTP Tech  Rep  Ser.  No.
80-35 NTIS PB 84-1555308 p.192.

U.S.  EPA.   1984.   Reproduction and  ninety-day oral  toxlclty study  In  rats
U.S. EPA/OPTS Public  Files Flche No.  OTS0509954.

U.S.  EPA.   1988.   Health  and Environmental  Effects  Document  for  Blsphenol
A.  Prepared by the  Office of Health and  Environmental  Assessment,  Environ-
mental  Criteria  and  Assessment   Office,  Cincinnati,   OH for  the Office  of
Solid Waste and Emergency Response, Washington, DC.

U.S.  EPA.   1990.    Integrated  Risk  Information  System  (IRIS).   Online.
Office  of Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office,  Cincinnati, OH.

Boron
U.S.  EPA.   1987.  Health Effects  Assessment for  Boron.   Prepared by  the
Office  of Health  and  Environmental  Assessment.  Environmental  Criteria  and
Assessment Office.  Cincinnati,  OH for  the  Office of  Emergency  and  Remedial
Response, Washington.  DC.

Weir,  R.J.,  Jr.  and  R.S.  Fisher.  1972.   Toxlcologlc  studies  on borax  and
boric acid.  Toxlcol.  Appl.  Pharmacol.   23(3): 351-364.
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Bromlnated d1benzo-p-d1ox1ns and Dlbenzofurans
U.S.  EPA.   1985a.  Health  and Environmental Effects  Profile for Bromlnated
Dlbenzofurans.   Prepared  by the  Office of  Health  and Environmental Assess-
ment,  Environmental  Criteria  and  Assessment Office,  Cincinnati,  OH for the
Office of Solid Waste and Emergency Response. Washington. DC.

U.S.  EPA.   1985b.  Health  and Environmental Effects  Profile for Bromlnated
D1benzo-p-d1ox1ns.   Prepared  by  the  Office  of   Health  and  Environmental
Assessment, Environmental Criteria  and  Assessment  Office, Cincinnati, OH for
the Office of Solid Waste and  Emergency Response, Washington, DC.

U.S.  EPA.   1986.   Health  and  Environmental Effects  Profile for Bromlnated
D1benzo-p-d1ox1ns  and  Dlbenzofurans.    Prepared  by  the Office  of Health and
Environmental  Assessment,  Environmental  Criteria  and  Assessment  Office,
Cincinnati,  OH  for  the   Office  of  Solid   Waste  and   Emergency   Response,
Washington, DC.

Bromoacetone
U.S.  EPA.   1986.   Health   and  Environmental   Effects   Profile   for  Bromo-
acetone.   Prepared by  the  Office  of  Health and  Environmental  Assessment,
Environmental Criteria  and  Assessment Office, Cincinnati,  OH for the Office
of Solid Waste and Emergency Response, Washington, DC.

Bromochloroethanes
U.S.  EPA.   1985.   Health  and  Environmental  Effects  Profile for  Bromochloro-
ethanes.   Prepared by  the  Office  of  Health and  Environmental  Assessment,
Environmental Criteria  and  Assessment Office, Cincinnati.  OH for the Office
of Solid Waste and Emergency Response. Washington, DC.

Bromodlchloromethane
NTP  (National Toxicology  Program).   1986.   Toxicology  and Carclnogenesls
Studies  of  Bromodlchloromethane  In  F344/N  Rats  and B6C3F1  Mice (Gavage
Studies).  NTP Tech. Report, Ser. No.  321, NIH Publ. No. 87-2537.

U.S.  EPA.   1985.   Health  and  Environmental  Effects  Profile for  Bromochloro-
methanes.   Prepared  by the  Office of  Health and  Environmental  Assessment,
Environmental Criteria  and  Assessment Office, Cincinnati,  OH for the Office
of Solid Waste and Emergency Response, Washington. DC.

U.S.  EPA.   1987.   Health  Effects  Assessment  for  Trlhalogenated  Methanes.
Prepared by the Office  of Health and  Environmental  Assessment, Environmental
Criteria and  Assessment Office, Cincinnati,   OH  for the  Office  of Emergency
and Remedial Response,  Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk   Information  System  (IRIS).   Online.
Office of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati,  OH.

Bromoform
NTP   (National   Toxicology   Program).    1988.    Technical   Report   on   the
toxicology and carclnogenesls  studies of  trlhalomethane  (bromoform)  (CAS No.
75-25-2)  1n F344  rats  and  B6C3F1 mice  (gavage studies).  Board Draft.
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U.S.  EPA.   1987.   Health  Effects  Assessment  for  TMhalogenated  Methanes.
Prepared  by  the  Office  of  Health and  Environmental Assessment, Environmental
Criteria  and  Assessment Office, Cincinnati,  OH for the  Office  of  Emergency
and Remedial Response, Washington, DC.

U.S.  EPA.   1989.  Health  and  Environmental Effects Document  for Bromoform.
Prepared  by  the  Office  of  Health and  Environmental Assessment, Environmental
Criteria and Assessment Office,  Cincinnati.  OH  for the Office of Solid Waste
and Emergency Response, Washington,  DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).    Online.
Office  of Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati. OH.
Bromomethane
Danse,  L.H..  F.L.  van  Velsen   and  C.A.  vander  Heljden.
bromide:  Carcinogenic  effects  In  the  rat  forestomach.
Pharmacol.  72: 262-271.
                                                   1984.   Methyl
                                                  Toxlcol.  Appl.
Russo,   J.M..
Neurobehavloral
the rabbit.  J.
    W.K.   Anger,   J.V.  Setzer   and  W.S.   Brlghtwell.    1984.
    assessment  of chronic  low-level  methyl  bromide  exposure In
    Toxlcol.  Environ. Health.  14: 247-255.
U.S.  EPA.   1986.   Health  and   Environmental   Effects   Profile  for  Methyl
Bromide.   Prepared  by  the  Office  of  Health  and  Environmental  Assessment,
Environmental Criteria  and Assessment Office.  Cincinnati.  OH  for  the Office
of Solid Waste and Emergency Response. Washington. DC.

U.S.  EPA.   1987.   Health  Effects  Assessment for  Bromomethane.   Prepared by
the  Office of  Health  and  Environmental  Assessment.  Environmental  Criteria
and  Assessment  Office,   Cincinnati.  OH  for  the  Office  of  Emergency  and
Remedial Response, Washington. DC.
U.S.  EPA.
Office   of
Cincinnati,
 1990.
 Health
OH.
Integrated  Risk  Information  System  (IRIS).   Online.
and   Environmental   Criteria  and   Assessment   Office.
4-Bromophenyl phenyl ether
U.S. EPA.  1986.  Health  and  Environmental  Effects  Profile for 4-Bromophenyl
Phenyl  Ether.   Prepared by  the  Office of  Health and  Environmental  Assess-
ment,  Environmental  Criteria and Assessment  Office, Cincinnati,  OH  for the
Office of Solid Waste and Emergency Response,  Washington, DC.

Bromophos
Leuschner,  P.,  A.  Leuschner  and E.  Poppe.    1967.   Chronlscher  Reproduk-
tlonsversuch  uber  3 Generatlonen  an Wlstar-Ratten  be1  fortdauernder  Vera-
brelchung  von  Bromophos.   Report  C.H.   Boehrlnger  Sohn.   (Unpublished).
(Cited 1n U.S. EPA.  1986).

U.S.  EPA.   1986.    Health  and Environmental  Effects Profile  for  Bromophos.
Prepared by  the Office  of  Health  and Environmental  Assessment, Environmental
Criteria and Assessment Office, Cincinnati, OH  for  the  Office of Solid Waste
and Emergency Response. Washington,  DC.
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BromoxynH
Union  Carbide  Agriculture  Products.  Inc.   1982.   Confidential  Business
Information; unpublished study.  MRID No. 00096521.

U.S.  EPA.   1984.   Health  and  Environmental Effects Profile  for  Bromoxynll.
Prepared by the Office  of  Health  and Environmental Assessment, Environmental
Criteria  and  Assessment  Office.  Cincinnati,  OH  for  the  Office of  Solid
Waste. Washington. DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health  and  Environmental  Assessment.  Environmental Criteria  and
Assessment Office. Cincinnati.  OH.

Bromoxynll octanoate
Union  Carbide  Agriculture  Products,  Inc.   1982.   Confidential  Business
Information; unpublished study.  MRID No. 00096521.

U.S.  EPA.   1984.   Health  and  Environmental  Effects Profile  for  Bromoxynll
Octanoate.  Prepared  by the Office  of  Health and  Environmental  Assessment,
Environmental  Criteria  and Assessment Office,  Cincinnati,  OH  for  the Office
of Solid Waste,  Washington. DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health  and  Environmental  Assessment.  Environmental Criteria  and
Assessment Office, Cincinnati,  OH.

Busan-77
U.S.  EPA.   1984.   Health  and  Environmental  Effects  Profile  for  Busan-77.
Prepared by the Office  of  Health  and Environmental Assessment. Environmental
Criteria  and  Assessment  Office.  Cincinnati.  OH  for  the  Office of  Solid
Waste. Washington, DC.

Busan-90
U.S.  EPA.   1984.   Health  and  Environmental  Effects  Profile  for  Busan-90.
Prepared by the Office  of  Health  and Environmental Assessment, Environmental
Criteria  and  Assessment  Office,  Cincinnati,  OH  for  the  Office of  Solid
Waste, Washington, DC.

1-Butanol
U.S.  EPA.   1986.   Butanol:  Rat  oral subchronlc  toxldty  study.   Office  of
Solid Waste, Washington, DC.

U.S.  EPA.   1989.   Health  and  Environmental Effects Document  for  1-Butanol.
Prepared by the Office  of  Health  and Environmental Assessment, Environmental
Criteria and Assessment Office, Cincinnati,  OH for  the  Office of  Solid Waste
and Emergency  Response,  Washington, DC.

U.S.  EPA. 1990.    Integrated  Risk  Information System (IRIS).  Online.   Office
of   Health   and   Environmental   Assessment.   Environmental   Criteria   and
Assessment Office. Cincinnati.  OH.

Butylate
Stauffer Chemical   Company.   1987.   Confidential  Business  Information; unpub-
lished study.  MIRD No.  40289101.
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U.S.  EPA.   1984.   Health and  Environmental  Effects  Profile  for  Butylate.
Prepared by the  Office  of  Health  and  Environmental  Assessment, Environmental
Criteria  and  Assessment  Office,  Cincinnati,  OH  for  the  Office  of  Solid
Waste. Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).    Online.
Office  of  Health  and  Environmental  Assessment.  Environmental  Criteria  and
Assessment Office. Cincinnati, OH.

Butyl benzyl phthalate
NTP  (National  Toxicology  Program).    1985.   Project  No.  12307-02,  -03.
Hazexlton Laboratories America, Inc; unpublished study.

U.S. EPA.   1986.   Drinking Water  Criteria Document for  Phthallc  Acid Esters
(PAE)s.   Prepared by  the  Office  of Health  and Environmental  Assessment,
Environmental  Criteria  and Assessment Office, Cincinnati,  OH  for  the Office
of Drinking Water, Washington. DC.  External Review Draft.

U.S.  EPA.   1987.    Health  Effects  Assessment  for   Selected   Phthallc  Acid
Esters.   Prepared by  the  Office  of Health  and Environmental  Assessment.
Environmental  Criteria  and Assessment Office, Cincinnati,  OH  for  the Office
of Emergency and Remedial Response, Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).    Online.
Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

t-Butylch!or1de
U.S. EPA.   1988.   Health and Environmental  Effects Document  for Monochloro-
butanes.   Prepared  by  the Office  of Health and Environmental  Assessment.
Environmental  Criteria  and Assessment Office, Cincinnati,  OH  for  the Office
of Solid Waste and Emergency Response, Washington, DC.

Butyrolactone. gamma
U.S. EPA.   1984.   Health and  Environmental  Effects  Profile for Gamma-butyro-
lactone.   Prepared  by  the Office  of Health and Environmental  Assessment,
Environmental  Criteria  and Assessment Office. Cincinnati,  OH  for  the Office
of Solid Waste,  Washington, DC.

Cacodyllc Acid
Nees, P.O.  1968.  Report  on  cacodyllc add  toxldty  to animals.   Wisconsin
Alumni Res. Found.  EPA Pesticide Petition No. OF0911.

U.S.  EPA.   1989.  Health  and Environmental  Effects  Document  for  Cacodyllc
Acid.   Prepared  by   the  Office   of   Health  and  Environmental  Assessment,
Environmental  Criteria  and Assessment Office, Cincinnati,  OH  for  the Office
of Solid Waste and Emergency Response, Washington, DC.

Cadmium
U.S.  EPA.   1980.    Ambient  Water  Quality  Criteria   Document for  Cadmium.
Prepared by the  Office  of  Health  and  Environmental  Assessment, Environmental
Criteria  and  Assessment  Office,  Cincinnati,  OH  for  the  Office  of  Water
Regulations  and  Standards,   Washington.   DC.   EPA-440/5-80-025.    NTIS  PB
81-117368.
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U.S.  EPA.   1984.  Health  Effects Assessment  for  Cadmium.   Prepared  by the
Office  of  Health  and Environmental  Assessment,  Environmental  Criteria and
Assessment Office.  Cincinnati,  OH for  the Office of  Emergency and Remedial
Response, Washington, DC.

U.S.  EPA.   1990.    Integrated  Risk  Information  System   (IRIS).   Online.
Office  of  Health  and Environmental  Assessment,  Environmental  Criteria and
Assessment Office. Cincinnati, OH.

Calcium cyanide
Howard,  J.W.  and  R.F.   Hanzal.   1955.   Chronic  toxlclty  for rats  of  food
treated with hydrogen cyanide.  Agrlc. Food Chem.  3: 325-329.

Ph1lbr1ck. D.J.,  J.B. Hopkins.  D.C.  Hill. J.C. Alexander  and R.G. Thomson.
1979.   Effects  of  prolonged  cyanide  and thlocyanate  feeding In  rats.  J.
Toxlcol. Environ. Health.  5: 579-592.

U.S.  EPA.   1990.    Integrated  Risk  Information  System   (IRIS).   Online.
Office  of  Health  and Environmental  Assessment,  Envoronmental  Criteria and
Assessment Office, Cincinnati. OH.

Caprolactam
Powers,  W.J.J,  J.C.  Peckham,  K.H.  Sllno and  S.C.  Gad.   1984.   Effects  of
subchronlc  dietary  caprolactam  on   renal  function.   lt\:  Proc   Symp.  Ind.
approach  Chem  Risk  Assessment:  Caprolactam  Relat.  Compd.  Case  Study  77-96
Ind. Health Found., Pittsburgh,  PA.

Serota, D.G., A.M.  Hoberman  and S.C. Gad.  1984.   A three generation repro-
duction  study  with  caprolactam In  rats.   In: Proc  Symp  Ind  Approach  Chem
Risk  Assessment:  Caprolactam RElat  Compl.   Case  study  191-204  Ind.  Health
Found.  Pittsburgh, PA.

U.S.  EPA.    1988.    Health  and  Environmental  Effects  Document   for  Capro-
lactam.   Prepared by the  Office of Health  and Environmental  Assessment,
Environmental Criteria and  Assessment Office,  Cincinnati,  OH for the Office
of Solid Waste and Emergency Response, Washington, DC.

U.S.  EPA.   1990.   Integrated   Risk  Information  System   (IRIS).   Online.
Office  of  Health  and Environmental   Assessment,  Environmental Criteria and
Assessment Office, Cincinnati, OH.

Captafol
Ortho-Chevron Chemical  Company.   1985.   Confidential  Business Information;
unpublished study.  Accession No.  260671.

U.S.  EPA.   1984.   Health  and  Environmental   Effects  Profile  for  Captafol.
Prepared by the Office of Health  and Environmental  Assessment, Environmental
Criteria  and  Assessment  Office,   Cincinnati,  OH  for  the  Office of  Solid
Waste, Washington, DC.

U.S.  EPA.    1990.   Integrated   Risk  Information  System   (IRIS).   Online.
Office  of  Health  and  Environmental   Assessment,  Environmental Criteria and
Assessment Office, Cincinnati, OH.
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Captan
Chevron  Chemical  Company.   1982.  Confidential  Business Information; unpub-
lished study.  MRID No. 0012.

Stauffer Chemical  Company.   1982.   Confidential Business Information; unpub-
lished study.  MRID No. 00120315.

U.S.  EPA.    1984.   Health  and  Environmental  Effects  Profile  for  Captan.
Prepared by  the  Office of  Health and Environmental Assessment. Environmental
Criteria  and  Assessment  Office,  Cincinnati,  OH  for   the  Office of  Solid
Waste, Washington. DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System   (IRIS).   Online.
Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati. OH.
Carbaryl
Carpenter, C.P., C.W. Well,  P.E.  Polln,  et  al.   1961.
1-naphthayl-n-methylcarbamate (Sevln  Insecticide).   J.
30-39.
                                      Mammalian toxlclty of
                                      Agrlc.  Food Chem.  9:
U.S.  EPA.   1984.   Health and  Environmental  Effects  Profile  for  Carbaryl.
Prepared by the  Office  of Health  and Environmental Assessment, Environmental
Criteria  and   Assessment  Office,  Cincinnati,  OH  for  the  Office  of  Solid
Waste. Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System   (IRIS).    Online.
Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office. Cincinnati, OH.
Carbofuran
FMC  Corporation.
study.  Accession
  1983.   Confidential
No. 250740-250755.
Business  Information;  unpublished
U.S.  EPA.   1984.   Health  and  Environmental  Effects  Profile  for Carbofuran.
Prepared by the Office  of  Health  and  Environmental Assessment, Environmental
Criteria  and  Assessment  Office,  Cincinnati,   OH  for  the  Office  of  Solid
Waste, Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk   Information  System  (IRIS).    Online.
Office  of  Health and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati,  OH.

Carbon dlsulflde
Hardln,  B.D.,  G.P.  Bond,  M.R.  S1kor. F.D.  Andrew.  R.P.  Bellies  and  R.W.
Nlemelr.   1981.   Testing  of  selected work  place  chemicals  for teratogenlc
potential.  Scand. J. Work Environ. Health.  7(Suppl. 4): 66-75.

U.S.  EPA.   1990.   Integrated  Risk   Information  System  (IRIS).    Online.
Office  of  Health and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati.  OH.
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Carbon tetrachlorlde
Bruckner. J.V.. W.F. MacKenzle, S. Muralldhara,  et  al.   1986.   Oral toxlclty
of  carbon  tetrachlorlde:  Acute,  subacute  and  subchronlc  studies  In  rats.
Fund. Appl. Toxlcol.  6(1): 16-34.

U.S.  EPA.    1984.   Health  Effects   Assessment  for  Carbon  Tetrachlorlde.
Prepared by the Office of  Health  and  Environmental  Assessment, Environmental
Criteria and  Assessment  Office,  Cincinnati, OH  for the Office  of Emergency
and Remedial Response,  Washington. DC.
                   Integrated Risk  Information
                   Environmental   Assessment,
                   Cincinnati,  OH.
           System (IRIS):
            Environmental
Online.   Office
  Criteria   and
U.S. EPA.  1990.
of   Health   and
Assessment Office,

Chloral
Sanders, V.M., B.M. Kauffmann. K.L. White,  Jr.   1982.   Toxicology of chloral
hydrate In the mouse.   Environ. Health Perspect.  44: 146-173.

U.S.  EPA.   1988.   Health and  Environmental Effects  Document  for  Chloral.
Prepared by the  Office of  Health  and  Environmental  Assessment. Environmental
Criteria and Assessment Office, Cincinnati.  OH  for  the Office of Solid Waste
and Emergency Response. Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk   Information  System  (IRIS).   Online.
Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

Chlordane
verslcol Chemical Corp.  1983.  Ace. No.  252267  Available from EPA under FOI.

U.S. EPA.  1988.   Health  Effects  Assessment for  Chlordane.   Prepared  by  the
Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office,  Cincinnati,  OH for the  Office of  Emergency  and  Remedial
Response, Washington,  DC.

U.S.  EPA.    1990.   Integrated  Risk  Information System (IRIS).   Online.
Office  of  Health  and Environmental  Assessment.  Envlromental  Criteria  and
Assessment Office, Cincinnati, OH.

Chlorine cyanide
Howard,  J.W.  and  R.F.  Hanzal.   1955.  Chronic  toxlclty  for  rats  of  food
treated with hydrogen  cyanide.  Agrlc. Food Chem.  3: 325-329.

Phllbrlck, D.J..  O.B.  Hopkins, D.C.  H111,  J.C.  Alexander  and  R.G.  Thomson.
1979.   Effects  of  prolonged  cyanide   and  thlocyanate  feeding In rats.   J.
Toxlcol. Environ. Health.   5:   579-592.

U.S.  EPA.   1990.   Integrated  Risk   Information  System  (IRIS).   Online.
Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.
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 Chloroacetaldehyde
 U.S.  EPA.   1988.  Health and  Environmental  Effects  Document for Chloroacet-
 aldehyde.   Prepared by  the Office  of  Health  and  Environmental Assessment,
 Environmental  Criteria  and Assessment Office.  Cincinnati.  OH for the Office
 of  Solid Waste and Emergency Response, Washington. DC.

 Chloroacetlc Acid
 IRDC   (International  Research  and  Development  Corporation).   1982a.   Sub-
 chronic  oral  toxlclty  test with monochloroacetlc  acid In  rats.   National
 Toxicology Program. Bethesda, MD.  p. 1-101.

 U.S.  EPA.   1988.   Health  and Environmental  Effects Document  for  Chloroacetlc
 Add.   Prepared  by  the  Office  of  Health  and  Environmental  Assessment,
 Environmental  Criteria  and Assessment Office,  Cincinnati,  OH for the Office
 of  Solid Waste and Emergency Response, Washington, DC.

 2-Chloroanlllne
 U.S.  EPA.    1987.   Health  and  Environmental   Effects  Document  for  Chloro-
 anlUnes.   Prepared  by  the Office of  Health  and  Environmental Assessment,
 Environmental  Criteria  and Assessment Office,  Cincinnati,  OH for the Office
 of  Solid Waste and Emergency Response, Washington, DC.

 3-Chloroan111ne
 U.S.  EPA.    1987.   Health  and  Environmental   Effects  Document  for  Chloro-
 anlllnes.   Prepared  by  the Office of  Health  and  Environmental Assessment,
 Environmental  Criteria  and Assessment Office,  Cincinnati,  OH for the Office
 of  Solid Waste and Emergency Response, Washington, DC.

 4-Chloroanlllne
 NCI  (National  Cancer  Institute).   1979.    Bloassay  of  p-chloroanlllne  for
 possible carclnogenlclty.   NCI  Cardnogenesls Tech Rep.  Ser. No. 189.   NTIS
 PB295896.

 U.S.  EPA.    1987.   Health  and  Environmental   Effects  Document  for  Chloro-
 anlllnes.   Prepared  by  the Office of  Health  and  Environmental Assessment,
 Environmental  Criteria  and  Assessment Office,  Cincinnati,  OH for the Office
 of  Solid Waste and Emergency Response, Washington, DC.

 U.S.  EPA.    1990.   Integrated  Risk  Information  System  (IRIS).    Online.
 Office  of  Health  and  Environmental   Assessment,  Environmental  Criteria  and
 Assessment Office, Cincinnati,  OH.

 Chlorobenzene
 Dllley,  J.V.  1977.   Toxic  Evaluation  of  Inhaled  Chlorobenzene.   NIOSH,
 DHEW, Cincinnati, OH.   Contract 210-76-0126.  (Cited 1n U.S.  EPA, 1985)

 U.S. EPA.   1984.   Health  Effects Assessment for  Chlorobenzene.   Prepared  by
 the  Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria
and  Assessment  Office,  Cincinnati,  OH  for  the Office  of Emergency  and
Remedial Response, Washington,  DC.  EPA  540/1-86-040.

U.S.  EPA.    1985.   Health   Assessment  Document  for  Chlorinated  Benzenes.
Office  of  Health and  Environmental   Assessment,  Environmental  Criteria  and
Assessment  Office, Cincinnati,  OH.  EPA  600/8/84/015F.  NTIS PB85-150332.
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U.S.  EPA.    1989.   Updated  Health  Effects  Assessment  for  Chlorobenzene.
Prepared by  the Office of  Health  and  Environmental  Assessment, Environmental
Criteria and  Assessment  Office,  Cincinnati, OH  for the Office  of  Emergency
and Remedial Response, Washington, DC.

U.S.  EPA.    1990.   Integrated  Risk  Information  System  (IRIS).    Online.
Office  of  Health and  Environmental  Assessment,  Environmental  Criteria  and
Assessment  Office, Cincinnati, OH.

Chlorobenzllate
Clba-Gelgy  Corporation.   1984.  MRID No. 00144691.

U.S.  EPA.    1990.   Integrated  Risk  Information  System  (IRIS).    Online.
Office  of  Health and  Environmental  Assessment.  Environmental  Criteria  and
Assessment  Office, Cincinnati, OH.

p-Chlorobenzolc acid
Kleckebusch, W., M. Grlem  and  K.  Lang.   1960.   The  tolerablllty of  p-chloro-
benzolc  add.   Arznelml  Hel-Forsch.    10:  999-10001.   (In German;  English
translation)

U.S.  EPA.   1987.   Health  and Environmental  Effects  Document  for  p-Chloro-
benzolc  Acid.   Prepared  by  the  Office of  Health and  Environmental  Assess-
ment,  Environmental  Criteria and Assessment  Office,  Cincinnati, OH  for  the
Office of Solid Waste and Emergence Response, Washington.  DC.

4-Chlorobenzotrlfluoride
Hooker  Chemical  Corp.  1981.  Modified 90-day gavage and  reproduction study
In  rats PCBTF.   Conducted  by Elars  Bloresearch  Laboratories, Inc.,  Fort
Collins. CO.  U.S. EPA/OPTS Public Files.   Microfiche #OTS0508148.

U.S.  EPA.   1988.   Health  and Environmental  Effects  Document  for  4-Chloro-
benzotrlfluorlde.   Prepared  by  the  Office  of  Health   and  Environmental
Assessment, Environmental  Criteria  and  Assessment Office,  Cincinnati, OH  for
the Office  of Solid Waste and Emergency Response, Washington, DC.

2-Chloro-l,3-butadlene
Du  Pont  de  Nemours  and  Company,  Inc.   1985.  2-Year Inhalation Carclnogen-
Iclty Study  of  Chloroprene In Rats.  E.I. Du Pont  De Nemours  and Co., Inc..
Wilmington, DE.

U.S.  EPA.   1989.   Health  and Environmental  Effects  Document  for  2-Chloro-
1,3-butadlene  (Chloroprene).   Prepared  by the Office of Health  and Environ-
mental Assessment,  Environmental  Criteria and  Assessment  Office, Cincinnati,
OH for the  Office of Solid Waste and Emergency Response, Washington, DC.

1-Chlorobutane
NTP  (National   Toxicology  Program).   1986.   Toxicology  and  Cardnogenesls
studies  of  n-butyl  chloride  1n  F344/N   rats  and   B6C3F1   mice  (gavage
studies).  CAS No. 109-69-3.  NTP-TR-312.   198 p.

U.S.  EPA.   1988.   Health and Environmental Effects Document  for Monochloro-
butanes.   Prepared  by the  Office  of  Health  and  Environmental  Assessment,
Environmental Criteria and Assessment Office,  Cincinnati,  OH  for  the Office
of Solid Waste and Emergency Response, Washington, DC.


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2-Chlorobutane
U.S.  EPA.   1988.   Health and Environmental Effects  Document for Monochloro-
butanes.   Prepared by  the  Office  of  Health  and  Environmental  Assessment,
Environmental Criteria  and Assessment Office,  Cincinnati,  OH  for  the Office
of Solid Waste and Emergency Response, Washington. DC.

Chlorocyclopentadlene
U.S.  EPA.   1988.   Health and Environmental Effects  Document for Chlorinated
Cyclopentadlenes.   Prepared  by  the  Office  of  Health  and  Environmental
Assessment, Environmental  Criteria and  Assessment Office, Cincinnati, OH for
the Office of Solid Waste and Emergency Response, Washington, DC.

p-Chloro-m-cresol
Madsen, C., P.H. Andersen,  0. Meyer  and 6.  Wurtzen.  1986.  4-Chloroemethyl-
phenol:   Salmonella/mammallan-mlcrosome  mutagenlclty   test   and   subacute
toxlclty test In rats.  Bull. Environ. Contam.  Toxlcol.  37(5): 651-654.

U.S.  EPA.   1988.   Health and Environmental Effects  Document for p-Chloro-m-
cresol.   Prepared  by  the  Office of  Health  and  Environmental  Assessment,
Environmental Criteria  and Assessment Office,  Cincinnati,  OH  for  the Office
of Solid Waste and Emergency Response, Washington, DC.

Chloroform
Heywood, R., R.J.  Sortwe11,  P.R.B. Noel,  et al.   1979.  Safety evaluation of
toothpaste containing  chloroform.   III. Long-term study  In beagle  dogs.  J.
Environ. Pathol. Toxlcol.  p. 835-851.

U.S.   EPA.    1988.   Updated  Health   Effects   Assessment  for  Chloroform.
Prepared by the Office  of  Health  and Environmental Assessment, Environmental
Criteria and  Assessment  Office,  Cincinnati, OH  for the  Office of  Emergency
and Remedial Response, Washington, DC.

U.S.  EPA.   1990.    Integrated  Risk  Information  System   (IRIS).    Online.
Office  of  Health  and  Environmental   Assessment.  Environmental  Criteria and
Assessment Office,  Cincinnati, OH.

m-Chloronltrobenzene
U.S.  EPA.   1985.   Health and Environmental Effects  Profile for Chloronltro-
benzenes.   Prepared  by  the Office  of  Health  and  Environmental  Assessment,
Environmental Criteria  and Assessment Office,  Cincinnati,  OH  for  the Office
of Solid Waste and  Emergency Response, Washington, DC.

Chlorophenol. 3- and 4-
U.S.  EPA.   1987.   Health and Environmental Effects  Document for Chlorinated
Phenols.   Prepared by  the  Office  of  Health  and  Environmental  Assessment,
Environmental Criteria  and Assessment Office,  Cincinnati,  OH  for  the Office
of Solid Waste and  Emergency Response, Washington, DC.

2-Chlorophenol
Exon,  J.H.  and  L.D.  Koller.   1982.   Effects  of transplacental exposure to
chlorinated phenols.   Environ. Health Perspect.  46: 137-140.
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U.S.  EPA.   1987a.   Health Effects Assessment  for  2-Chlorophenol  and 2,4-DI-
chlorophenol.   Prepared  by  the  Office of  Health and  Environmental  Assess-
ment,  Environmental  Criteria and Assessment  Office, Cincinnati, OH  for  the
Office of Emergency and Remedial Response, Washington, DC.

U.S.  EPA.   1987b.  Health  and  Environmental  Effects  Document for Chlorinated
Phenols.   Prepared by  the  Office  of  Health  and Environmental  Assessment,
Environmental Criteria and Assessment Office, Cincinnati,  OH  for  the Office
of Solid Waste and Emergency Response, Washington. DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System   (IRIS).    Online.
Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office. Cincinnati,  OH.
2-Chloropropane
Gage, 3.C.   1970.
Icals.  Br. J. Ind.
The subacute
Hed.  27(1):
Inhalation
1-18.
toxlclty of 109  Industrial  chem-
U.S. EPA.  1987.  Health and  Environmental  Effects Document for 2-Chloropro-
pane.   Prepared  by  the   Office  of  Health  and  Environmental  Assessment,
Environmental Criteria  and Assessment  Office, Cincinnati,  OH  for  the Office
of Solid Waste and Emergency Response,  Washington. DC.
Chlorotoluenes. m- and p-
U.S.  EPA.    1985.   Health  and  Environmental
toluenes.   Prepared  by  the  Office of  Health
Environmental  Criteria  and  Assessment  Office.
of Solid Waste. Washington.  DC.
                            Effects  Profile  for  Chloro-
                            and  Environmental Assessment,
                            Cincinnati,  OH for the Office
o-Chlorotoluene
Gibson,  W.R.,   F.O.  Gossett.  G.R.  Koenlg  and  F.  Harroquln.
toxldty  of  dally  oral  doses  of o-chlorotoluene  In  the  rat.
Division, Lilly  Research  Laboratories.   Submitted to  Test Rules
Branch. Office of Toxic Substances. U.S. EPA. Washington, DC.
                                               1974.   The
                                               Toxicology
                                               Development
U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health and  Environmental  Assessment,  Environmental  Criteria  and
Assessment office, Cincinnati, OH.
Chlorpyrlfos
Dow Chemical Company.   1972.
study.  Accession No. 112118.
           Confidential Business Information; unpublished
U.S. EPA.   1984.   Health  and Environmental Effects  Profile for Chlorpyrlfos
and Chlorpyrlfos-methyl.  Prepared by the  Office  of  Health and Environmental
Assessment, Environmental  Criteria and Assessment  Office.  Cincinnati,  OH for
the Office of Solid Waste. Washington.  DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati. OH.
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ChlorpyrIfos-methyl
U.S. EPA.   1984.   Health and Environmental Effects  Profile  for  Chlorpyrlfos
and Chlorpyrlfos-methyl.  Prepared by  the  Office  of  Health and Environmental
Assessment, Environmental Criteria and  Assessment  Office.  Cincinnati,  OH for
the Office of Solid Waste. Washington,  DC.
Chlorthalonll
Diamond  Shamrock  Chemical  Company.   1970.   Confidential
tlon; unpublished study.  Accession No.  111253.
                        Business  Informa-
U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health and  Environmental Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

Chlorthlophos
Worthing, C.R.  and  S.B. Walker,  Ed.  1983.   The Pesticide Manual,  7th  ed.
British  Crop  Protection  Council,  The Lavenham Press  Ltd.,  Suffolk.  England.
p. 130.

U.S.  EPA.   1986.  Health  and Environmental  Effects  Profile  for  Chlorthlo-
phos.   Prepared  by   the  Office  of  Health  and  Environmental  Assessment.
Environmental Criteria and Assessment  Office, Cincinnati,  OH  for  the Office
of Solid Waste and Emergency Response,  Washington, DC.

Chromium (III)
Ivankovlc, S.  and R.  Preussman.   1975.   Absence  of  toxic  and carcinogenic
effects  after  administrations  of  high  doses of  chromic  oxide  pigment  In
subacute  and  long-term  feeding  experiments  In  rats.  Food Cosmet  Toxlcol.
13: 347-351.

U.S.   EPA.    1984.    Health  Effects  Assessment   for   Trlvalent   Chromium.
Prepared by the  Office of  Health  and Environmental Assessment, Environmental
Criteria and  Assessment  Office,  Cincinnati,  OH  for the  Office of Emergency
and Remedial  Response, Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System (IRIS).   Online.
Office  of  Health and  Environmental Assessment.  Environmental  Criteria  and
Assessment Office. Cincinnati, OH.

Chromium (VI)
MacKenzle, R.D.,  R.U.  Byerrum,  C.F. Decker  et al.   1958.   Chronic  toxlclty
studies.   II.  Hexavalent  and  trlvalent  chromium  administered 1n  drinking
water to rats.  Am.  Ned Assoc. Arch. Ind.  Health.  18: 232-234.

U.S.   EPA.   1984.    Health   Effects  Assessment  for  Hexavalent   Chromium.
Prepared by the  Office of  Health  and Environmental Assessment, Environmental
Criteria and  Assessment  Office,  Cincinnati,  OH  for the  Office of Emergency
and Remedial  Response, Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health and  Environmental Assessment.  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.
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 Chrysene
 U.S.  EPA.   1984.   Health  and  Environmental  Effects  Profile for  Chrysene.
 Prepared by the Office of Health and Environmental  Assessment,  Environmental
 Criteria and  Assessment  Office,  Cincinnati,  OH  for  the  Office  of  Solid
 Waste,  Washington,  DC.

 Copper
 U.S.  EPA.   1984.   Health Effects  Assessment  for  Copper.   Prepared  by  the
 Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
 Assessment  Office,  Cincinnati,  OH  for  the Office  of Emergency and Remedial
 Response, Washington,  DC.

 U.S.  EPA.   1987.   Drinking Water Criteria  Document for Copper.  Prepared  by
 the  Office  of  Health  and  Environmental Assessment,  Environmental Criteria
 and  Assessment Office, Cincinnati,  OH  for  the  Office  of  Drinking  Water,
 Washington,  DC.  External  Review Draft.

 Copper  cyanide
 U.S.  EPA.   1986.   90-Day  oral  toxldty  study  of  copper cyanide.  Office  of
 Solid Waste, Washington, DC.

 U.S.  EPA.   1990.    Integrated  Risk   Information   System  (IRIS).    Online.
 Office  of  Health  and  Environmental  Assessment, Environmental  Criteria  and
 Assessment  Office, Cincinnati, OH.

 m-Cresol
 Microbiological  Associates.    1986.   o.m.p-Cresol.   90-Day  oral   subchronlc
 toxlclty  studies   1n   rats.    Sponsored  by   the  Office  of  Solid  Waste,
 Washington,  DC.

 Toxldty   Research   Laboratories.     1987.    o.m.p-Cresol.     90-Day  oral
 subchronlc  neurotoxlclty study  1n  rats.   Sponsored  by the  Office of  Solid
 Waste,  Washington, DC.

 U.S.  EPA.   1984.   Health  Effects  Assessment  for  Cresols.   Prepared  by  the
 Office  of  Health  and  Environmental  Assessment, Environmental  Criteria and
 Assessment  Office,  Cincinnati,  OH for  the  Office  of  Emergency and Remedial
 Response, Washington, DC.

 U.S.  EPA.    1985.   Health  and  Environmental   Effects  Profile  for Cresols.
 Prepared by  the Office  of  Health and  Environmental Assessment, Environmental
 Criteria  and Assessment  Office,  Cincinnati,   OH   for  the  Office of  Solid
 Waste, Washington, DC.

 U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).    Online.
 Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria and
 Assessment Office, Cincinnati, OH.

 o-Cresol
Microbiological  Associates.   1986.   o.m.p-Cresol.   90-Day  oral  subchronlc
 toxldty  studies   In   rats.   Sponsored  by   the   Office  of  Solid  Waste,
Washington,  DC.
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Toxlclty   Research   Laboratories.    1987.    o.m.p-Cresol.    90-Day   oral
subchronlc  neurotoxlclty study  In  rats.   Sponsored  by the  Office of  Solid
Waste, Washington, DC.

U.S.  EPA.   1984.  Health  Effects Assessment  for Cresols.   Prepared  by  the
Office  of  Health  and Environmental  Assessment, Environmental  Criteria  and
Assessment  Office,  Cincinnati, OH for  the Office of  Emergency and Remedial
Response. Washington. DC.

U.S.  EPA.    1985.   Health  and  Environmental   Effects  Profile  for Cresols.
Prepared by  the  Office  of  Health and Environmental Assessment,  Environmental
Criteria  and  Assessment Office,  Cincinnati,   OH for  the  Office  of  Solid
Waste, Washington, DC.

U.S.  EPA.   1990.    Integrated  Risk  Information  System   (IRIS).    Online.
Office  of  Health  and Environmental  Assessment, Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

p-Cresol
Microbiological  Associates.   1986.   o.m.p-Cresol.   90-Day  oral   subchronlc
toxlclty  studies  In rats.   Sponsored  by   the  Office  of   Solid  Waste,
Washington, DC.

Toxlclty   Research   Laboratories.    1987.    o.m.p-Cresol.     90-Day   oral
subchronlc  neurotoxlclty study  In  rats.   Sponsored  by the  Office of  Solid
Waste, Washington, DC.

U.S.  EPA.   1984.  Health  Effects Assessment  for Cresols.   Prepared  by  the
Office  of  Health  and Environmental  Assessment, Environmental  Criteria  and
Assessment  Office, Cincinnati, OH for  the Office of  Emergency and Remedial
Response, Washington, DC.

U.S.  EPA.    1985.   Health  and  Environmental   Effects  Profile  for Cresols.
Prepared by  the  Office of  Health and Environmental Assessment,  Environmental
Criteria  and  Assessment Office,  Cincinnati,   OH for  the  Office  of  Solid
Waste, Washington, DC.

U.S.  EPA.    1990.    Integrated  Risk  Information  System  (IRIS).    Online.
Office  of  Health  and Environmental  Assessment, Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

Cumene
Monsanto Company.   1986.  One month study of  cumene  vapor  administered to
male  and female  Sprague-Dawley  rats by   Inhalation.   U.S.  EPA/OTS  Public
Files, 8D submission.  Microfiche # OTS 0513229.

U.S.  EPA.    1987.   Health  and  Environmental   Effects  Document for  Cumene.
Prepared by  the Office of Health  and Environmental  Assessment,  Environmental
Criteria and Assessment  Office, Cincinnati, OH  for  the Office of Solid Waste
and Emergency Response,  Washington, DC.

U.S.  EPA.    1990.   Integrated  Risk  Information  System  (IRIS).    Online.
Office of  Health and Environmental   Assessment, Environmental  Criteria  and
Assessment  Office, Cincinnati, OH.
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Wolf,  M.A.,  V.K.  Rowe,  D.D. McColllster,  R.L.  Holllngsworth  and  F.  Oyen.
1956.  lexicological  Studies of certain  alkylated benzene and  benzenes  AHA
Arch. Ind. Health.  14: 387-398.

Cyanazlne
Shell  Chemical  Company.   1986.  Confidential  Business  Information;  unpub-
lished study.  MRID No. 40081901 and 40229001.

U.S.  EPA.   1984.   Health  and  Environmental  Effects  Profile  for  Cyanazlne.
Prepared by  the Office  of  Health and  Environmental Assessment, Environmental
Criteria  and Assessment  Office.  Cincinnati.  OH for  the Office  of  Solid
Waste. Washington. DC.

U.S.  EPA.   1990.   Integrated   Risk  Information  System  (IRIS).   Online.
Office of  Health  and  Environmental Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

Cyanide
Howard,  J.W.  and  R.F.  Hanzal.   1955.    Chronic  toxldty  for  rats of  food
treated with hydrogen  cyanide.   J.  Agrlc. Food Chem.   3:325-329.   (Cited 1n
U.S. EPA, 1985)

U.S.  EPA.   1984.   Health  Effects  Assessment for  Cyanide.  Prepared  by  the
Office of  Health  and  Environmental Assessment,  Environmental  Criteria  and
Assessment Office,  Cincinnati,  OH  for  the  Office of Emergency  and Remedial
Response, Washington, DC.   EPA 540/1-86-011.

U.S.  EPA.   1990.   Integrated   Risk  Information  System  (IRIS).   Online.
Office of  Health  and  Environmental Assessment,  Environmental  Criteria  and
Assessment Office. Cincinnati, OH.

Cyanogen
Howard,  J.W.  and  R.F.  Hanzal.   1955.    Chronic  toxldty  for  rats of  food
treated with hydrogen cyanide.  Agrlc.  Food Chem.   3:  325-329.

Phllbrlck, D.J..  J.B.  Hopkins.  D.C. H111,  J.C. Alexander  and  R.G.  Thomson.
1979.  Effects  of  prolonged  cyanide and  thlocyanate  feeding  In  rats.   J.
Toxlcol.  Environ.  Health.   5: 579-592.

U.S.  EPA.   1990.   Integrated   Risk  Information  System  (IRIS).   Online.
Office of  Health  and  Environmental Assessment,  Environmental  Criteria  and
Assessment Office. Cincinnati, OH.

Cyanogen bromide
Howard,  J.W.  and  R.F.  Hanzal.   1955.    Chronic  toxldty  for  rats of  food
treated with hydrogen cyanide.  Agrlc.  Food Chem.   3:  325-329.

Phllbrlck, D.J.,  J.B.  Hopkins,  D.C. Hill.  J.C. Alexander  and  R.G.  Thomson.
1979.  Effects  of  prolonged  cyanide and  thlocyanate  feeding  In  rats.   J.
Toxlcol.  Environ.  Health.   5: 579-592.

U.S.  EPA.   1990.   Integrated   Risk  Information  System  (IRIS).   Online.
Office of  Health  and  Environmental Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.
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Cycloate
U.S.  EPA.   1984.   Health  and  Environmental  Effects  Profile  for  Cycloate.
Prepared by the Office of  Health  and  Environmental  Assessment, Environmental
Criteria  and  Assessment  Office.   Cincinnati,  OH  for  the  Office  of  Solid
Waste, Washington,  DC.

Cyclohexanol
U.S.  EPA.   1985.    Health and   Environmental  Effects  Profile  for  Cyclo-
hexanol.   Prepared  by  the Office  of Health  and Environmental  Assessment,
Environmental  Criteria and Assessment Office,  Cincinnati, OH  for  the Office
of Solid Waste and  Emergency Response, Washington, DC.

Cyclohexylamlne
Gaunt,  I.F.,  M. Sharratt, P.G.  Grasso,  A.B.  Lansdown  and  S.D.  Gangolll.
1974.  Short-term toxldty  of  cyclohexylamlne  HC1 1n the  rat.   Food  Cosmet.
Toxlcol.  12:  609-624.

Gaunt,  I.F.,   J.  Hardy,  P.  Grasso,   S.D.  Gangolll  and  K.R.  Butterworth.
1976.  Long-term toxldty  of cyclohexylamlne hydrochlorlde In  the  rat.   Food
Cosmet.  Toxlcol.   14(4):  255-268.

U.S.  EPA.   1987.   Health  and  Environmental  Effects  Document for Cyclohexyl-
amlne.   Prepared  by  the  Office  of   Health  and  Environmental  Assessment,
Environmental  Criteria and Assessment Office.  Cincinnati, OH  for  the Office
of Solid Waste and  Emergency Response, Washington. DC.

U.S.  EPA.   1990.    Integrated  Risk   Information  System   (IRIS).    Online.
Office  of  Health and  Environmental  Assessment.  Environmental  Criteria  and
Assessment Office,  Cincinnati,  OH.

Cyclopentadlene
Dow.   1987.   Confidential  Business   Information;   unpublished  data.    Dow
Chemical U.S.A.. Midland.  MI.

U.S.  EPA.   1987.   Health  and  Environmental  Effects  Document for Cyclopenta-
dlene and  Dlcyclopentadlene.   Prepared by  the  Office of  Health and Environ-
mental Assessment,  Environmental  Criteria and Assessment  Office, Cincinnati.
OH for the Office of Solid  Waste and Emergency  Response. Washington, DC.

Dacthal
Diamond  Shamrock  Agricultural   Chemicals.   1963.    Confidential   Business
Information; unpublished study.  MRID  No.  00083584.

U.S.  EPA.   1984.   Health   and Environmental  Effects  Profile  for  Dacthal.
Prepared by the Office of  Health  and  Environmental  Assessment. Environmental
Criteria  and  Assessment  Office,   Cincinnati,  OH  for  the  Office  of  Solid
Waste, Washington,  DC.

U.S.  EPA.   1990.    Integrated  Risk   Information  System   (IRIS).    Online.
Office  of  Health and  Environmental  Assessment.  Environmental  Criteria  and
Assessment Office,  Cincinnati.  OH.
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Dalapon (sodium salt)
Paynter,  O.E.,  T.W. Tuslng,  D.D.  McColllster  and
cology  of  dalapon  sodium  (2,2-d1chloropropo1on1c
Agrlc. Food Chem.  8: 47-51.
                              V.K.  Rowe.   1960.   Tox1-
                              acld,  sodium  salt).   J.
U.S.  EPA.    1984.   Health  and  Environmental  Effects  Profile  for  Dalapon.
Prepared by  the  Office  of  Health and  Environmental Assessment, Environmental
Criteria  and  Assessment  Office,  Cincinnati,  OH  for  the  Office of  Solid
Waste, Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.
2.4-DB
Rhodla  Inc.   1969.
MRID No. 0092165.
Confidential  Business  Information;  unpublished  study.
U.S.  EPA.    1984.   Health  and  Environmental  Effects  Profile  for  2.4-DB.
Prepared by  the  Office  of  Health  and  Environmental Assessment, Environmental
Criteria  and  Assessment  Office,  Cincinnati,  OH  for  the  Office of  Solid
Waste, Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

DDT
Laug, E.P.,  A.A. Nelson,  O.G.  Fltzhugh and  P.M.  Kunze.   1950.   Liver  cell
alteration and  DDT storage In  the  fat  of  the rat Induced  by dietary levels
of 1-50 ppm DDT.  J. Pharmacol. Exp. Therap.  98: 268-273.

U.S. EPA.  1984.   Health Effects  Assessment  for  DDT.   Prepared by the Office
of  Health  and Environmental  Assessment.  Environmental  Criteria  and  Assess-
ment  Office,  Cincinnati.   OH  for  the  Office  of  Emergency  and  Remedial
Response, Washington,  DC.

U.S.  EPA.   1988.  Updated  Health Effects  Assessment  for  DDT.   Prepared  by
the  Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria
and  Assessment  Office,  Cincinnati,  OH  for  the  Office  of  Emergency  and
Remedial Response, Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health  and  Environmental  Assessment.  Environmental  Criteria  and
Assessment Office. Cincinnati. OH.

Decabromodlphenyl ether
Koclba,   R.J.,  L.O.  Frauson,   C.G.  Humlston.  et  al.   1975.   Results of  a
two-year  dietary  feeding   study  with  decabromodlphenyl   oxide   (DBDPO)  In
rats.  Combust. Toxlcol.  2: 267-285.

U.S.  EPA.   1983.   Health  and  Environmental  Effects  Profile  for Bromlnated
Dlphenyl Ether.  Prepared  by  the  Office of Health and  Environmental  Assess-
ment. Environmental Criteria  and Assessment  Office,  Cincinnati,  OH  for  the
Office of Solid Waste. Washington. DC.
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U.S.  EPA.   1900.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

Decabromodlphenyl oxide
Koclba,  R.J.,   L.O.  Frauson,  C.G.   Humlston,  et  al.   1975.   Results of  a
two-year  dietary  feeding  study with   decabromodlphenyl   oxide   (DCDPO)  1n
rats.  Combust. Toxlcol.  2: 267-285.

Morris.  J.M.,  J.U. Ehrmantraut,  C.L.  Gibbons,  et  al.   1973.   lexicological
and  environmental factors  Involved  In  the  selection of  decadlbromophenyl
oxide as a fire retardant chemical.   Appl.  Polym. Symp.  22: 195-219.

Morris,  J.M.,  J.W.  Ehrmantraut, C.L. Gibbons,  et al.  1975.   Toxicology of
octabromoblphenyl  and   decabromodlphenyl  oxide.   Environ.  Health Perspect.
11: 153-161.

U.S. EPA.   1987.   Health  and  Environmental  Effects Document for Decabromodl-
phenyl  oxide.   Prepared by  the Office  of  Health and  Environmental  Assess-
ment,  Environmental  Criteria and Assessment  Office,  Cincinnati,  OH  for  the
Office of Solid Waste and Emergency Response, Washington,  DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

Dldzlnon
Davles,  D.B. and  B.J.  Holub.   1979.  Comparative  susceptibility  of  male  and
female rats to dietary dlazlnon toxldty.  0. Nutr.  109(6): xxvlll.

Davles,  D.B.   and B.J.  Holub.   1980a.    Comparative  subacute  toxlclty  of
dietary  dlazlnon  In the  male  and  female   rat.   Toxlcol.  Appl.  Pharmacol.
54(3): 359-367.

Davles,  D.B.  and  B.J.  Holub.   1980b.   Toxlcologlcal  evaluation  of  dietary
dlazlnon In the rat.   Arch.  Environ. Contam. Toxlcol.   9(6): 637-650.

U.S.  EPA.   1984.   Health and  Environmental Effects  Profile  for Dlazlnon.
Prepared by the Office  of Health and Environmental Assessment, Environmental
Criteria  and   Assessment  Office, Cincinnati,   OH  for  the Office of  Solid
Waste, Washington, DC.

Dlbenzofuran
U.S. EPA.   1987.   Health Effects Assessment for  Dlbenzofuran.   Prepared by
the  Office  of   Health  and Environmental Assessment,   Environmental  Criteria
and  Assessment Office,  Cincinnati,  OH for  the  Office   of  Emergency  and
Remedial Response, Washington. DC.

1.4-D1bromobenzene
Carlson,  G.P.  and  R.G.  Tradlff.   1977.   Effect  of   l,4-d1bromobenzene  and
1,2,4-trlbromobenzene on  xenoblotlc metabolism.   Toxlcol.  Appl.  Pharmacol.
42: 189-196.
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U.S.  EPA.   1984.   Health and  Environmental  Effects  Profile  for  Bromoben-
zenes.   Prepared  by  the  Office  of  Health  and  Environmental  Assessment,
Environmental Criteria  and  Assessment  Office. Cincinnati, OH  for  the Office
of Solid Waste,  Washington,  DC.

U.S.  EPA.   1990.   Integrated   Risk  Information  System  (IRIS).   Online.
Office  of  Health  and  Environmental Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

Dlbromochloromethane
NTP  (National   Toxicology  Program).   1985.    Toxicology  and  Carclnogenesls
Studies  of  Chlorodlbromomethane   In  F344/N  Rats  and B6C3F1  mice  (Gavage
Studies).  NTP TR282.

U.S.  EPA.   1985.   Health and Environmental  Effects  Profile  for Bromochloro-
methanes.   Prepared  by  the  Office of  Health and  Environmental  Assessment,
Environmental Criteria  and  Assessment  Office, Cincinnati, OH  for  the Office
of Solid Waste,  Washington,  DC.

U.S.  EPA.   1989.   Health and  Environmental  Effects  Document  for  Dlbromo-
chloromethane.    Prepared  by the  Office  of Health and  Environmental  Assess-
ment.  Environmental  Criteria and  Assessment  Office, Cincinnati.  OH  for  the
Office of Solid  Waste and Emergency Response, Washington,  DC.

U.S.  EPA.   1990.   Integrated   Risk  Information  System  (IRIS).   Online.
Office  of  Health  and  Environmental Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

Dl-n-butyl phthalate
Smith,  C.C.   1953.  Toxlclty  of   butyl  stearate,  dlbutyl sebacate,  dlbutyl
phthalate and methoxyethyl oleate.  Arch. Hyg. Occup. Ned.  7: 310-318.

U.S.  EPA.    1987.   Health  Effects  Assessment  for   Selected   Phthallc  Add
Esters.   Prepared by  the  Office  of  Health  and  Environmental  Assessment,
Environmental Criteria  and  Assessment  Office, Cincinnati, OH  for  the Office
of Emergency and Remedial Response, Washington, DC.

U.S.  EPA.   1990.   Integrated   Risk  Information  System  (IRIS).   Online.
Office  of  Health  and  Environmental Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

1.2-D1chlorobenzene
Holllngsworth,   R.L.,  V.K.  Rowe,   F.  Oyen,  T.R.  Torkelson  and E.M.  Adams.
1958.   Toxldty  of o-dlchlorobenzene.   Am.  Med. Assoc.  Arch.  Ind.  Health.
17(1): 180-187.

NTP  (National   Toxicology  Program).   1985.    Toxicology  and  Carclnogenesls
studies of  l,2-d1chlorobenzene  In F344/N  rats  and  B6C3F1 mice.   U.S.  DHHS.
NIH  Tech.  Rep.   Sen.  No.  255.    (Also  publ.  as  NIH  Publ.  No. 86-2511  and
PB86-144888)

U.S.  EPA.   1987.   Health Effects   Assessment  for  Dlchlorobenzenes.  Prepared
by the Office of  Health  and  Environmental  Assessment,  Environmental  Criteria
and  Assessment   Office,  Cincinnati,  OH  for  the  Office of   Emergency  and
Remedial Response, Washington, DC.


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U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

1.3-D1ch1orobenzene
U.S.  EPA.   1987.   Health Effects Assessment  for  Dlchlorobenzenes.  Prepared
by  the  Office  of  Health  and Environmental  Assessment, Environmental Criteria
and  Assessment  Office,   Cincinnati,  OH  for  the  Office  of  Emergency  and
Remedial Response, Washington. DC.

1.4-D1chlorobenzene
R1ley,  R.A.,  I.S.   Chart,  A.  Doss,  et  al.   1980.   Para-dlchlorobenzene:
Long-Term Inhalation Study  1n the Rat.  ICI Report  Nso.  CTL/P/447.  August.
1980.

U.S.  EPA.   1987.   Health Effects Assessment  for  Dlchlorobenzenes.  Prepared
by  the  Office  of  Health  and Environmental  Assessment, Environmental Criteria
and  Assessment  Office,   Cincinnati,  OH  for  the  Office  of  Emergency  and
Remedial Response, Washington, DC.

Dlchlorobutenes
U.S.  EPA.   1987.   Health and Environmental  Effects Document  for Dlchloro-
butenes.   Prepared by  the Office  of Health  and  Environmental  Assessment,
Environmental  Criteria and  Assessment Office, Cincinnati,  OH  for  the Office
of Solid Waste and Emergency Response. Washington, DC.

Dlihlorodlfluoromethane
Clayton,  W.J.,  Jr.   1967.   Fluorocarbon  toxlclty  and  biological  action.
Fluorine Chem. Rev.  1(2): 197-252.

Prendergast, J.A.,  R.A.  Jones,  L.J.  Jenkins  and  J.  Slegal.   1967.  Effects
on experimental animals  of  long-term Inhalation  of  trlchloroethylene, carbon
tetrachlorlde,  1,1,1-trlchloroethane,  dlchlorodlfluoromethane  and  1,1-dl-
chloroethylene.  Toxlcol. Appl.  Pharmacol.   10: 270-289.

Sherman,  H.   1974.   Long-term  feeding  studies  In  rats  and  dogs  with
dlchlorodlfluoromethane  (Freon 12 Food Freezant).   Haskell  Laboratory Report
No. 24-74.  Unpublished,  courtesy duPont  de Nemours  Co.

U.S.  EPA.   1982.   Errata:  Halomethanes   Ambient   Water  Quality  Criteria
Document  for   the  Protection  of  Human  Health.   Environmental  Criteria  and
Assessment Office. Cincinnati, OH.  ECAO-CIN-D023.

U.S.  EPA.   1987.   Health Effects Assessment for  Fully  Halogenated Methanes.
Prepared by the Office of Health  and Environmental  Assessment, Environmental
Criteria and  Assessment  Office.  Cincinnati. OH  for the  Office  of Emergency
and Remedial Response,  Washington, DC.

U.S.  EPA.   1990.   Integrated   Risk  Information  System  (IRIS).   Online.
Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.
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1,1-Dlchloroethane
Hofmann, H.T.. H. B1rnst1el and  P.  Jobst.   1971.   The Inhalation toxlclty of
1,1- and l,2-d1chloroethane.   Arch. Toxlkol.   27:  248-265.   (Cited  In U.S.
EPA, 1983b)

U.S. EPA.   1983.  Drinking Water  Criteria  Document  for  1,l-D1chloroethane.
Prepared by the  Office  of  Health and  Environmental  Assessment, Environmental
Criteria and  Assessment Office,  Cincinnati, OH  for  the  Office  of  Drinking
Mater.  Washington. DC.  Final  Draft.

U.S.   EPA.    1984.    Health   Effects   Assessment   for   1,1-Dlchloroethane.
Prepared by the  Office  of  Health and  Environmental  Assessment, Environmental
Criteria and  Assessment Office,  Cincinnati,  OH  for the  Office  of  Emergency
and Remedial Response, Washington, DC.

1.1-Dlchloroethylene
Quasi,  J.F., C.G. Humlston, C.E. Wade,  et  al.  1983.   A chronic toxldty and
oncogenlclty study In rats and subchronlc  toxlclty  study  In dogs on Ingested
vlnylldene chloride.   Fund. Appl. Toxlcol.   3: 55-62.

U.S.  EPA.    1984.    Health   Effects   Assessment   for  1,1-Dlchloroethylene.
Prepared by the  Office  of  Health and  Environmental  Assessment, Environmental
Criteria and  Assessment Office,  Cincinnati,  OH  for the  Office  of  Emergency
and Remedial Response, Washington. DC..

U.S. EPA.   1988.  Updated  Health  Effects  Assessment  for  1,1-Dlchloroethy-
lene.    Prepared by  the  Office  of   Health  and  Environmental  Assessment,
Environmental  Criteria  and  Assessment  Office, Cincinnati,  OH  for  the Office
of Emergency and Remedial Response. Washington. DC.

U.S.  EPA.    1990.   Integrated  Risk   Information  System  (IRIS).    Online.
Office   of  Health and  Environmental Assessment,  Environmental  Criteria  and
Assessment Office. Cincinnati, OH.

1,2-c-Dlchloroethylene
McCauley, P.T.,  M. Robinson,  L.W.  Condle and M.  Parveil.   n.d.   The effects
of  subacute  and subchronlc  oral  exposure  to   ds-l,2-d1chloroethylene  In
rats.  Health  Effects  Research Laboratory.  U.S. EPA, Cincinnati, OH.

U.S.  EPA.   1984.  Health  Effects  Assessment   for  1.2-c-D1chloroethylene.
Prepared by the Office  of  Health  and  Environment  Assessment. Environmental
Criteria and  Assessment Office,  Cincinnati,  OH  for the  Office  of  Emergency
and Remedial Response, Washington,  DC.

U.S.  EPA.    1990.   Integrated  Risk   Information  System  (IRIS).    Online.
Office   of  Health and  Environmental Assessment,  Environmental  Criteria  and
Assessment  Office, Cincinnati. OH.

1,2-t-D1chloroethylene
Barnes,  D.W.,  W.M.  Sanders,  K.L.  Shite, Jr.,  et al.  1985.   Toxicology of
trans-1,2-d1chloroethylene In  the mouse.  Drug Chem. Toxlcol.  8: 373-392.
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U.S.  EPA.   1984.    Health  Effects  Assessment  for  1,2-t-Dlchloroethylene.
Prepared  by the Office of  Health  and  Environmental  Assessment. Environmental
Criteria  and  Assessment  Office.  Cincinnati. OH  for the  Office  of  Emergency
and Remedial Response. Washington. DC.

U.S.  EPA.   1990.    Integrated  Risk  Information  System  (IRIS).    Online.
Office  of Health and  Environmental  Assessment.  Environmental  Criteria  and
Assessment Office,  Cincinnati, OH.

2.4-D1chloropheno1
Exon.  J.H.  and  L.D.  Koller.  1985.   Toxlclty  of 2-chlorophenol,  2,4-dl-
chlorophenol and 2,4,6-trlchlorophenol.  Water  Chlorlnatlon.   Chem. Environ.
Impact Health Eff.  Proc.  Conf.  5: 307-330.

U.S.  EPA.   1986.   Integrated Risk Information System  (IRIS):  Reference Dose
(RfD) for oral exposure  for  2,4-dlchlorophenol.   Online.   (Verification date
01/22/86.)   Office   of  Health  and  Environmental   Assessment,  Environmental
Criteria and Assessment Office, Cincinnati.  OH.

U.S.  EPA.   1987a.   Health  Effects Assessment for 2-Chlorophenol  and 2,4-DI-
chlorophenol.   Prepared  by  the  Office of  Health  and  Environmental  Assess-
ment, Environmental  Criteria and  Assessment  Office.  Cincinnati. OH  for  the
Office of Emergency and Remedial  Response.  Washington.  DC.

U.S.  EPA.   1987b.  Health  and Environmental  Effects Document  for Chlorinated
Phenols.  Prepared  by  the  Office  of  Health  and  Environmental  Assessment,
Environmental  Criteria and Assessment  Office,  Cincinnati, OH  for  the Office
of Solid Waste and  Emergency Response,  Washington, DC.

U.S.  EPA.   1990.    Integrated  Risk  Information  System  (IRIS).    Online.
Office  of Health and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office,  Cincinnati, OH.

Dlchlorophenol.  2.3-. 2-5.  2.6-.  3-4-.  3.5-
U.S.  EPA.   1987.   Health and Environmental Effects Document  for Chlorinated
Phenols.  Prepared  by  the  Office  of  Health  and  Environmental  Assessment,
Environmental  Criteria and Assessment  Office,  Cincinnati. OH  for  the Office
of Solid Waste and  Emergency Response,  Washington, DC.

2.4-D1ch1orophenoxy acetic  add (2.4-D)
Dow Chemical Co.   1983.  Ace. No.  251473.

U.S.  EPA.   1990.    Integrated  Risk  Information  System  (IRIS).    Online.
Office  of Health and  Environmental  Assessment.  Environmental  Criteria  and
Assessment Office,  Cincinnati, OH.

Dlchloroprop
U.S.  EPA.  1984.   Health  and  Environmental  Effects  Profile  for  Dlchloro-
prop.   Prepared  by   the  Office   of  Health  and   Environmental  Assessment,
Environmental  Criteria and Assessment  Office,  Cincinnati, OH  for  the Office
of Solid Waste.  Washington, DC.
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Dlchloropropanes
U.S.  EPA.   1985.   Health and Environmental  Effects  Profile for Dlchloropro-
panes.   Prepared  by  the  Office  of  Health  and Environmental  Assessment,
Environmental  Criteria  and  Assessment Office, Cincinnati,  OH  for  the Office
of Solid Waste and Emergency Response, Washington, DC.

l.3-D1ch1oropropene
Dow Chemical  Co.   1973.   MRID Nos. 0067977.  0039684.   U.S. EPA. Washington.
DC.

Stott, W.T..  J.T.  Young, L.L.  Calhoun  and  J.E.  Battjes.   1988.  Subchronlc
tox1c1ty  of  Inhaled  technical  grade 1,3-dlchloropropene   In rats  and mice.
Fund. Appl. Toxlcol.  11: 207-220.

U.S.  EPA.   1985.   Health and  Environmental  Effects Profile for 1,3-D1chloro-
propene.   Prepared  by  the  Office  of  Health and Environmental  Assessment,
Environmental  Criteria  and  Assessment Office, Cincinnati,  OH  for  the Office
of Solid Waste and Emergency Response, Washington, DC.

U.S.   EPA.    1989.    Health   and   Environmental   Effects    Document   for
1,3-Dlchloropropene.   Prepared  by  the  Office of  Health  and  Environmental
Assessment, Environmental Criteria and  Assessment Office,  Cincinnati, OH for
the Office of Solid Waste and Emergency Response. Washington. DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health  and  Environmental   Assessment.  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

Dlcyclopentadlene
Dodd.  D.E.,  L.C.  Longo  and  D.L.  Elsler.   1982.   Dlcyclopentadlene  vapor
ninety-day  Inhalation  study  on rats  and mice.   Bushy Run  Research  Center.
Export. PA.   PSCA  8e submission by Exxon Chem.  Amer.   Doc. I.D. 88-8300464.
Odd Doc. I.D.  8EHQ-0283-0364.   Microfiche No. OTS204864.

Litton  Blonetlcs.  Inc.  1980.   Mammalian Toxlcologlcal  Evaluation  of  DIMP
and  DCPD.   (Phase  2).   LUton  Blonetlcs.   Inc..  Kensington,   MD.   Contract
DAMB.  17-77-C-7003.  NTIS AD-A082685.

U.S.  EPA.   1987.   Health and  Environmental  Effects  Document  for Cyclopenta-
dlene and  Dlcyclopentadlene.  Prepared  by the Office  of  Health and Environ-
mental Assessment, Environmental  Criteria and Assessment  Office, Cincinnati,
OH for the Office of Solid Waste and  Emergency Response. Washington. DC.

Dleldrln
Walker, A.I.T., D.E.  Stevenson, J. Robinson,  et al.   1969.   The  toxicology
and pharmacodynamlcs of dleldrln  (HEOD): Two-year  oral exposures of rats  and
dogs.  Toxlcol. Appl. Pharmacol.  15:  345-373.

U.S.  EPA.   1987.   Health Effects  Assessment  for  Dleldrln.  Prepared  by  the
Office of  Health   and  Environmental   Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati,  OH for  the  Office of  Emergency  and Remedial
Response,  Washington, DC.
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U.S.  EPA.   1990.    Integrated  Risk  Information  System  (IRIS).    Online.
Office of  Health and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office,  Cincinnati,  OH.

N.N-Dlethylanlllne
U.S. EPA.   1987.   Health  and Environmental Effects Profile  for  N,N-D1ethyl-
anlllne.    Prepared  by  the  Office  of  Health  and Environmental  Assessment.
Environmental Criteria  and  Assessment  Office.  Cincinnati. OH for  the Office
of Solid  Waste and  Emergency Response.  Washington, DC.

Dlethylene glycol monoethyl  ether
Hall, D.E.,  F.S. Lee,  P.  Austin  and  F.A.  Falrweather.   1966.   Short-term
feeding study with dlethylene  glycol monoethyl ether  In  rats.   Food  Cosmet.
Toxlcol.   4: 263.

Smyth, H.F.,  C.P.  Carpenter  and  C.B.  Shaffer.   1964.   A  2-year  study  of
dlethylene  glycol  monoethyl   ether  In  rats.    Food  Cosmet.  Toxlcol.   2:
641-642.

U.S. EPA.   1984.  Health  Effects Assessment for  Glycol Ethers.   Prepared  by
the  Office  of Health  and Environmental  Assessment,  Environmental  Criteria
and  Assessment  Office, Cincinnati,  OH  for the  Office   of  Solid Waste  and
Emergency Response, Washington, DC.   EPA  540/1-86-052.

Dlethylformamlde
Argus,  M.F.,  J.C.   Arcos  and  C.   Hoch-Llgetl.    1965.    The   carcinogenic
activity  of  protein-denaturing  agents  hepatocardnogenlclty of  dloxane.   J.
Natl. Cancer Inst.   35: 949-958.

U.S. EPA.   1986.   Health  and Environmental Effects Profile  for  Dlethylform-
amlde.   Prepared by   the  Office  of  Health   and Environmental  Assessment,
Environmental Criteria  and  Assessment  Office,  Cincinnati, OH for  the Office
of Solid  Waste and  Emergency Response,  Washington. DC.

!.2-D1ethy1hydraz1ne
U.S. EPA.   1984.   Health  and Environmental Effects Profile  for  1.2-D1ethyl-
hydrazlne.   Prepared  by the Office  of  Health and  Environmental  Assessment,
Environmental Criteria  and  Assessment  Office.  Cincinnati. OH for  the Office
of Solid  Waste,  Washington.  DC.

D1 ethyl-p-nUrophenylphosphate  (Paraoxon)
U.S. EPA.   1989.  Health  and  Environmental Effects Document for  Dlethyl-p-
nltrophenylphosphate.    Prepared  by  the  Office of  Health and  Environmental
Assessment, Environmental  Criteria and Assessment Office, Cincinnati, OH  for
the Office of Solid Waste  and Emergency Response.  Washington. DC.

Dlethyl  phthalate
Brown. D.,   K.R.  Butterworth,   I.F.  Gaunt  et  al.   1978.   Short-term  oral
toxlclty  study of dlethyl phthalate  1n the rat.   Food Cosmet.  Toxlcol.  16:
415-422.

U.S.  EPA.    1987.   Health  Effects  Assessment for  Selected  Phthallc  Add
Esters.    Prepared  by  the  Office  of  Health  and Environmental  Assessment,
Environmental Criteria  and  Assessment  Office,  Cincinnati, OH for  the Office
of Emergency and Remedial  Response.  Washington, DC.


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 U.S.   EPA.    1990.    Integrated  Risk   Information   System  (IRIS).    Online.
 Office of  Health  and Environmental  Assessment, Environmental  Criteria and
 Assessment  Office,  Cincinnati, OH.

 Dlmethoate
 American  Cyanlmld  Company.   1986.   MRIO No. 00164177.  U.S.  EPA, Washington,
 DC.

 U.S.  EPA.  1985.   Health  and Environmental  Effects  Profile for Dlmethoate.
 Prepared  by the Office of  Health and Environmental Assessment,  Environmental
 Criteria  and  Assessment  Office,  Cincinnati,  OH  for  the  Office  of  Solid
 Waste, Washington,  DC.

 U.S.   EPA.    1990.    Integrated  Risk   Information  System  (IRIS).    Online.
 Office of  Health  and Environmental  Assessment, Environmental  Criteria and
 Assessment  Office,  Cincinnati, OH.

 N.N-D1methylan111ne
 Abdo,  K.,  M.  Wolfe  and  R.  Hlles.   1984.   Subchronlc  toxlclty  of  N,N-d1-
 methylanlllne  to F-344 rats and B6C3F1 mice.  Fed.  Proc.   43(3): 1698.

 U.S.  EPA.   1986.   Health and  Environmental Effects Profile  for  N,N-D1methyl-
 anlllne.   Prepared  by  the Office  of  Health and  Environmental Assessment,
 Environmental  Criteria  and  Assessment Office, Cincinnati, OH for  the Office
 of Solid Waste and  Emergency Response, Washington,  DC.

 U.S.   EPA.   1990.    Integrated  Risk  Information  System  (IRIS).    Online.
 Office  of  Health  and Environmental  Assessment, Environmental  Criteria and
 Assessment  Office, Cincinnati, OH.

 N.N-Dlmethylformamlde
 Beccl,  P.J.,  K.A.  Voss,  W.D. Johnson,  M.A. Gallo and  J.G.  Bablsh.   1983.
 Subchronlc  feeding  study of N.N-dlmethylformamlde  In rats and  mice.  J. Am.
 Coll.  Toxlcol.  2(6): 371-378.

 U.S.  EPA.   1986.   Health and  Environmental Effects  Profile  for  N.N-Dlmethyl-
 formamlde.   Prepared by the  Office  of  Health and  Environmental Assessment,
 Environmental  Criteria  and  Assessment Office, Cincinnati,  OH for  the Office
 of Solid Waste and Emergency Response, Washington, DC.

 Dlmethylphenols (2.3-; 2.5-)
 U.S.  EPA.   1986.   Health   and  Environmental Effects  Profile  for   Dimethyl-
 phenols.   Prepared  by  the  Office  of  Health  and  Environmental Assessment,
 Environmental  Criteria and  Assessment Office, Cincinnati,  OH for  the Office
 of Solid Waste and Emergency Response, Washington, DC.

 2.4-D1methylpheno1
American  B1ogen1cs  Corporation.   1989.   Ninety-day  gavage study  In albino
mice using 2,4-dlmethylphenol.  Study 410-2831.

U.S.  EPA.   1986.   Health   and  Environmental Effects  Profile  for   Dimethyl-
phenols.   Prepared   by  the  Office  of  Health  and  Environmental Assessment,
Environmental Criteria and  Assessment Office, Cincinnati,  OH  for  the Office
of Solid Waste and Emergency Response, Washington, DC.
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U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health and  Environmental Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

2.6-D1methy1phenol
Veldre,  I.A.  and H.J.  Janes.   1979.  lexicological  studies  of  shale  oils,
some of  their components and  commercial  products.   Environ. Health Perspect.
30: 141-146.

U.S. EPA.   1987.  Health  Effects Assessment for  Dlmethylphenols.  Prepared
by  the  Office of  Health  and  Environmental  Assessment,  Environmental Criteria
and  Assessment   Office,  Cincinnati,  OH  for  the  Office  of  Emergency  and
Remedial Response. Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health and  Environmental Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

3.4-D1methy1phenol
Veldre,  I.A.  and H.J.  Janes.   1979.  lexicological  studies  of  shale  oils,
some   of   their   components   and  commercial  products.    Environ.   Health
Perspect.  30: 141-146.

U.S. EPA.   1987.  Health  Effects Assessment for  Dlmethylphenols.  Prepared
by  the  Office of  Health  and  Environmental  Assessment,  Environmental Criteria
and  Assessment   Office,  Cincinnati,  OH  for  the  Office  of  Emergency  and
Remedial Response, Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health and  Environmental Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

Dimethyl phthalate
Lehman, A.J.  1955.  Insect repellants.  Assoc. Food  Drug Office, U.S.  Quart
Bull.  19: 87.

U.S. EPA.  1987.  Health and  Environmental  Effects  Profile for Phthallc Add
Alkyl,   Aryl  and  Alkyl/Aryl  Esters.  Prepared  by  the  Office of  Health  and
Environmental  Assessment,   Environmental  Criteria  and  Assessment  Office,
Cincinnati,   OH   for   the  Office  of  Solid  Waste  and  Emergency  Response,
Washington,  DC.

Dimethyl terephthalate
NCI  (National Cancer  Institute).   1979.  Bloassay  of  dimethyl terephthalate
for possible carclnogenlclty.   DHEW/PUB/NIH 79-1376, NCI-C6-TR121.

U.S. EPA.   1984.  Health and  Environmental Effects Profile for  Dimethyl  and
Methyl   lerephthalate.   Prepared  by  the Office of  Health  and Environmental
Assessment,  Environmental  Criteria  and Assessment  Office, Cincinnati,  OH for
the Office of Solid Waste,  Washington,  DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health and  Environmental Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.
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N.N-D1methy1iirea
U.S.  EPA.   1984.   Health  and Environmental  Effects Profile for N.N-Dlmethyl-
urea.   Prepared  by  the  Office  of   Health  and  Environmental  Assessment,
Environmental  Criteria  and Assessment Office, Cincinnati,  OH for  the Office
of Solid Waste and Emergency Response, Washington, DC.

m-Dlnltrobenzene
Cody,  T.E.,  S.  Wltherup,  L. Hastings, K. Stemmer  and R.T. Christian.  1981.
l,3-D1n1trobenzene: Toxic  effect  Ui vivo  and  In  vitro.  J. Toxlcol. Environ.
Health.  7(5): 829-847.

U.S.  EPA.   1985.  Health  and  Environmental Effects  Profile  for  DlnHroben-
zenes  (o-,  m-,  p-).    Prepared  by the  Office  of Health  and Environmental
Assessment, Environmental  Criteria and Assessment  Office, Cincinnati, OH for
the Office of Solid Waste and Emergency Response, Washington, DC.

U.S.   EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health  and  Environmental   Assessment,  Environmental Criteria  and
Assessment Office, Cincinnati, OH.

Dlnltrobenzene (o-. p-)
Cody,  I.E.,  S.  Wltherup,  L. Hastings, K. Stemmer  and R.T. Christian.  1981.
l,3-D1n1trobenzene: Toxic  effect  U) vivo  and  In  vitro.  J. Toxlcol. Environ.
Health.  7(5): 829-847.

U.S.  EPA.   1985.  Health  and  Environmental Effects  Profile  for  Dlnltroben-
zenes  (o-,  m-,  p-).    Prepared  by the  Office  of Health  and Environmental
Assessment, Environmental  Criteria and Assessment  Office, Cincinnati, OH for
the Office of Solid Waste and Emergency Response, Washington. DC.

2.6-D1n1tro-p-creso1
U.S.  EPA.   1984.   Health and Environmental Effects  Profile for 2,6-D1n1tro-
p-cresol.   Prepared  by  the Office of Health and  Environmental  Assessment,
Environmental  Criteria  and Assessment Office, Cincinnati,  OH for  the Office
of Solid Waste. Washington. DC.

4.6-Dlnltro-o-cresol
U.S.  EPA.   1986.   Health  and  Environmental  Effects  Profile for  Dlnltro-
cresols.   Prepared by  the  Office  of Health  and Environmental  Assessment,
Environmental  Criteria  and Assessment Office, Cincinnati,  OH for  the Office
of Solid Waste and Emergency Response, Washington.  DC.
2,4-Dlnltrophenol
Homer,  W.D.    1942.   Dlnltrophenol  and
cataracts.  Arch. Ophthalmol.  27: 1097-1121
         Us   relation  to  formation  of
U.S.  EPA.   1984.   Health  and  Environmental  Effects  Profile for  Dlnltro-
phenols  (Selected).   Prepared  by  the  Office  of  Health and  Environmental
Assessment, Environmental Criteria and Assessment  Office, Cincinnati.  OH for
the Office of  Solid Waste. Washington.  DC.

U.S.  EPA.    1990.    Integrated   Risk  Information  System  (IRIS).   Online.
Office  of  Health  and  Environmental  Assessment,  Environmental Criteria  and
Assessment Office,  Cincinnati,  OH.
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Dlnltrophenols
U.S.  EPA.   1984.   Health  and  Environmental  Effects  Profile for  Dlnltro-
phenols  (Selected).   Prepared  by  the  Office  of  Health and  Environmental
Assessment. Environmental Criteria and Assessment  Office, Cincinnati,  OH for
the Office of Solid Waste. Washington. DC.

Dlnltrotoluenes
U.S.  EPA.   1986.   Health  and  Environmental  Effects  Profile for  DlnHro-
toluene.   Prepared  by  the  Office  of Health  and  Environmental  Assessment,
Environmental Criteria  and  Assessment Office,  Cincinnati, OH  for  the  Office
of Solid Waste and Emergency Response, Washington. DC.

Dl-n-octyl phthalate
Plekacz, H.  1971.  Effect  of dloctyl and  dlbutyl  phthalates on the organism
of rats after oral administration In  prolonged  experiment.   II. Subacute and
chronic toxldty.  Rocz. Panstw.  Zakl. Hlg.  22(3): 295-307.   (CA 75:96911v)

U.S. EPA.  1987.  Health  and Environmental  Effects Profile  for Phthallc  Acid
Alkyl,  Aryl  and  Alkyl/Aryl  Esters.   Prepared  by  the  Office  of  Health and
Environmental  Assessment,  Environmental   Criteria  and  Assessment  Office,
Cincinnati,  OH  for   the Office  of  Solid  Waste  and   Emergency  Response,
Washington, DC.

Dlnoseb
Dow Chemical Company.   1981.  Confidential  Business Information;  unpublished
Study.  NRID No. 00152675.

U.S.  EPA.   1984.   Health  and  Environmental  Effects  Profile for  Dlnoseb.
Prepared by the  Office  of Health  and  Environmental Assessment, Environmental
Criteria  and  Assessment  Office.  Cincinnati.  OH  for  the  Office of  Solid
Waste, Washington, DC.

U.S.  EPA.   1990.   Integrated   Risk   Information  System  (IRIS).   Online.
Office  of  Health and  Environmental   Assessment,  Environmental Criteria and
Assessment Office, Cincinnati,  OH.

N.N-Dlphenylamlne
Thomas, G.O., W.E. Rlbelln,  J.R.  Woodward  and F.  DeEds.   1967.  The chronic
toxldty of dlphenylamlne for dogs.   Toxlcol. Appl. Pharmacol.  11: 184-194.

U.S. EPA.  1985.  Health  and Environmental  Effects Profile  for N,N-D1phenyl-
amlne.   Prepared by  the  Office of  Health and  Environmental  Assessment,
Environmental Criteria  and  Assessment Office,  Cincinnati, OH  for  the  Office
of Solid Waste and Emergency Response. Washington, DC.

U.S.  EPA.   1990.   Integrated   Risk   Information  System  (IRIS).   Online.
Office  of  Health and  Environmental   Assessment,  Environmental Criteria and
Assessment Office, Cincinnati,  OH.

Direct Ughtfast blue
U.S. EPA.  1987.  Health and Environmental  Effects Profile  for Direct  Light-
fast Blue.   Prepared  by the Office of  Health and  Environmental  Assessment,
Environmental Criteria  and  Assessment Office.  Cincinnati, OH  for  the  Office
of Solid Waste, Washington,  DC.
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 Dlsulfoton
 Mobay  Chemical  Company.   1985.
 Available from EPA.  Write to FOI,
 MRIO  No.  00129456,  00146873,
EPA. Washington, DC 20460.
41115401
 U.S.   EPA.    1990a.    Health   and   Environmental   Effects   Document  for
 Dlsulfoton.   Prepared  by the Office of  Health and Environmental Assessment,
 Environmental  Criteria  and Assessment Office,  Cincinnati,  OH for the  Office
 of  Solid Waste and Emergency Response, Washington, DC.

 U.S.  EPA.   1990b.   Integrated  Risk   Information  System  (IRIS).   Online.
 Office  of  Health  and  Environmental  Assessment,   Environmental  Criteria and
 Assessment Office, Cincinnati, OH.

 Endosulfan
 Huntlngton Research  Center.   1984.   Effect of Endosulfan-Technlcal on  Repro-
 ductive  Function of Multiple  Generations In  the Rat.   Report  submitted by
 J.A. Edwards et  al. to OPP, U.S. EPA.

 U.S.  EPA.   1987.   Health  Effects  Assessment   for  Alpha- and  Beta-Endo-
 sulfan.   Prepared  by  the  Office  of  Health  and  Environmental  Assessment,
 Environmental  Criteria  and Assessment Office,  Cincinnati,  OH for the  Office
 of  Emergency and Remedial Response, Washington, DC.

 U.S.  EPA.   1990.   Integrated  Risk  Information  System   (IRIS).   Online.
 Office  of  Health  and  Environmental Assessment,   Environmental  Criteria and
 Assessment Office, Cincinnati, OH.

 Endothall
 Keller,  J.   1965.   Two-year chronic feeding study of  dlsodlum endothall to
 beagle  dogs.   Scientific  Associates Report.   EPA Pesticide Petition 6G0503,
 redeslgnated No. 7F0570, June 1966.  Accession No. 24601.

 Pennwalt Agchem.   n.d.   MRID  No. 00101735.  Available  from U.S.  EPA.  Write
 to  FOI, EPA,  Washington, DC 20460.

 U.S. EPA.   1989.  Health  and  Environmental  Effects  Document for Endothall.
 Prepared by  the  Office of  Health and Environmental Assessment, Environmental
 Criteria and Assessment  Office, Cincinnati,  OH,  for   the  Office  of  Solid
 Waste and Emergency Response,  Washington, DC.

 U.S.  EPA.    1990.   Integrated  Risk  Information  System   (IRIS).   Online.
 Office  of  Health  and  Environmental Assessment,   Environmental  Criteria and
 Assessment Office, Cincinnati, OH.
Endrln
Treon,  3.F.,  F.P.  Cleveland  and  J. Cappel.   1955.
laboratory animals.  Agrlc. Food Chem.   3: 842-848.
                   Toxlclty of  endrln  for
U.S. EPA.  1985.   Drinking  Water  Criteria Document  for  Endrln.   Prepared by
the  Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria
and  Assessment  OFflce,  Cincinnati,  OH  for  the  Office  of  Drinking  Water,
Washington,  DC.   EPA 600/X-84-176.  NTIS PB 86-117967.
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U.S.  EPA.   1987.   Health  Effects Assessment  for  Endrln.   Prepared  by  the
Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office,  Cincinnati,  OH for  the  Office of  Emergency  and Remedial
Response, Washington. DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

Eplchlorohydrln
Laskln, S., A.R.  Sellakumar,  M. Kuschner. et  al.   1980.  Inhalation carclno-
genlclty  of  eplchlorohydrln  1n  non-Inbred  Sprague-Dawley  rats.   3.  Natl.
Cancer Inst.   65(4): 751-757.

Quast.  J.F.,   J.W.  Henck,   B.J.  Postma.  et   al.  1979.   Eplchlorohydrln
subchronlc studies.  I. A 90-day  Inhalation study In Laboratory Rodents.   8D
submission.  Microfiche #206200.

U.S.  EPA.  1984.   Health Assessment  Document  for  Eplchlorohydrln.  Office of
Health  and  Environmental Assessment,  Environmental Criteria  and Assessment
Office, Research Triangle Park, NC.  EPA 600/8-83-032F.  NTIS PB85-132363.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

Ethoprop
U.S.  EPA.   1984.   Health  and  Environmental  Effects  Profile  for  Ethoprop.
Prepared by the  Office of Health  and Environmental  Assessment, Environmental
Criteria  and  Assessment  Office,   Cincinnati.  OH for  the  Office   of  Solid
Waste, Washington, DC.

2-Ethoxyethanol
Barbee, S.J., J.B. Terrlll, D.J.  DeSousa and  C.C. Conaway.  1984. Subchronlc
Inhalation toxicology  of  ethylene  glycol  monoethyl  ether  In  the rat  and
rabbit.  Environ. Health Perspect.  57: 157-163.

Doe,  J.E.    1984.   Ethylene   glycol   monoethyl   ether  and  ethylene  glycol
monoethyl ether  acetate  teratology studies.  Environ.  Health  Perspect.   57:
33-41.

Melnlck,  R.L.    1984.   Toxlcltles of   ethylene   glycol  and ethylene  glycol
monoethyl  ether  In  Fischer  344/N  rats  and  B6C3F1  mice.   Environ  Health
Perspect.  57:  147-155.

Stenger, E.G.,   A.  Llslott,  D. Mueller  et al.  1971.   Toxicology of ethylene
glycol  monoethylether.   Arznelm.-Forsch.   21(6):  880-885.  (In  German  with
English translation)

U.S.  EPA.  1984.   Health Effects  Assessment for  Glycol  Ethers.   Prepared by
the  Office  of   Health  and  Environmental  Assessment,  Environmental  Criteria
and  Assessment  Office.  Cincinnati,  OH  for  the  Office  of  Solid  Waste  and
Emergency Response, Washington, DC.
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 U.S.  EPA.   1985.   Health  and  Environmental  Effects Profile  for 2-Ethoxy-
 ethanol.   Prepared by  the  Office  of  Health and  Environmental  Assessment,
 Environmental  Criteria  and Assessment Office, Cincinnati,  OH for the Office
 of Solid  Waste and Emergency Response, Washington. DC.
 2-Ethoxyethanol acetate
 Union  Carbide.   1984.
 Fisher   344   rats  and
 exposure.    Bushy   Run
 FYI-AX-1184-0360.
A  teratogenlc  evaluation  of
New  Zealand   White   rabbits
  Research   Center,   Export.
Cellosolve  Acetate  In
 following  Inhalation
  PA,   October   1984.
U.S.  EPA.   1985.   Health  and  Environmental  Effects  Profile  for 2-Ethoxy-
ethanol  Esters.   Prepared  by the Office of  Health  and Environmental Assess-
ment,  Environmental  Criteria and  Assessment Office,  Cincinnati,  OH  for the
Office of Solid Waste and Emergency Response. Washington. DC.

2-Ethoxyethanol esters
U.S.  EPA.   1985.   Health  and  Environmental  Effects  Profile  for 2-Ethoxy-
ethanol  Esters.   Prepared  by the Office of  Health  and Environmental Assess-
ment.  Environmental  Criteria and  Assessment Office,  Cincinnati,  OH  for the
Office of Solid Waste and Emergency Response, Washington, DC.
Ethyl acetate
U.S.  EPA.   1986a.   Rat  oral
Solid Waste, Washington, DC.
    subchronlc study  with  ethyl acetate.  Office of
U.S.  EPA.   1986b.    Health  and  Environmental  Effects  Profile  for  Ethyl-
acetate.   Prepared  by  the  Office  of  Health  and  Environmental Assessment,
Environmental  Criteria  and Assessment Office, Cincinnati,  OH for the Office
of Solid Waste and Emergency Response, Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of Health and Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati. OH.

N-Ethylanlllne
U.S.  EPA.   1986.   Health  and  Environmental  Effects  Profile  for  N-Ethyl-
anlllne.   Prepared  by  the  Office  of  Health  and  Environmental Assessment,
Environmental  Criteria  and Assessment Office, Cincinnati,  OH for the Office
of Solid Waste and Emergency Response. Washington, DC.

Ethylbenzene
U.S.  EPA.   1984.   Health  Effects  Assessment for Ethylbenzene.   Prepared by
the  Office of Health  and Environmental  Assessment,  Environmental  Criteria
and  Assessment Office,  Cincinnati,  OH  for  the  Office  of Emergency  and
Remedial Response. Washington. DC.

U.S.  EPA.   1986.   Health  and   Environmental  Effects   Profile for  Ethyl-
benzene.   Prepared  by  the  Office  of  Health  and  Environmental Assessment,
Environmental  Criteria  and Assessment Office, Cincinnati,  OH for the Office
of Solid Waste and Emergency Response. Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.
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Wolf, M.A., V.K.  Rowe,  D.D.  McColllster  et  al.   1956.  Toxlcologlcal studies
of certain alkylated  benzenes and  benzene.   Arch.  Ind. Health.  14: 387-398.
(CHed 1n U.S. EPA, 1985)

Ethyl chloride
U.S. EPA.  1987.   Health  Effects Assessment  for  Ethyl Chloride.  Prepared by
the  Office  of  Health and  Environmental  Assessment,  Environmental  Criteria
and  Assessment  Office,  Cincinnati,  OH  for  the  Office  of   Emergency  and
Remedial Response, Washington, DC.

S-Ethyl dlpropylthlocarbamate (EPTC)
PPG  Industries,  Inc.   1986.  Confidential  Business  Information; unpublished
study.  Accession No. 263695, 262696.  (CHed In U.S. EPA, 1987)

U.S.  EPA.   1984.   Health  and  Environmental  Effects  Profile  for  EPTC.
Prepared by the  Office  of Health and Environmental Assessment, Environmental
Criteria  and   Assessment  Office,  Cincinnati,  OH  for  the  Office   of  Solid
Waste, Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).    Online.
Office  of  Health  and Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati. OH.

Ethylene cyanohydrln
Sauerhoff, M.W.,  W.H.  Braun,  J.C.  Ramsey,  C.B.  Humlston  and  G.C.  Jersey.
1976.   lexicological  evaluation and pharmacoklnetlc  profile  of  B-hydroxy-
proplonltMle In rats.  J. Toxlcol. Environ. Health.  2(1): 31-44.

U.S.  EPA.   1988.   Health  and  Environmental   Effects  Document for  Cyano-
hydrlns.  Prepared by  the  Office  of Health  and  Environmental  Assessment,
Environmental  Criteria  and  Assessment Office,  Cincinnati,  OH  for  the Office
of Solid Waste and Emergency Response, Washington, DC.

Ethylenedlamlne
Pozzanl,  U.C.  and  C.P.  Carpenter.   1954.   Response  of  rats to  repeated
Inhalation of  ethylenedlamlne vapors.  Arch. Ind. Hyg. Occ. Med.  9: 223-226.

U.S.  EPA.   1988.   Health and Environmental  Effects Document  for  Ethylene-
dlamlne.  Prepared by  the  Office  of Health  and  Environmental  Assessment,
Environmental  Criteria  and  Assessment Office,  Cincinnati,  OH  for  the Office
of Solid Waste and Emergency Response. Washington, DC.

Yang, R.S.,  R.H.  Garman,  R.R.  Maronpot,  et al.   1983.   Acute  and subchronlc
toxlclty  of  ethylenedlamlne  In laboratory  animals.   Fund.   Appl.  Toxlcol.
3(6): 512-520.

Ethylene glycol
DePass,  L.R.,  R.H.  Garman,  M.D. Woods1de et  al.   1986a.   Chronic  toxlclty
and  oncogenlclty  studies  of ethylene glycol  In  rats and mice.  Fund.  Appl.
Toxlcol.   7:  547-565.

Maronpot,  R.R.,  J.P.  Zelenak, E.V.  Weaver  and  N.O.  Smith.   1983.   Terato-
genldty study  of  ethylene glycol  In  rats.   Drug.  Chem. Toxlcol.   6(6):
579-594.
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U.S.  EPA.   1987.   Health  Effects  Assessment  for Ethylene  Glycol.   Prepared
by  the Office of  Health  and  Environmental  Assessment,  Environmental Criteria
and  Assessment  Office,  Cincinnati,  OH  for   the  Office  of  Emergency  and
Remedial Response, Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health   and  Environmental Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

Ethylene glycol  monobutyl ether
Dodd, D.E., W.M.  Spellings,  R.R. Maronpot  and  B.  Balantyne.  1983.  Ethylene
glycol monobutyl  ether:  Acute.  9-day and 90-day  vapor  Inhalation studies 1n
Fischer 344 rats.   Toxlcol. Appl.  Pharmacol.   68: 405-414.

U.S.  EPA.  1984.   Health Effects  Assessment  for  Glycol  Ethers.   Prepared by
the  Office of  Health  and Environmental  Assessment,  Environmental  Criteria
and  Assessment  Office,  Cincinnati, OH  for  the  Office  of Solid  Waste  and
Emergency Response, Washington, DC.  EPA 540/1-86-052.

Ethylene thlourea
U.S.  EPA.   1984.   Health  and Environmental  Effects  Profile  for  Ethylene
Thlourea.  Prepared  by  the  Office  of  Health  and  Environmental Assessment,
Environmental  Criteria and Assessment  Office,  Cincinnati.  OH  for the Office
of Solid Waste,  Washington, DC.

Ethyl ether
American  Blogenlcs  Corp.  1986.   90-Day  gavage  study  In  rats  using  ehtyl
ether.  Status Report for ABC Study No.  410-2343.  3/18/86.

U.S.  EPA.   1987.   Health  Effects  Assessment   for  Ethyl  Ether.   Prepared by
the  Office of  Health  and Environmental  Assessment,  Environmental  Criteria
and  Assessment  Office,  Cincinnati  OH  for  the  Office  of  Solid  Waste  and
Emergency Response, Washington, DC.

Ethyl methacrylate
Borzelleca, J.F.,   P.S. Larson,  G.R. Hennlgar,  et al.   1964.   Studies on the
chronic  oral  toxldty  of  monomer 1c  ethyl  acrylate  and  methyl methacrylate.
Toxlcol. Appl. Pharmacol.  6: 29-36.

U.S.  EPA.  1986.   Health and  Environmental Effects Profile for  Ethyl  Meth-
acrylate.  Prepared  by  the  Office  of  Health  and  Environmental Assessment,
Environmental  Criteria and Assessment  Office,  Cincinnati,  OH  for the Office
of Solid Waste and Emergency Response,  Washington. DC.

Ethyl Toluene
U.S.  EPA.  1984.   Health and Environmental Effects  Profile for  Methyl  Ethyl
Benzene.   Prepared by the  Office  of  Health  and  Environmental  Assessment.
Environmental  Criteria and Assessment  Office,  Cincinnati,  OH  for the Office
of Solid Waste,  Washington, DC.

4-Ethyl-o-xylene
U.S.  EPA.  1984.   Health and Environmental Effects  Profile for  Methyl  Ethyl
Benzenes.  Prepared  by  the  Office  of  Health  and  Environmental  Assessment,
Environmental  Criteria and Assessment  Office,  Cincinnati,  OH  for the Office
of Solid Waste,  Washington, DC.


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Fluoranthene
U.S. EPA.   1988.   13-week mouse  oral  subchronlc  toxldty study.  Prepared by
Toxldty  Research  Laboratories,  LTD.   Muskegon,  MI  for the  Office  of Solid
Waste, Washington, DC.
Fluorene
U.S.  EPA.   1989.   Mouse  oral  subchronlc  study.
Research  Laboratories,  LTD,  Muskegon,  MI  for  the
Washington, DC.
                                          Prepared
                                        Office  of
                 by  Toxlclty
                 Solid  Waste,
Fluoride
Hodge.  H.C.
Simons, Ed.
and F.A.  Smith.   1965.  ]j\:  Fluorine
Academic Press, New York, NY.  789 p.
    Chemistry,  Vol.  IV, J.H.
U.S.  EPA.   1989.   Health  and  Environmental  Effects Document  for  Fluoride.
Prepared by the  Office  of  Health  and Environmental Assessment, Environmental
Criteria and Assessment Office, Cincinnati, OH  for the  Office of Solid Waste
and Emergency Response, Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.
Flurldone
Ell  Lilly  and  Company.
Ushed study.  Accession
              1980.   Confidential
            Nos. 070933. 070939.
Business  Information;  unpub-
U.S.  EPA.   1984.   Health
Prepared by the  Office  of
Criteria  and  Assessment
Waste, Washington, DC.
              and Environmental  Effects Profile  for  Flurldone.
              Health  and Environmental Assessment, Environmental
             Office,  Cincinnati,  OH  for  the  Office of  Solid
U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of Health  and  Environmental Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati. OH.

Folpet
Chevron  Chemical  Corporation.    1986.   Confidential  Business  Information;
unpublished study.  Accession No. 263772.

U.S.  EPA.   1984.   Health  and  Environmental  Effects  Profile  for  Folpet.
Prepared  by  the  Office of Health and Environmental  Assessment, Environmental
Criteria  and Assessment  Office,  Cincinnati.  OH  for  the  Office of  Solid
Waste, Washington. DC.
U.S.  EPA.    1990.   Integrated  Risk
Office  of  Health and  Environmental
Assessment Office,  Cincinnati,  OH.
                         Information
                        Assessment.
   System  (IRIS).   Online.
  Environmental  Criteria  and
Formaldehyde cyanohydrln
U.S.  EPA.    1988.   Health  and  Environmental  Effects   Document  for  Cyano-
hydrlns.   Prepared  by  the  Office  of Health  and  Environmental  Assessment,
Environmental Criteria  and  Assessment Office, Cincinnati, OH  for  the Office
of Solid Waste and Emergency Response, Washington, DC.
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Formic acid
Malorny,  6.  1969.
Z. Ernachrungswlss.
Acute and  chronic
 9:  332-339.
toxlclty of  formic  acid and  formate.
U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of Health  and  Environmental Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

Furan
SRI  (Southern  Research  Institute).   1982.   Subchronlc  toxlclty  report  on
furan  (C56202)   1n  B6C3F1  mice.   Prepared  for  National  Toxicology  Program
under Contract No. l-CP-95641-01. Bethesda, MD.

U.S.  EPA.   1987.    Health  and  Environmental  Effects  Document  for  Furan.
Prepared  by  the  Office of  Health  and Environmental  Assessment, Environmental
Criteria  and Assessment Office, Cincinnati,  OH  for  the Office of Solid Waste
and Emergency Response, Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of Health  and  Environmental Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

Furfural
Feron,  V.J., A.  Kruysse  and  H.C.  Dreef  Vander  Meulen.    1979.   Repeated
exposure  to  furfural  vapor:   13  week  study  In  Syrian  golden  hamsters.
Zentrase.  Baktevlol  Pavaslten  Kd Infection  SKV.  Hyg.  Abt  1 orlg Relhe  B.
168(5-6): 442-451.
SRI  (Southern  Research Institute).
study performed for NTP.
                 1981.  90  day rat report.   Unpublished
U.S.  EPA.   1988.   Health  and Environmental  Effects Document  for  Furfural.
Prepared by the  Office of  Health  and  Environmental  Assessment, Environmental
Criteria and Assessment Office, Cincinnati,  OH  for  the  Office of Solid Waste
and Emergency Response, Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk   Information  System  (IRIS).    Online.
Office  of  Health and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

Glycldaldehvde
Mine,  C.H.,  R.J.  Guzman,  M.K.   Dunlap.  R.  Lima  and  G.S.   Loquvam.   1961.
Studies on the toxlclty of glyddaldehyde.  Arch. Environ. Health.  2: 23-30.

U.S.  EPA.   1989.   Health  and Environmental  Effects  Document  for  Glydd-
aldehyde.  Prepared  by the  Office of  Health and  Environmental  Assessment,
Environmental  Criteria and  Assessment Office, Cincinnati, OH for the Office
of Solid Waste and Emergency Response, Washington,  DC.

U.S.  EPA.   1990.   Integrated  Risk   Information  System  (IRIS).    Online.
Office  of  Health and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.
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n-Heptane
U.S.  EPA.   1989.  Health  and  Environmental Effects  Document  for n-Heptane.
Prepared by  the  Office  of  Health  and Environmental  Assessment. Environmental
Criteria and Assessment Office, Cincinnati.  OH  for  the Office of Solid Haste
and Emergency Response. Washington, DC.

Heptachlor
Velslcol Chemical Corp.  1955.   MRID No. 00062599.  Available under FOI.

U.S.  EPA.  1987.  Health Effects  Assessment  for Heptachlor.   Prepared by the
Office  of  Health and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office.  Cincinnati,  OH for  the  Office of  Emergency  and Remedial
Response, Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati,  OH.

Hexabromobenzene
Mendoza, C.E.,  H.M.  Vljay. J.B.  Shields  and G.W. Laver.   1977.   Effects of
hexabromobenzene on the male rat.   Toxlcol.  Appl. Pharmacol.  41: 127-130.

U.S.  EPA.    1984.   Health   and  Environmental Effects  Profile  for  Bromoben-
zenes.   Prepared by  the   Office  of  Health and Environmental  Assessment,
Environmental Criteria  and Assessment Office,  Cincinnati, OH  for the Office
of Solid Waste, Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati,  OH.

Hexachlorobenzene
Arnold,  D.L.,  C.A.  Noodle,   S.M.  Charbonneau  et  al.   1985.   Long-term
toxldty of  hexachlorobenzene  In  the  rat and  the effect  of  dietary vitamin
A.  Food Chem. Toxlcol.  (In press).  (Cited In U.S.  EPA. 1985)

U.S.  EPA.  1984.  Health Effects  Assessment for Hexachlorobenzene.  Prepared
by the  Office of  Health and Environmental Assessment, Environmental Criteria
and  Assessment  Office,  Cincinnati,  OH  for  the Office  of  Emergency  and
Remedial Response, Washington,  DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health and  Environmental  Assessment.  Environmental  Criteria  and
Assessment Office, Cincinnati,  OH.

Hexachlorobutadlene
Koclba,  R.J.,  D.G.   Keys,  G.C.  Jersey, et  al.    1977.   Results  of  a  2-year
chronic  toxldty study  with   hexachlorobutadlene In  rats.   Am.  Ind.  Hyg.
Assoc. J.  38: 589-602.

U.S.  EPA.    1984.    Health  Effects  Assessment   for  Hexachlorobutadlene.
Prepared by  the Office of  Health  and Environmental  Assessment. Environmental
Criteria and  Assessment Office,  Cincinnati,  OH for  the Office  of Emergency
and Remedial  Response,  Washington, DC.
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U.S.  EPA.   1990.    Integrated  Risk  Information  System  (IRIS).    Online.
Office  of  Health and  Environmental  Assessment.  Environmental Criteria  and
Assessment Office.  Cincinnati,  OH.

Hexachlorocyclohexane.  gamma (Undane)
Zoecon Corporation.   1983.   MRID No.  00128356.   Available under FOI.

U.S.  EPA.   1984.   Health Effects  Assessment for  Llndane.   Prepared by  the
Office  of  Health and  Environmental  Assessment,  Environmental Criteria  and
Assessment Office. Cincinnati.  OH  for  the  Office of Emergency and  Remedial
Response, Washington, DC.

U.S.  EPA.   1990.    Integrated  Risk  Information  System  (IRIS).    Online.
Office  of  Health and  Environmental  Assessment,  Environmental Criteria  and
Assessment Office,  Cincinnati,  OH.

Hexachlorocyclopentadlene
Abdo, K.M.,  C.A.  Montgomery.  W.M.   Kluwe  et al.   1984.  Toxlclty  of  hexa-
chlorocyclopentadlene:  Subchronlc (13-week)  administration  by  gavage to F344
rats and B6C3F1 mice.  3. Appl. Toxlcol.   4: 75-81.

Battelle Northwest Laboratories.   1984.   Inhalation  Cardnogenesls  Bloassay
Study:   Subchronlc   Study   Report   on   Hexachlorocyclopentadlene   In  Rats.
Submitted to the National Toxicology  Program.

SRI  (Southern  Research  Institute).  1981a.  Subchronlc  Toxlclty Report  on
Hexachlorocyclopentadlene  (C53607)   In  B6C3F1  Mice.   Report   for   the  NTP.
Project  No. 4419-XXXVIX.   Doc.  #40-8349230.   Microfiche #0150507497.

U.S.  EPA.   1984.   Health  Effects  Assessment for  Hexachlorocyclopentadlene.
Prepared by the Office of Health and Environmental Assessment, Environmental
Criteria and Assessment  Office, Cincinnati, OH  for the Office of  Emergency
and Remedial Response,  Washington.  DC.

U.S.  EPA.   1990.    Integrated  Risk  Information  System  (IRIS).    Online.
Office  of  Health and  Environmental  Assessment.  Environmental Criteria  and
Assessment Office,  Cincinnati.  OH.

Hexachloroethane
Gorzlnskl,  S.J.,  R.J.  Nolan,   S.B.  McColllster,  et  al.   1985.   Subchronlc
oral  toxldty,  tissue  distribution and clearance  of  hexachloroethane In  the
rat.  Drug Chem. Toxlcol.  8(3): 155-169.

U.S.  EPA.   1987.   Health Effects Assessment for  Hexachloroethane.   Prepared
by the Office of Health  and  Environmental Assessment, Environmental  Criteria
and  Assessment Office,  Cincinnati.   OH  for the  Office   of  Emergency  and
Remedial Response,  Washington,  DC.

U.S.  EPA.   1989.  Health and Environmental   Effects  Document  for  Hexachloro-
ethane.    Prepared  by  the  Office  of  Health and  Environmental  Assessment,
Environmental  Criteria and  Assessment  Office,  Cincinnati,  OH  for  the Office
of Solid Waste  and  Emergency Response,  Washington, DC.
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U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health  and  Environmental Assessment.  Environmental  Criteria  and
Assessment Office. Cincinnati. OH.
Hexachlorophene
Nationwide Chemical  Corporation.   1974.
unpublished study.  HRID No. 00055365.
      Confidential  Business Information;
U.S.  EPA.   1986.   Health and  Environmental  Effects Profile  for  Hexachloro-
phene.   Prepared   by   the  Office  of  Health  and  Environmental  Assessment.
Environmental Criteria  and  Assessment  Office. Cincinnati, OH  for  the Office
of Solid Waste. Washington.  DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health  and  Environmental Assessment.  Environmental Criteria  and
Assessment Office, Cincinnati.  OH.

Hexamethylenedlamlne
U.S.  EPA.   1985.   Health   and  Environmental  Effects  Profile  for  Hexa-
methylenedlamlne.    Prepared  by  the  Office  of  Health  and  Environmental
Assessment. Environmental Criteria  and  Assessment  Office,  Cincinnati. OH for
the Office of Solid Waste and Emergency Response, Washington, DC.

n-Hexane
Krasavage,  W.J.,   J.L.  O'Donoghue.  G.D.  Dlvlncenzo  and  Terhaar.   1980.
Relative neurotoxlclty  of methyl-n-butyl ketone,  n-hexane and their metabo-
lites.  Toxlcol. Appl.  Pharmacol.  52(3): 433-441.

Sanagl. S.,  Y.  Sekl.  K. Suglmoto  and  M. Hlrata.   1980.   Peripheral nervous
system  functions  of workers  exposed to n-hexane at  a  low level.   Int. Arch.
Occup. Environ. Health.  47: 69-79.

U.S.  EPA.   1989.   Health  and   Environmental  Effects Document  for n-Hexane.
Prepared by the Office  of Health and Environmental Assessment, Environmental
Criteria and Assessment Office,  Cincinnati,  OH for the  Office of  Solid Waste
and Emergency Response, Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health  and  Environmental Assessment,  Environmental Criteria  and
Assessment Office, Cincinnati,  OH.

2-Hexanone
U.S.  EPA.   1990.   Health  and Environmental  Effects  Document  for  2-Hexanone.
Prepared by the Office  of Health and Environmental Assessment, Environmental
Criteria and Assessment Office,  Cincinnati,  OH for the  Office of  Solid Waste
and Emergency Response, Washington, DC.

Hydrogen sulflde
U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health  and  Environmental Assessment.  Environmental Criteria  and
Assessment Office, Cincinnati,  OH.
Watterau,  H.,  W.   Ockert  and  U.G.
hydrogen sulflde  1n animal  feeding.
et al.. 1975.  Landwlrtsch.   Forsch.
  Knape.   1964-1965.   In:
  Survey of  the  literature.
  28: 70-80.)
Toxlclty  of
 (Westermann
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p-Hydroqulnone
Carlson,  A.J.
Soc. Exp. Blol.
and  N.R.  Brewer.
 Med.  84:  684-688.
ToxUHy  studies  on  Hydrogulnone.   Proc.
U.S.  EPA.   1987.   Health  and  Environmental  Effects  Document  for  Hydro-
qulnone.   Prepared  by  the Office  of  Health and  Environmental Assessment,
Environmental  Criteria  and  Assessment Office, Cincinnati.  OH for the Office
of Solid Waste and Emergency Response, Washington, DC.

Iron
U.S.  EPA.   1984.    Health  Effects   Assessment  for  Iron.   Prepared  by  the
Office  of Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office,  Cincinnati.  OH  for  the Office of  Emergency and Remedial
Response, Washington, DC.

Isobutyl alcohol
U.S.  EPA.   1986a.   Rat  oral  subchronlc  toxlclty  with  Isobutyl  alcohol.
Office of Solid Waste.  Washington, DC.

U.S.  EPA.   1986b.  Health and Environmental  Effects  Profile for Isobutanol.
Prepared  by  the  Office  of  Health  and Environmental  Assessment,  Environmental
Criteria  and  Assessment  Office,  Cincinnati, OH for  the  Office  of  Solid
Waste, Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System   (IRIS).   Online.
Office  of Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.
Isophorone
Rohm and Haas.
 1972.   Pesticide  Petition  No.  2F1224.   Available  under  FOI.
NTP  (National  Toxicology  Program).   1986.   Toxicology  and  Carclnogenesls
Studies  of  Isophorone  (CAS  No.  78-59-1)  In  F344/N Rats  and  B6C3F1  Mice
(Gavage Studies).  NTP Tech. Report Ser. No. 291, NIH Publ. No. 86-2547.

U.S. EPA.  1987.  Health Effects  Assessment for  Isophorone.   Prepared by the
Office  of  Health and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office,  Cincinnati,  OH for  the  Office of Emergency  and Remedial
Response. Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati. OH.
Isopropalln
Ell  Lilly  Company.
study.
      1985.   Confidential  Business  Information;  unpublished
U.S. EPA.   1984.   Health  and Environmental Effects  Profile for Isopropalln.
Prepared by the Office of  Health  and  Environmental  Assessment, Environmental
Criteria  and  Assessment  Office,   Cincinnati,  OH  for  the  Office of  Solid
Waste,  Washington, DC.
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U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health and  Environmental Assessment,  Environmental  Criteria  and
Assessment Office. Cincinnati, OH.

Lead
U.S.  EPA.    1984.   Health  Effects   Assessment  for  Lead.   Prepared  by  the
Office  of  Health and  Environmental Assessment,  Environmental  Criteria  and
Assessment Office,  Cincinnati,  OH for  the  Office of Emergency  and Remedial
Response. Washington, DC.

U.S.  EPA.   1986.   A1r  Quality  Criteria  for Lead.   June.  1986 and Addendum.
September,  1986.   Office of  Health and  Environmental   Assessment,  Research
Triangle Park, NC.  EPA 600/8-83-028F.   NTIS PB 87-142378.
Lead alkyls
Scheper,  G.W.H.
Environ. Health.
 1964.   Tetraethyl
8:  277-295.
lead  and  tetramethyl  lead.   Arch.
U.S. EPA.  1985.   Health  and Environmental Effects Profile  for  Lead Alkyls.
Prepared by the Office of  Health  and  Environmental  Assessment, Environmental
Criteria and Assessment Office, Cincinnati, OH  for  the Office of Solid Waste
and Emergency Response, Washington, DC.
Llnuron
Du Pont de  Nemours  and Company. Inc.  1962.
tlon; unpublished study.  MRID No.  00018374.
                             Confidential  Business Informa-
U.S.  EPA.   1984.   Health  and  Environmental  Effects  Profile for  Llnuron.
Prepared by the Office of Health  and  Environmental  Assessment, Environmental
Criteria and  Assessment  Office,   Cincinnati,  OH  for  the  Office  of  Solid
Waste, Washington, DC.

U.S.  EPA.    1990.   Integrated   Risk   Information  System  (IRIS).    Online.
Office  of  Health and  Environmental  Assessment,  Environmental Criteria  and
Assessment  Office, Cincinnati,  OH.

Malathlon
Hoeller. H.C.  and  J.A.  Rider.   1962.   Plasma  and  red  blood  cell-cholln-
esterase activity as  Indications  of the threshold  of  Incipient  toxlclty  of
ethyl-p-nltrophenol   thlonebenzenephosphorate  (EPN)  and  malathlon  In  human
beings.  Toxlcol.  Appl.  Pharmacol.  4:  123-130.
U.S.  EPA.   1984.   Health
Prepared by the Office of
Criteria  and  Assessment
Waste, Washington,  DC.
         and Environmental  Effects Profile  for  Malathlon.
         Health  and  Environmental  Assessment, Environmental
        Office.   Cincinnati,  OH  for  the  Office  of  Solid
U.S.  EPA.   1990.    Integrated  Risk  Information  System  (IRIS).    Online.
Office  of  Health and  Environmental  Assessment,  Environmental Criteria  and
Assessment Office,  Cincinnati,  OH.
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Malelc anhydride
Jessup,  D.C.,   0.  Aldrldge,  G.L.   Schardeln  and  M.  Blair.    1982.   Three-
generation  reproduction  study  In  rats  (modified  to a  2-generatlon study).
Malelc  anhydride IR-79-358.   International  Research  and  Development  Corp.
for Monsanto Co., St.  Louis.  Mo.   Unpublished  8D submission.   Microfiche No.
OTS 0206655.  Document ID 878214777.

Preache,  M.   1983.    Chronic  Dietary  Administration  of  Malelc  Anhydride.
Vol.  1:  Narrative.   FYI-OTS Submission 1283-0277.   Prepared  by ITT Research
Institute  for  Chemical Industry Institute  of Technology,  Research Triangle
Park, NC.

U.S.  EPA.   1986.    Health  and  Environmental   Effects   Profile  for  Malelc
Anhydride.   Prepared  by  the  Office  of Health and  Environmental  Assessment,
Environmental Criteria and Assessment Office.  Cincinnati,  OH  for  the Office
of Solid Waste and Emergency Response, Washington, DC.

U.S.  EPA.   1990.    Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health and  Environmental  Assessment,  Environmental Criteria  and
Assessment Office.  Cincinnati, OH.

Malelc hydrazlde
U.S.  EPA.    1989.   Health  and  Environmental   Effects  Document  for  Malelc
Hydrazlde.   Prepared  by  the  Office  of Health and  Environmental  Assessment,
Environmental Criteria and Assessment Office,  Cincinnati,  OH  for  the Office
of Solid Waste and Emergency Response, Washington, DC.

U.S.  EPA.   1990.    Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health and  Environmental  Assessment,  Environmental Criteria  and
Assessment Office,  Cincinnati, OH.

Van der He 1.)den, C.A., E.M.  Den Tonkelaar, J.M.  Garbls-Berkvens and G.J.  Van
Esch.   1981.  Malelc  hydrazlde,  carclnogenlclty study  In rats.  Toxicology.
19(2): 139-150.

Malononltrlle
Panov, I., M. Zlateva and  G.  Antov.   1972.   Toxlcologlcal characteristics of
dlcyanomethane.    Chronic   effects   In  white  rats.   Khlg.  Zdraveopazvane.
15(6): 553-562.

U.S.  EPA.    1986.   Health  and  Environmental   Effects  Profile for  Malano-
nltrlle.   Prepared  by the Office  of Health  and  Environmental  Assessment,
Environmental Criteria and  Assessment Office,  Cincinnati,  OH  for  the Office
of Solid Waste and  Emergency Response, Washington,  DC.

Mancozeb
U.S.  EPA.   1984.   Health  and  Environmental  Effects  Profile  for  Mancozeb.
Prepared by the  Office of  Health and  Environmental  Assessment, Environmental
Criteria  and  Assessment  Office,   Cincinnati,  OH  for  the Office  of  Solid
Waste, Washington,  DC.

Maneb
Maneb Data Task  Force.  1986.  MRID No. 00161552.  (Cited In U.S.  EPA, 1987)

Rohm and Haas Co.  1977.   MRID No.  00129980.   (CHed In U.S. EPA,  1987)


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U.S.  EPA.   1984.    Health  and   Environmental  Effects  Profile  for  Maneb.
Prepared  by the Office of  Health  and  Environmental  Assessment, Environmental
Criteria  and  Assessment  Office,   Cincinnati.   OH  for  the  Office  of  Solid
Waste, Washington,  DC.
U.S.  EPA.    1990.    Integrated  Risk
Office  of  Health and  Environmental
Assessment Office, Cincinnati, OH.
                   Information
                   Assessment.
                      System  (IRIS).   Online.
                     Environmental  Criteria and
Manganese
Lai.  J.C.K..  T.K.C.  Leung  and  L. Urn.   1982.   Activities of  the mitochon-
dria!  NAD-1 Inked  IsocHMc  dehydrogenase  In  different  regions  of  the  rat
brain.  Changes In aging and  the  effect  of  chronic  manganese chloride admin-
istration.  Gerontology.  28(2): 81-85.

Laskey, J.W.,  G.L.  Rehnberg, J.F. Heln  and S.D. Carter.   1982.   Effects of
chronic  manganese  ^304)  exposure  on  selected  reproductive  parameters
In rats.  J. Toxlcol.  Environ. Health.  9: 677-687.

Leung,  T.K.C.,  J.C.K.  Lai  and  L.  Urn.  1981.  The  regional  distribution of
monoamlne  oxldase  activities towards  different substrates:  Effects  In  rat
brain  of  chronic  administration  of  manganese  chloride  and  of   aging.   J.
Neurochem.  36(6): 2037-2043.
Sarlc. M..  S.  Mark1cev1c  and  0.  Hrustlc.
manganese.  Br. J. Ind. Med.  34:  114-118.
                          1977.   Occupational  exposure to
U.S. EPA.  1984a.  Health Effects Assessment  for  Manganese.   Prepared by the
Office  of  Health and  Environmental Assessment.  Environmental  Criteria  and
Assessment Office, Cincinnati,  OH for the  Office of Emergency  and Remedial
Response, Washington. DC.   ECAO-CIN-H057.

U.S.  EPA.   1984b.   Health  Assessment Document  for  Manganese.   Prepared  by
the  Office  of  Health  and  Environmental  Assessment, Environmental  Criteria
and Assessment Office,  Cincinnati, OH.   EPA 600/8/83-013F.  NTIS PB84-229954.

Mephosfolan
U.S. EPA.  1984.   Health  and Environmental Effects  Profile  for  Mephosfolan.
Prepared by the Office of Health  and  Environmental  Assessment, Environmental
Criteria  and  Assessment  Office,   Cincinnati. OH  for  the  Office  of  Solid
Waste. Washington. DC.
Mercury. Inorganic
Andres,  P.   1984.
Ingesting mercuric
  IgA-IgG
chloride.
disease  In  the
 Clln. Immunol.
Intestine of  Brown
 Immunopathol.   20:
 Norway  rats
488-494.
Bernaudln,  J.F.,  E.  Druet.  P.  Druet and  R.  Masse.   1981.   Inhalation  or
Ingestlon of organic or Inorganic mercurials produces  auto-Immune disease In
rats.  Clln. Immunol.  Immunopathol.   20:  129-135.

Druet,  P.,   E.  Druet,   F.   Potdevln  and  C.   Sapln.    1978.    Immune  type
glomerulonephrltis  Induced  by   HgCl2  1n  the  Brown   Norway  rat.    Ann.
Immunol.  129C: 777-792.
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Fawer,  R.F.,   V.  DeR1baup1erre,  M.P.  Gulllemln,  M.   Berode and  M.  Lobe.
1983.  Measurement of hand tremor  Induced  by  Industrial exposure to metallic
mercury.  J. Ind.  Med.  40: 204-208.
P11k1v1,  L.   1989.
mercury vapor.  Int.
         Cardiovascular  reflexes  and  low  long-term  exposure to
        Arch. Occup. Environ. Health.  61: 391-395.
Pllklvl.  L.
performance
15: 69-74.
and  H.  Hannlnen.
of  chlorine-alkali
1989.  Subjective  symptoms and  psychloglcal
workers.   Scand.  J.  Work  Environ.  Health.
P11k1v1,  L.  and V.  Tolonen.   1989.   EEG findings  In  chlor-alkall  workers
subjected to low long-term exposure to mercury  vapor.   Br.  J. Ind. Med.  46:
370-375.

U.S.  EPA.   1984.   Health  Effects  Assessment for  Mercury.    Prepared  by  the
Office  of  Health and  Environmental  Assessment.  Environmental  Criteria  and
Assessment Office, Cincinnati,  OH for the Office of  Emergency  and  Remedial
Response, Washington. DC.
U.S.  EPA.   1987.   Peer
1987,  Summary  Report.
Cincinnati, OH.
            Review Workshop
              Environmental
         on Mercury  Issues.   October  26-27,
          Criteria   and  Assessment   Office,
U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health and  Environmental Assessment.  Environmental  Criteria  and
Assessment Office. Cincinnati. OH.
Herphos
Abou-Donla, M.B., D.G. Graham,  P.R.  Tlmmons
acute,  delayed  neurotoxlc  and  chollnerglc
phorotrlthlolte (merphos) In hens.   Toxlcol.
                                and  B.L.  Relchert.  1980.  Late
                                 effects   of  S.S.S-trlbutylphos-
                                Appl. Pharmacol.   53: 439-457.
U.S.  EPA.   1984.   Health  and  Environmental  Effects  Profile  for  Merphos.
Prepared by the Office of Health  and  Environmental  Assessment, Environmental
Criteria and  Assessment  Office,   Cincinnati,  OH  for  the  Office  of  Solid
Waste, Washington. DC.

U.S.  EPA.    1990.   Integrated   Risk   Information  System  (IRIS).    Online.
Office  of  Health and  Environmental  Assessment,  Environmental  Criteria  and
Assessment  Office. Cincinnati,  OH.
Merphos oxide
Abou-Donla, M.B..
neurotoxlc,  late
trlthloate (DEF):
14: 229-243.
      D.G.  Graham.  K.M.  Abdo and  A.A.  Komell.   1979.   Delayed
     acute and  chollnerglc effects  of  S,S,S-tr1butylphosphoro-
      Subchronlc  (90 days) administration  In hens.  Toxicology.
U.S.  EPA.    1984.   Health  and  Environmental   Effects   Profile  for  Merphos
Oxide.   Prepared  by  the  Office  of  Health  and  Environmental  Assessment,
Environmental Criteria and  Assessment  Office,  Cincinnati, OH  for  the Office
of Solid Waste,  Washington.  DC.
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U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office of  Health and  Environmental  Assessment.  Environmental Criteria  and
Assessment Office, Cincinnati, OH.

Methacrylonltrlle
Pozzanl,  U.C., C.R. Klnkead and J.M. King.   1968.   The mammalian  toxlclty of
methacrylonltrlle.  Am. Ind. Hyg.  Assoc.  J.   29(3): 202-210.

U.S.  EPA.   1987.   Health  and  Environmental  Effects  Document for  Selected
Nltrlles.   Prepared  by the Office of Health and  Environmental  Assessment,
Environmental Criteria  and  Assessment  Office. Cincinnati.  OH  for  the Office
of Solid  Waste and Emergency Response,  Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office of  Health and  Environmental  Assessment,  Environmental Criteria  and
Assessment Office, Cincinnati, OH.

Methanol
U.S.  EPA.   1986.   Rat  oral  subchronlc  toxlclty study  with  methanol.   Office
of Solid  Waste.  Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office of  Health and  Environmental  Assessment,  Environmental Criteria  and
Assessment Office. Cincinnati, OH.

Methorny!
Kaplan,  A.M.   and  H.   Sherman.    1977.    Toxldty   studies  with   methyl
N-[[(methylam1no)   carbonyl]   oxyl]   ethanlmldothloate.    Toxlcol.   Appl.
Pharmacol.  40(1): 1-17.

U.S.  EPA.   1986.   Integrated  Risk  Information System  (IRIS):  Reference Dose
(RfD)  for   Oral   Exposure   for   Methomyl.   Online.    (Verification  date
04/22/86.)   Office of  Health  and  Environmental  Assessment.  Environmental
Criteria  and Assessment Office, Cincinnati.  OH.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office of  Health and  Environmental  Assessment,  Environmental Criteria  and
Assessment Office, Cincinnati, OH.

Hethoxychlor
U.S.  EPA.    1984.   Health  and Environmental  Effects  Profile for  Methoxy-
chlor.   Prepared  by   the   Office  of  Health  and  Environmental  Assessment,
Environmental Criteria  and  Assessment  Office, Cincinnati.  OH  for  the Office
of Solid  Waste, Washington,  DC.

2-Methoxyethanol
Miller, R.R., L.L. Calhoun  and B.L.  Yano.   1982.   Ethylene  glycol  monomethyl
ether: 13-week  vapor  Inhalation  study  In male rabbits.   Report  prepared  for
the CMA March 25, 1982.

U.S.  EPA.   1984.   Health  Effects  Assessment for Glycol  Ethers.   Prepared by
the  Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria
and  Assessment  Office,   Cincinnati,  OH  for  'the  Office  of  Emergency  and
Remedial  Response, Washington, DC.
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U.S.  EPA.   1986.  Health  and Environmental  Effects  Profile  for  2-Methoxy-
ethanol.   Prepared  by  the Office  of Health  and Environmental  Assessment,
Environmental Criteria  and Assessment Office. Cincinnati. OH  for  the Office
of Solid Waste and Emergency Response, Washington, DC.

2-Methoxyethanol acetate
Miller, R.R.. L.L. Calhoun and B.L. Yano.   1982.   Ethylene glycol  monomethyl
ether: 13-week  vapor  Inhalation  study In male rabbits.   Report  prepared for
the Chemical Manufacturers Association, March 25,  1982.

U.S.  EPA.   1987.  Health  and Environmental  Effects  Profile  for  2-Methoxy-
ethanol Acetate.  Prepared by the Office of  Health and  Environmental Assess-
ment,  Environmental  Criteria  and Assessment  Office.  Cincinnati, OH  for the
Office of Solid Waste and Emergency Response, Washington, DC.

Methyl acetate
Toxlclty  Research Laboratory.   1986.   Rat  oral   subchronlc  toxlclty  study
with methanol.  Sponsored by Office of Solid Waste, U.S. EPA, Washington, DC.

U.S.  EPA.   1986.   Health and  Environmental  Effects   Profile  for  Methyl
Acetate.   Prepared  by  the Office  of Health  and Environmental  Assessment,
Environmental Criteria  and Assessment Office, Cincinnati, OH  for  the Office
of Solid Waste and Emergency Response, Washington, DC.

Methyl acrylate
Kllmlsch,  H.O.   and  W.  Relnlnghaus.   1984.   Carclnogenlclty of  acrylates:
Long-term  Inhalation  studies  on  methyl  acrylate  (MA)  and  n-butyl  acrylate
(BA) In rats.  lexicologist.  4(1):  53.  (Taken from Abstract No. 211)

U.S.  EPA.   1987.   Health and  Environmental  Effects   Profile  for  Methyl
Acrylate.   Prepared  by  the  Office of  Health and Environmental  Assessment,
Environmental Criteria  and Assessment Office, Cincinnati. OH  for  the Office
of Solid Waste and Emergency Response, Washington, DC.

Methyl chloride
U.S.  EPA.   1986.   Health and  Environmental  Effects   Profile  for  Methyl
Chloride.   Prepared  by  the  Office of  Health and Environmental  Assessment,
Environmental Criteria  and Assessment Office, Cincinnati. OH  for  the Office
of Solid Waste and Emergency Response. Washington, DC.

Methylchlorocarbonate
U.S.  EPA.   1989.   Health  and  Environmental  Effects  Document  for  Methyl-
chlorocarbonate.   Prepared   by  the   Office  of   Health  and  Environmental
Assessment,  Environmental  Criteria and Assessment  Office. Cincinnati. OH for
the Office of Solid Waste and  Emergency Response,  Washington, DC.

2-Methy1-4-ch1orophenoxy acetic  acid (MCPA)
Industry  Task  Force  on MCPA  Research  Data.   1986.    Confidential  Business
Information; unpublished study.   MRID No. 00164352.

U.S.  EPA.   1984.   Health and  Environmental  Effects Profile  for   MCPA and
MCPB.   Prepared  by   the  Office  of  Health  and  Environmental  Assessment,
Environmental Criteria  and Assessment Office. Cincinnati, OH  for  the Office
of Solid Waste, Washington, DC.
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U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health and  Environmental Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

4-(2-Methy1-4-ch1orophenoxy) butyric add (MCPB)
Rhodla,  Inc.   1970a.   Confidential  Business  Information;  unpublished study.
MRID No. 00116345.

Rhodla,  Inc.   1970b.   Confidential  Business  Information;  unpublished study.
MRID No. 00116344.

U.S.  EPA.   1984  .  Health and  Environmental  Effects Profile  for  MCPA  and
MCPB.   Prepared  by the   Office  of  Health  and  Environmental  Assessment,
Environmental Criteria and Assessment  Office. Cincinnati, OH  for  the Office
of Solid Waste, Washington. DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health and  Environmental Assessment,  Environmental  Criteria  and
Assessment Office. Cincinnati. OH.

2-(2-Methy1-4-ch1orophenoxv) proplonlc  acid (HCPP)
BASF  Aktlegerellschaft.    1985.   Confidential  Business   Information;  unpub-
lished study.  MRID No. 00158359.

U.S.  EPA.   1984.   Health  and  Environmental   Effects   Profile  for  MCPP.
Prepared by  the  Office of  Health  and Environmental  Assessment, Environmental
Criteria  and Assessment  Office,  Cincinnati,  OH  for  the  Office of  Solid
Waste, Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health and  Environmental Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

Methylcyclohexane
U.S.  EPA.   1984.   Health  and Environmental Effects  Profile  for  Methylcyclo-
hexane.   Prepared by  the  Office  of  Health and Environmental  Assessment,
Environmental Criteria and Assessment  Office. Cincinnati, OH  for  the Office
of Solid Waste, Washington, DC.

Methylene bromide
Keyes,  D.G.,  J.W. Henck.  G.C. Jersey.  R.J.  Koclba,  D.J.  Schwetz  and  T.D.
Landry.   1982.    Methylene  bromide: A  90-day  repeated   Inhalation  toxlclty
study  In  rats  and dogs with  a subsequent two-year  holding  period for  rats.
Toxicology  Research  Lab,  Health  and  Environmental  Sciences,  Dow  Chemical
Co., Midland. MI.

U.S.  EPA.   1987.   Health   and  Environmental  Effects  Profile for  Methylene
Bromide.   Prepared  by   the Office  of  Health and Environmental  Assessment,
Environmental Criteria  and Assessment  Office, Cincinnati, OH  for  the Office
of Solid Waste and Emergency Response,  Washington, DC.

Methylene chloride
National Coffee  Association.   1982.  24-Month Chronic Toxlclty  and  Oncogen-
Iclty  Study  of  Methylene  Chloride In  Rats.   Final Report.   Prepared  by
Hazleton Laboratories America, Inc., Vienna,  VA.  (Unpublished).


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NUschke, K.D., J.D.  Bured.  T.J.  Bell,  et al.   1988.   Methylene chloride:  A
2-year  Inhalation  toxlclty  and  oncogenldty study  1n  rats.   Fund.  Appl.
Toxlcol.  (In press)

U.S.  EPA.   1989.   Updated  Health Effects Assessment  for  Methylene Chloride.
Prepared by  the Office of  Health  and  Environmental  Assessment,  Environmental
Criteria and  Assessment  Office, Cincinnati,  OH  for the  Office  of Emergency
and Remedial Response, Washington, DC.

U.S.  EPA.   1990.   Integrated Risk  Information System  (IRIS).   Online. Office
of   Health   and   Environmental  Assessment.   Environmental   Criteria   and
Assessment Office,  Cincinnati,  OH.

4.4'-Methy1ened1phenyl Isocyanate
U.S.  EPA.   1985.    Health  and  Environmental  Effects  Profile  for  4,4'-
Methylenephenyl Isocyanate.  Prepared by the Office  of  Health  and  Environ-
mental Assessment, Environmental  Criteria and Assessment  Office, Cincinnati,
OH for the Office of  Solid  Waste and Emergency Response, Washington,  DC.

Methyl mercury
Clarkson, T.W.,  L.  Am1n-Zak1  and S.K.  Al-T1kr1t1.  1976.   Federation  Pro-
ceedings.  35(12):  2395-2399.

Nordberg,  G.F. and  P.  Strangert.    1976.    Estimations  of  a  dose-response
curve  for   long-term  exposure   to  methylmercurlc compounds   In  human beings
taking   Into   account  variability  of  critical   organ   concentration  and
biological   half-time:   A  preliminary   communication.    In.:   Effects  and
Dose-Response  Relationships  of  Toxic  Metals.  G.F. Nordberg, Ed.   Elsevler,
Amsterdam,  p. 273-282.

U.S.  EPA.   1980.    Ambient  Water  Quality   Criteria   Document   for  Mercury.
Prepared by  the Office of  Health  and  Environmental  Assessment,  Environmental
Criteria  and  Assessment  Office,  Cincinnati, OH   for  the Office of  Water
Regulations  and  Standards,  Washington,  DC.   EPA-440/5-80-058.   NTIS  PB
81-117699.

U.S.  EPA.   1984.   Health  Effects  Assessment  for  Mercury.   Prepared  by  the
Office  of  Health  and Environmental  Assessment,  Environmental  Criteria  and
Assessment  Office, Cincinnati,  OH for the  Office   of  Emergency  and  Remedial
Response, Washington, DC.

U.S.  EPA.    1990.   Integrated   Risk  Information  System  (IRIS).   Integrated
Risk  Information System  (IRIS).  Online. Office of Health and Environmental
Assessment, Environmental Criteria and Assessment Office,  Cincinnati, OH.

WHO  (World  Health  Organization).   1976.   Environmental  health  criteria  for
mercury.  ln_:  Environmental Health Criteria 1.  WHO,  Geneva.

Methyl ethyl ketone
LaBelle. C.W.  and  H.  Brleger.   1955.  Vapour  toxlclty of  a composite solvent
and  Us principal components.  Arch. Ind. Health.   12: 623-627.
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U.S.  EPA.   1984.    Health  Effects  Assessment  for  Methyl  Ethyl  Ketone.
Prepared by the Office of  Health  and  Environmental  Assessment, Environmental
Criteria and Assessment  Office.  Cincinnati, OH  for the Office  of  Emergency
and Remedial Response, Washington, DC.

U.S. EPA.   1985.   Integrated Risk Information System  (IRIS):  Reference Dose
(RfD)  for  oral  exposure  for  methyl  ethyl  ketone.   Online.   (Verification
date  07/08/85).   Office  of  Health  and  Environmental Assessment,  Environ-
mental Criteria and Assessment Office, Cincinnati, OH.

U.S.  EPA.   1989.    Updated  Health  Effects  Assessment  for  Methyl  Ethyl
Ketone.   Prepared  by  the  Office of  Health  and  Environmental  Assessment,
Environmental  Criteria and Assessment Office,  Cincinnati, OH  for  the Office
of Emergency and Remedial Response, Washington. DC.

U.S.  EPA.   1990.   Integrated Risk  Information  System (IRIS).   Integrated
Risk Information System  (IRIS).   Online.  Office  of  Health  and Environmental
Assessment, Environmental Criteria and Assessment Office, Cincinnati, OH.

Methyl Isobutyl ketone
Microbiological Associates.   1986.  Subchronlc  toxlclty of  methyl  Isobutyl
ketone  In Sprague-Dawley  rats.    Preliminary  report  for  Research  Triangle
Institute, RTP, NC.   Study No. 5221.04.   January.

Union  Carbide  Corp.   1983.   Ninety-day  Inhalation  study  In  rats   and  mice
sponsored by CMA.   U.S.  EPA/OTS public files 0750507469.

U.S.  EPA.   1987.    Health  Effects  Assessment  for  Methyl  Ethyl  Ketone.
Prepared by the Office of  Health  and  Environmental  Assessment, Environmental
Criteria and Assessment  Office,  Cincinnati. OH  for the Office  of  Emergency
and Remedial Response. Washington. DC.

U.S.  EPA.   1989.    Updated  Health  Effects  Assessment  for  Methyl  Ethyl
Ketone.    Prepared  by  the  Office  of Health  and  Environmental  Assessment,
Environmental  Criteria and Assessment Office,  Cincinnati, OH  for  the Office
of Emergency and Remedial Response, Washington, DC.

U.S.  EPA.   1990.    Integrated  Risk   Information  System  (IRIS).    Online.
Office  of  Health and  Environmental   Assessment.  Environmental  Criteria  and
Assessment Office,  Cincinnati, OH.

Methyl Isocvanate
U.S.  EPA.   1986.    Health  and   Environmental   Effects  Profile  for  Methyl
Isocyanate.  Prepared by  the Office of Health and  Environmental Assessment,
Environmental  Criteria and Assessment Office.  Cincinnati. OH  for  the Office
of Solid Waste  and  Emergency Response, Washington, DC.

Methyl methacrylate
Borzelleca, J.F., P.S. Larson. G.R. Hennlgar,  et al.   1964.   Studies on the
chronic oral toxlclty of  monomerlc ethyl  acrylate and  methyl methacrylate.
Toxlcol. Appl.  Pharmacol.  6: 29-36.
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U.S. EPA.  1985.  Health  and  Environmental  Effects Profile  for  Methyl  Meth-
acrylate.  Prepared  by the  Office of  Health  and  Environmental  Assessment,
Environmental Criteria and  Assessment  Office,  Cincinnati, OH  for  the Office
of Solid Waste and Emergency Response,  Washington, DC.

Methyl  parathlon
Monsanto  Co.   1983.   Accession  No.   252501-252503,  253346,  253372-253374.
U.S. EPA, Washington, DC.

U.S.  EPA.   1984.    Health  and   Environmental  Effects  Profile  for  Methyl
Parathlon.   Prepared  by  the Office of Health and  Environmental  Assessment,
Environmental Criteria and  Assessment  Office,  Cincinnati, OH  for  the Office
of Solid Waste,  Washington,  DC.

U.S.  EPA.   1990.   Integrated   Risk   Information  System  (IRIS).    Online.
Office  of  Health and  Environmental  Assessment,  Environmental Criteria  and
Assessment Office, Cincinnati,  OH.

Methyl  styrene
MRI  (Midwest  Research  Institute).  1984a.   Study of  the  Inhalation carclno-
genlcUy  (bloassay)  of  vinyl  toluene  In B6C3F1  mice.  Final  chronic report
performed for the NTP under  Contract  No. N01-ES-38042.

U.S.  EPA.   1987.   Health  and  Environmental   Effects  Document  for  Methyl
Styrenes.  Prepared  by the  Office of  Health  and  Environmental  Assessment,
Environmental Criteria and  Assessment  Office,  Cincinnati, OH  for  the Office
of Solid Waste and Emergency Response,  Washington, DC.

Hethylstyrene. alpha
U.S. EPA.  1987.  Health and Environmental  Effects  Profile for alpha-Methyl-
styrene.   Prepared  by  the  Office  of   Health  and  Environmental  Assessment,
Environmental Criteria and  Assessment  Office,  Cincinnati, OH  for  the Office
of Solid Waste,  Washington,  DC.

Wolf.  M.A.,   V.K.   Rowe,  D.D.  McColllster,  et  al.   1956.   Toxlcologlcal
studies of certain  alkylated benzenes  and  benzene.   Arch. Ind.  Health.   14:
387-398.

Mlrex
Shannon, V.C.   1976.   The effects of  ml rex on the  reproductive  performance
and  behavioral   development  1n   the   prairie  vole   (Mlcrotus  ochrogaster).
Ph.D. Dissertation,  Iowa  State  University,  Ames,  IA.

U.S. EPA.    1987.   Health  Effects  Assessment  for  Mlrex.   Prepared by  the
Office  of  Health and  Environmental  Assessment,  Environmental Criteria  and
Assessment Office,  Cincinnati.  OH for   the  Office of Emergency  and Remedial
Response. Washington, DC.

U.S.  EPA.   1990.   Integrated   Risk   Information  System  (IRIS).    Online.
Office  of  Health and  Environmental  Assessment,  Environmental Criteria  and
Assessment Office, Cincinnati,  OH.

Mollnate
Stauffer Chemical Company.  1981.  MRID No. 00079209.  U.S.  EPA.  Washington,
DC.


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U.S.  EPA.   1984.   Health and  Environmental Effects  Profile  for  Mollnate.
Prepared by the  Office of  Health  and  Environmental  Assessment. Environmental
Criteria  and  Assessment  Office,   Cincinnati.  OH  for  the  Office  of  Solid
Waste, Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk   Information  System  (IRIS).    Online.
Office  of  Health and  Environmental Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati,  OH.

Monochlorobutane
NTP  (National  Toxicology  Program).   1986.   Toxicology  and  cardnogenesls
studies  of  n-butyl  chloride  In  F344/N   rats  and   B6C3F1   mice  (gavage
studies).  (CAS No.  109-69-3).   NTP TR-312.

U.S.  EPA.   1989.  Health  and Environmental   Effects  Document  for Monochloro-
butanes.   Prepared  by  the Office  of Health  and Environmental  Assessment,
Environmental  Criteria and Assessment  Office,  Cincinnati, OH  for  the Office
of Solid Waste and Emergency  Response,  Washington, DC.

Naphthalene
Schmahl,  D.   1955.   Testing  of  naphthalene and  anthracene as  carcinogenic
agents  In  the  rat.   Z.  Krebsforsch.   60:  697-710.   (German  with  English
translation)

U.S.  EPA.   1986.  Health  and Environmental   Effects  Profile  for Naphthalene.
Prepared by the  Office of  Health  and  Environmental  Assessment, Environmental
Criteria and Assessment Office, Cincinnati.  OH for  the  Office  of Solid Waste
and Emergency  Response,  Washington, DC.

U.S.  EPA.   1988.  Health  Effects Assessment  for  Naphthalene.  Prepared  by
the  Office of Health  and Environmental  Assessment, Environmental  Criteria
and  Assessment   Office,  Cincinnati,  OH  for  the Office  of  Emergency  and
Remedial Response, Washington,  DC.

1.4-Naphthoqulnone
U.S.  EPA.   1986.  Health  and Environmental   Effects  Profile  for 1,4-Naphtho-
qulnone.   Prepared  by  the Office  of  Health  and Environmental  Assessment,
Environmental  Criteria and Assessment  Office,  Cincinnati, OH  for  the Office
of Solid Waste and Emergency  Response,  Washington, DC.

Nickel
Ambrose, A.M.,  D.S.  Larson,  J.R.  Borzelleca and 6.R.  Hennlgar, Jr.   1976.
Long-term  toxlcologlc assessment  of nickel   In rats  and dogs.   J.  Good Scl.
Technol.  13:  181-187.

U.S.  EPA.   1984.  Health  Effects Assessment  for Nickel.   Prepared by  the
Office  of  Health and  Environmental Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati,  OH for the Office  of Emergency  and  Remedial
Response. Washington,  DC.

U.S.  EPA.   1990.   Integrated Risk   Information  System  (IRIS).    Online.
Office  of  Health and  Environmental Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati,  OH.
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Nlcotlnonltrlle
U.S.  EPA.   1987.   Health  and  Environmental  Effects  Document for  Selected
NUMles.  Prepared  by the  Office of  Health  and Environmental  Assessment,
Environmental Criteria and Assessment  Office,  Cincinnati, OH  for  the  Office
of Solid Waste and Emergency  Response,  Washington. DC.
Nitric oxide
U.S. EPA.  1990.
of   Health   and
Assessment Office,
Integrated Risk Information
Environmental   Assessment,
Cincinnati, OH.
System (IRIS).
 Environmental
Online. Office
 Criteria   and
Walton. G.  1951.  Survey of  literature  relating  to  Infant methemogloblnemla
due to nitrate-contaminated  water.   Am.  J.  Public  Health.   41: 986-996.

Nitrite
U.S.  EPA.   1989.   Health  and  Environmental  Effects  Document for  Nitrite.
Prepared by the Office of Health and  Environmental Assessment, Environmental
Criteria and Assessment Office, Cincinnati, OH for the  Office of  Solid  Waste
and Emergency Response, Washington,  DC.
U.S. EPA.  1990.
of   Health   and
Assessment Office,
Integrated Risk Information
Environmental   Assessment,
Cincinnati, OH.
System (IRIS).
 Environmental
Online. Office
 Criteria   and
Walton, G.  1951.  Survey of  literature  relating  to  Infant methemogloblnemla
due to nitrate-contaminated  water.   Am.  J.  Pub.  Health.   41: 986-996.

Nltroanlllnes
U.S. EPA.  1985.  Health and  Environmental Effects Profile for  Nltroanlllnes
(o-. m-,  p-).   Prepared by  the Office  of  Health and  Environmental  Assess-
ment,  Environmental  Criteria  and Assessment  Office.  Cincinnati, OH  for  the
Office of Solid Waste and Emergency  Response,  Washington, DC.

Nitrobenzene
CUT (Chemical  Industry  Institute of Toxicology).  1984.  Ninety-day  Inhala-
tion study of nitrobenzene In F-344 rats. CD  rats  and B6C3F1 mice with cover
letter  dated  6/24/84  and  EPA  response dated  8/06/84.   Unpublished  study.
FYI-OTS-0784-0333 and computer print-out of  pathology finding.

U.S. EPA.   1987.   Health Effects Assessment  for  Nitrobenzene.   Prepared  by
the  Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria
and  Assessment  Office.  Cincinnati,  OH  for  the  Office   of  Emergency  and
Remedial Response, Washington, DC.

U.S.  EPA.   1990.   Integrated   Risk   Information  System  (IRIS).    Online.
Office  of  Health and  Environmental  Assessment,  Environmental   Criteria  and
Assessment Office, Cincinnati, OH.
Nltrofurantoln
SRI  (Southern Research  Institute).   1980.
Nltrofurantoln (C55196)  1n  F1scher-344  rats
Inc. Rockvllle. MD contract  Nos  N01-CP-43350
                            Subchronlc  Toxlclty  Report on
                           and B6C3F1  mice  Tracer Jit CO,
                          and 78-65-106002  U.S.  EPA.
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U.S.  EPA.   1987.   Health and Environmental Effects  Document  for NHrofurans
Prepared by  the Office of  Health  and  Environmental  Assessment, Environmental
Criteria and Assessment  Office, Cincinnati, OH  for  the Office of Solid Waste
and Emergency Response, Washington, DC.

Nitrogen dioxide
Kubota, K., M. Murakami, S.  Takenaka,  K.  Kawal  and  H.  Kyono.   1987.  Effects
of   long-term  nitrogen   dioxide  exposure   on   rat   lung   morphological
observations.  Environ. Health Perspect.   73(0): 157-169.

Sagal,  H.   and  T.  Ichlnose.   1987.   Llpld-peroxldatlon and  antloxldatlve
protection  mechanism  In  rat  lungs   upon  acute  and  chronic  exposure  to
nitrogen-dioxide.   Environ. Health Perspect.   73: 179-189.

Sagal,  M..  T.  Ichlnose  and  K.  Kubota.   1984.   Studies on  the biochemical
effects  of  nitrogen  dioxide.  IV.   Relation  between the  change of  llpld
peroxldatlon and the  antloxldatlve protective system  In  rat  lungs  upon life
span  exposure  to  low  levels  of  NOp.   Toxlcol.   Appl.  Pharmacol.   73(3):
444-456.

U.S.  EPA.    1990a.    Integrated  Risk  Information   System  (IRIS).   Online.
Office  of  Health  and  Environmental Assessment,  Environmental  Criteria  and
Assessment Office.  Cincinnati, OH.

U.S.  EPA.   1990b.   Health  and Environmental  Effects  Document  for  Nitrogen
Dioxide.   Prepared  by  the  Office  of Health  and  Environmental  Assessment,
Environmental Criteria and  Assessment  Office, Cincinnati, OH  for  the Office
of Solid Waste and  Emergency Response,  Washington,  DC.

Walton, G.  1951.   Survey of  literature  relating to Infant  methemogloblnemla
due to nitrate-contaminated water.  Am. J. Public Health.  41: 986-996.

Nitrogen oxides
U.S.  EPA.   1982.   Air Quality  Criteria   for  Oxides of Nitrogen.   Office  of
Health  and  Environmental Assessment,   Research  Triangle Park, NC.  EPA 600/
8-82-026F.   NTIS PB83-163337.

Nltromethane
U.S.  EPA.    1985.   Health   and  Environmental   Effects  Profile  for   Nltro-
methane.   Prepared  by  the  Office  of  Health  and  Environmental  Assessment,
Environmental Criteria and  Assessment  Office, Cincinnati, OH  for  the Office
of Solid Waste and  Emergency Response,  Washington.  DC.

NUrophenols
U.S.  EPA.   1987.   Health Effects  Assessment  for Nltrophenols.   Prepared  by
the Office  of Health  and   Environmental  Assessment,  Environmental Criteria
and  Assessment  Office.  Cincinnati,  OH   for   the   Office  of  Emergency  and
Remedial Response,  Washington, DC.

p-N1trosod1phenylam1ne
U.S.  EPA.    1986.   Health  and  Environmental  Effects  Profile  for  Nltros-
amlnes.  Prepared  by  the   Office of  Health  and  Environmental  Assessment,
Environmental Criteria and  Assessment  Office, Cincinnati, OH  for  the Office
of Solid Waste and  Emergency Response,  Washington.  DC.
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NUrotoluenes
Clss, M., N. Huyen, H. Dutertre, N.  Phu-Llch  and  R.  Truhaut.  1980.  Toxlco-
loglcal  study  of  nUrotoluenes:  Long-term  toxlclty.   Dakar  Medical.   25:
293-302.

U.S. EPA.  1986.  Health and  Environmental Effects  Profile for NUrotoluenes
(o-. m-,  p-).   Prepared by  the Office  of  Health and  Environmental  Assess-
ment.  Environmental  Criteria  and Assessment  Office,  Cincinnati, OH  for  the
Office of Solid Waste and Emergency  Response,  Washington, DC.

Octabromodlphenyl ether
Carlson,  G.P.   1980.   Induction of  xenoblotlc metaollsm  In rats  by  broml-
nated dlphenyl  ethers administered  for 90 days.  Toxlcol. Lett.  6:207-212.

U.S. EPA.   1983.  Health  and Environmental  Effects  Profile  for  Bromlnated
Dlphenyl Ethers.  Prepared by the Office of Health  and  Environmental  Assess-
ment,  Environmental  Criteria  and Assessment  Office,  Cincinnati, OH  for  the
Office of Solid Waste. Washington,  DC.

U.S.  EPA.   1990.   Integrated   Risk  Information  System  (IRIS).    Online.
Office  of  Health and  Environmental   Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

Octamethylpyrophosphoramlde
Rider.  J.A., H.C. Moeller. E.J. Pulettl and J.I.  Swader.  1969.   Toxldty of
parathlon, systox, Octamethylpyrophosphoramlde and  methyl parathlon  In  man.
Toxlcol. Appl.  Pharmacol.  14(3): 603-611.

U.S. EPA.   1989.   Health and  Environmental  Effects Document  for Octamethyl-
pyrophosphoramlde.   Prepared  by  the Office  of  Health  and  Environmental
Assessment, Environmental Criteria and Assessment Office,  Cincinnati,  OH for
the Office of Solid Waste and  Emergency Response,  Washington, DC.

Ozone and other photochemical  oxldants
U.S. EPA.   1986.  Air  Quality  Criteria  for   Ozone  and Other  Photochemical
Oxldants.  Office of  Health  and Environmental Assessment,  Research Triangle
Park, NC.  EPA 600/8-84-020F.   NTIS  PB87-142949.

Paraldehyde
U.S. EPA.   1986.   Health and  Environmental  Effects Profile  for  Paraldehyde.
Prepared by the Office of Health and  Environmental  Assessment, Environmental
Criteria and Assessment Office,  Cincinnati,  OH for  the  Office  of Solid Waste
and Emergency Response, Washington,  DC.

Parathlon
U.S. EPA.  1987.  Health Effects Assessment  for Parathlon.  Prepared  by  the
Office  of  Health and  Environmental   Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati,  OH  for the Office  of Emergency  and Remedial
Response, Washington,  DC.

Partlculate matter and sulfur  oxides
U.S. EPA.   1986.  Air  Quality  Criteria  for   Partlculate  Matter and  Sulfur
Oxides.   Office  of  Health and  Environmental  Assessment.  Research  Triangle
Park, NC.  EPA 600/8-82-029F.  NTIS  PB84-156777.
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Pebulate
U.S.  EPA.   1984.   Health and  Environmental  Effects  Profile  for  Pebulate.
Prepared by the  Office  of  Health  and  Environmental Assessment, Environmental
Criteria  and  Assessment  Office,  Cincinnati,   OH  for  the  Office  of  Solid
Waste, Washington, DC.
Pendlmethalln
American Cyanamld Company.   1979.
llshed study.  HRID No. 0058657.
          Confidential Business Information; unpub-
U.S.  EPA.   1984.  Health  and Environmental  Effects Profile  for  Pendlmeth-
alln.   Prepared  by   the   Office  of  Health  and  Environmental  Assessment,
Environmental Criteria  and Assessment  Office, Cincinnati,  OH  for  the Office
of Solid Waste. Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health and  Environmental Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati. OH.
Pentabromodlphenyl ether
Carlson, G.P.   1980.   Induction  of  xenoblotlc
nated dlphenyl ethers  administered for 90 days.
                       metaollsm In  rats  by broml-
                       Toxlcol. Lett.  6:207-212.
U.S.  EPA.   1983.  Health  and Environmental  Effects Profile  for  Bromlnated
Dlphenyl Ethers.  Prepared by the Office of  Health and  Environmental Assess-
ment, Environmental  Criteria  and Assessment  Office, Cincinnati, OH  for  the
Office of Solid Waste, Washington,  DC.

U.S.  EPA.   1990.   Integrated   Risk  Information  System  (IRIS).    Online.
Office  of  Health and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

Pentachlorobenzene
Linden,   R..   T.   Scott.1,  J.   Goldstein  and  K.  McElroy.   1980.   Acute  and
subchronlc  toxlclty   of  pentachlorobenzene.   J.   Environ.  Pathol.  Toxlcol.
4(5-6):  183-196.

U.S. EPA.  1989.  Health and  Environmental  Effects Document for Pentachloro-
benzene.   Prepared  by  the  Office  of Health  and  Environmental  Assessment,
Environmental Criteria and Assessment Office, Cincinnati,  OH  for  the Office
of Solid Waste and Emergency  Response. Washington, DC.

U.S.  EPA.   1990.   Integrated   Risk  Information  System  (IRIS).    Online.
Office  of  Health and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

Pentachlorocyclopentadlene
U.S. EPA.  1988.   Health  and  Environmental Effects  Document  for Chlorinated
Cyclopentadlenes.   Prepared   by   the  Office  of  Health  and  Environmental
Assessment, Environmental  Criteria  and Assessment  Office,  Cincinnati, OH  for
the Office of Solid Waste  and  Emergency  Response,  Washington,  DC.
Pentachloronltrobenzene
Olln Corporation.   1968.
MRID NO. 000114201.  U.S. EPA. Washington. DC.
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U.S.  EPA.   1986.   Health and Environmental  Effects  Profile for Pentachloro-
nltrobenzene.   Prepared by  the Office  of  Health and  Environmental Assess-
ment.  Environmental  Criteria and  Assessment Office, Cincinnati,  OH for  the
Office of Solid Waste and Emergency Response, Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System   (IRIS).   Online.
Office  of  Health  and   Environmental  Assessment.  Environmental  Criteria  and
Assessment Office, Cincinnati. OH.

Pentachlorophenol
Schwetz, B.A.,  J.F.  Quast,  P.A.  Keeler  et  al.  1978.   Results of two-year
toxlclty and  reproduction  studies on pentachlorophenol  In  rats.  Iji: Penta-
chlorophenol:  Chemistry,  Pharmacology  and   Environmental   Toxicology,  K.R.
Rao, Ed.  Plenum Press, New York.  p. 301.   (Cited 1n U.S. EPA.  1985)

U.S.  EPA.   1984.   Health Effects  Assessment  for Pentachlorophenol.  Prepared
by  the  Office of  Health and  Environmental Assessment, Environmental Criteria
and  Assessment   Office, Cincinnati,  OH  for  the  Office  of   Emergency   and
Remedial Response, Washington, DC.

U.S.  EPA.   1986.   Health and Environmental  Effects  Profile for Pentachloro-
phenol.   Prepared by   the  Office  of  Health  and Environmental Assessment,
Environmental Criteria  and  Assessment Office,  Cincinnati,  OH  for  the Office
of Solid Waste and Emergency Response, Washington, DC.

U.S.  EPA.    1990.   Integrated   Risk  Information  System   (IRIS).   Online.
Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office. Cincinnati, OH.

1.1.2.3.3-Pentachloropropene
U.S.  EPA.   1983.  Health  and  Environmental  Effects Profile  for  Chloropro-
penes.   Prepared  by   the  Office  of  Health  and Environmental  Assessment,
Environmental Criteria  and  Assessment Office,  Cincinnati,  OH  for  the Office
of Solid Waste,  Washington,  DC.

n-Pentane
U.S. EPA.   1987.   Health Effects  Assessment  for  n-Pentane.   Prepared  by  the
Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment  Office, Cincinnati.  OH for the Office of Emergency and Remedial
Response. Washington.  DC.

Phenanthrene
U.S.  EPA.   1984.   Health Effects  Assessment for Phenanthrene.   Prepared  by
the  Office  of  Health  and  Environmental  Assessment, Environmental  Criteria
and  Assessment   Office,  Cincinnati,  OH  for  the Office  of   Emergency   and
Remedial Response, Washington. DC.

U.S.  EPA.    1987.   Health  and   Environmental  Effects   Profile for  Phenan-
threne.  Prepared  by  the   Office of  Health  and Environmental  Assessment,
Environmental Criteria  and  Assessment  Office, Cincinnati,  OH  for  the  Office
of Solid Waste and Emergency Response, Washington, DC.

Phenol
Research Triangle  Institute.  1983.   Teratologlc Evaluation of  Phenol  In  CD
Rats.  Report prepared  for  NIEHS/NTP,  Research Triangle  Park, NC.


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U.S.  EPA.   1984.   Health  Effects Assessment  for  Phenol.   Prepared  by  the
Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office,  Cincinnati,  OH for  the  Office of  Emergency  and Remedial
Response. Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

Phenylenedlamlnes (o-.  p-)
U.S.  EPA.   1985.   Health  and Environmental  Effects  Profile  for  Phenylene-
dlamlnes  (o-,  m-,  p-).   Prepared by  the Office  of  Health  and Environmental
Assessment, Environmental Criteria and  Assessment Office.  Cincinnati.  OH for
the Office of Solid Waste and Emergency Response, Washington, DC.

m-Phenylenedlamlne
Hofer, H.  and  R.  Hruby.   1982.  Ninety-day toxlclty  study  with m-phenylene-
dlamlne on rats.   Oestrr. Forschungszent. Selbersdorf (Ber.)   OEFZS Ber.  No.
4155.  p. 50.

U.S.  EPA.   1985.   Health  and Environmental  Effects  Profile  for  Phenylene-
dlamlnes  (o-,  m-,  p-).   Prepared by  the Office  of  Health  and Environmental
Assessment, Environmental Criteria and  Assessment Office,  Cincinnati,  OH for
the Office of Solid Waste and Emergency Response, Washington. DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

Phenylmercurlc acetate
Fltzhugh, Q.G., A.A. Nelson,  E.P.  Laug and I.H.  Kunze.   1950.  Chronic oral
toxldtles of  mercuric   phenyl and mercuric  salts.   Arch. Ind.  Hyg.  Occup.
Hed.  2: 433-442.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

2-Phenylphenol
U.S.  EPA.   1984.   Health  and  Environmental  Effects  Profile  for  2-Phenyl-
phenol.   Prepared  by  the  Office of  Health and Environmental  Assessment,
Environmental Criteria and  Assessment  Office,  Cincinnati,  OH  for  the  Office
of Solid Waste, Washington.  DC.

Phosgene
U.S.  EPA.   1984.   Health  and  Environmental  Effects  Profile  for  Phosgene.
Prepared by the Office of Health  and  Environmental  Assessment, Environmental
Criteria  and  Assessment  Office, Cincinnati,  OH for  the Office  of  Solid
Waste, Washington, DC.

Phosphlne
Hackenberg, J.   1972.   Chronic  Ingestlon  by  rats  of standard  diet  treated
with aluminum phosphide.   Toxlcol. Appl. Pharmacol.   23:  147-158.
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Kllmmer.  O.R.    1969.   Contribution  to  the  study  of  action  of  phosphlne
(PH3).   On  the  question of  so-called chronic  phosphlne  poisoning.   Arch.
Toxlcol.  24:  164-187.

U.S.  EPA.   1989.  Health and  Environmental  Effects Document  for  Phosphlne.
Prepared by  the  Office  of Health  and  Environmental  Assessment,  Environmental
Criteria and Assessment Office, Cincinnati, OH  for  the Office of  Solid Waste
and Emergency Response, Washington, DC.

Phthallc acid esters, selected
U.S.  EPA.    1987.    Health   Effects   Assessment  for   Phthallc  Acid  Esters.
Prepared by  the  Office  of Health  and  Environmental  Assessment,  Environmental
Criteria and Assessment Office,  Cincinnati, OH  for the Office of  Emergency
and Remedial Response. Washington, DC.

Phthallc adds
U.S.  EPA.    1986.   Health  and Environmental  Effects  Profile  for  Phthallc
Adds.   Prepared  by  the  Office  of   Health  and   Environmental  Assessment,
Environmental Criteria  and  Assessment Office,  Cincinnati,  OH for  the  Office
of Solid Waste  and Emergency Response, Washington,  DC.

p-Phtha11c add
CUT  (Chemical  Industry Institute  of  Technology).   1982.   A Ninety-Day Study
of  Terephthallc  Acid-Induced  Urollthlasls  and  Reproductive Performance  In
Wlstar and CD rats.  CUT.  Research Triangle Park,  NC.

Gross,  J.   1974.   The Effects  of Prolonged  Feeding  of   Terephthallc  Add
(TPA)  to  Rats.    Project  FG-IS-175.    Agricultural Research  Service,  U.S.
Department of Agriculture,  Washington, DC.

U.S.  EPA.    1986.   Health  and Environmental  Effects  Profile  for  Phthallc
Adds  (o-,  m-,  p-).   Prepared  by the  Office  of  Health  and  Environmental
Assessment, Environmental Criteria and Assessment Office,  Cincinnati,  OH for
the Office of Solid Waste and Emergency Response. Washington, DC.

Phthallc anhydride
NCI  (National Cancer  Institute).   1979.   Bloassay   of  phthallc  anhydride for
possible cardnogenldty.  NCI Carclnogenesls Tech. Rep. Ser. No.  159.   NTIS
PB293594.

U.S.  EPA.   1986.   Health  and Environmental  Effects  Profile  for  Phthallc
Anhydride.   Prepared  by the Office of  Health  and  Environmental  Assessment,
Environmental Criteria  and  Assessment Office,  Cincinnati.  OH for  the  Office
of Solid Waste  and Emergency Response, Washington.  DC.

U.S.  EPA.    1990.    Integrated  Risk   Information   System  (IRIS).   Online.
Office  of  Health  and  Environmental   Assessment, Environmental  Criteria  and
Assessment  Office,  Cincinnati,  OH.

Polybromlnated  blphenyls
NTP  (National Toxicology  Program).   1983.  Carclnogenesls studies of  poly-
bromlnated  blphenyl mixture  In F344/N rats and B6C3F1  mice (gavage  studies).
Flremaster  FF-1.   Case No. 67774-32-7.  NTP, Research  Triangle Park,  NC.
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U.S.  EPA.   1989.  Health  and  Environmental Effects  Document  for Polybroml-
nated Blphenyls.  Prepared by  the  Office  of Health and Environmental Assess-
ment, Environmental  Criteria and  Assessment  Office, Cincinnati,  OH for the
Office of Solid Waste and Emergency Response, Washington, DC.

Potassium cyanide
Howard.   J.W.  and  R.F.   Hanzal.   1955.   Chronic  toxlclty  for  rats  of  food
treated with hydrogen cyanide.   Agrlc. Food Chem.  3: 325-329.

Phllbrlck,  D.J.,  J.B.  Hopkins, D.C.  Hill,  J.C. Alexander  and  R.G.  Thomson.
1979.   Effects  of prolonged cyanide  and thlocyanate  feeding  In  rats.   J.
Toxlcol. Environ. Health.  5: 579-592.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati,  OH.
Potassium silver cyanide
Howard,  J.W.  and  R.F.  Hanzal.   1955.  Chronic  toxlclty  for
treated with hydrogen cyanide.  Agrlc. Food Chem.  3: 325-329.
                                    rats  of  food
Phllbrlck. D.J.,  J.B.  Hopkins, D.C. H111.
1979.   Effects  of  prolonged  cyanide and
Toxlcol. Environ. Health.  5:  579-592.
               J.C.  Alexander  and R.G.  Thomson.
               thlocyanate  feeding  In  rats.   J.
U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health and  Environmental Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

Profluralln
U.S. EPA.   1984.   Health and Environmental Effects  Profile  for Profluralln.
Prepared by the Office of  Health  and Environmental  Assessment, Environmental
Criteria  and  Assessment  Office,  Cincinnati,   OH  for  the  Office of  Solid
Waste, Washington, DC.

Pronamlde
Rohm & Haas. Co.  1970.   Ace. Nos. 000967, 004417.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health and  Environmental Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.
Propachlor
Monsanto  Company.    1964.
Study.  MRID NO. 00094370.
Confidential  Business  Information;  unpublished
U.S. EPA.   1984.   Health and  Environmental  Effects Profile  for  Propachlor.
Prepared by the Office of Health and  Environmental  Assessment,  Environmental
Criteria  and  Assessment  Office,   Cincinnati,  OH  for  the Office  of  Solid
Waste,  Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk   Information  System  (IRIS).    Online.
Office   of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati,  OH.
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Propazlne
Gelgy   Company.    1980.    Confidential  Business   Information;   unpublished
study.  Accession No. 243353.

U.S.  EPA.   1984.   Health  and Environmental  Effects Profile  for  Propazlne.
Prepared by the  Office of  Health  and  Environmental  Assessment, Environmental
Criteria  and   Assessment  Office,  Cincinnati.  OH  for  the  Office  of  Solid
Waste, Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).    Online.
Office  of  Health and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office. Cincinnati. OH.

Proplonltrlle
U.S.  EPA.   1985.    Health  and  Environmental  Effects   Profile  for  Proplo-
nltrlle.   Prepared   by  the  Office  of Health and Environmental  Assessment,
Environmental   Criteria and  Assessment Office, Cincinnati, OH  for  the Office
of Solid Waste and Emergency Response, Washington, DC.

n-Propyl alcohol
U.S.  EPA.   1987.   Health  and  Environmental  Effects  Document  for  n-Propyl
Alcohol.   Prepared   by  the  Office  of Health and Environmental  Assessment,
Environmental   Criteria and  Assessment Office. Cincinnati, OH  for  the Office
of Solid Waste and Emergency Response. Washington, DC.

Propylene glycol
Gaunt,  I.F., R.M.B.  Carpanlnl,  P. Grasso and  A.B.G.  Lansdown.   1972.  Long-
term  toxlclty  of  propylene  glycol  In  rats.   Food Cosmet.  Toxlcol.   10:
151-162.

Guerrant, N.B., G.P. Whltlock, M.L. Wolff and R.A.  Dutcher.   1947.   Response
of  rats  to  diets   containing  varying  amounts  of  glycerol  and  propylene
glycol.  Bull.  Natl. Formulary Comm.   15:  204-229.   (Cited  In  Informatics,
Inc., 1973)

Robertson. O.H.. C.G. Loosll,  T.T.  Puck. H.  Wise. H.M.  Lemon  and  W.  Lester.
1947.   Tests for  chronic  toxlclty  of  propylene glycol  and  oral  administra-
tion.  J. Pharmacol. Exp.  Ther.  91: 52-75.

U.S.  EPA.   1987.   Health  and Environmental  Effects Document for  Propylene
Glycol.   Prepared   by  the  Office  of  Health  and Environmental  Assessment,
Environmental   Criteria and  Assessment Office, Cincinnati. OH  for  the Office
of Solid Waste  and Emergency Response, Washington, DC.

Propylene glycol monoethyl  ether
Smyth,  H.F.,  Jr. and  C.P.   Carpenter.   1948.  Further  experience  with  the
range  finding  test   1n the  Industrial toxicology  laboratory.   J.   Ind.  Hyg.
Toxlcol.  30:  63-68.

U.S. EPA.  1984.  Health Effects  Assessment  for Glycol  Ethers.  Prepared by
the  Office  of  Health  and  Environmental  Assessment, Environmental  Criteria
and  Assessment Office.  Cincinnati, OH  for  the  Office of  Solid  Waste  and
Emergency Response,  Washington, DC.   EPA 540/1-86-052.
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Propylene glvcol monomethyl ether
Landry. T.D., T.S. Gushow  and  B.L.  Yano.   1983.   Propylene glycol monomethyl
ether:  A  13-week  Inhalation  toxldty  In  rats  and  rabbits.    Fund.  Appl.
Toxlcol.  3: 627-630.

MUler, R.R.,  E.A.  Herman, O.T. Young  et  al.  1984.   Ethylene  glycol  mono-
methyl  ether and propylene glycol  monomethyl  ether:  Metabolism,  disposition,
and  subchronlc  Inhalation  toxldty studies.  Environ.  Health  Perspect.   57:
233-239.

Rowe,  V.K.,  D.D.  McColllster,  H.C.  Spencer  et  al.   1954.   Toxicology  of
mono-,  d1-,  and  tr1-propylene  glycol  methyl ethers.  Arch.  Ind.  Hyg.  Occup.
Ned.  9: 509-525.

U.S.  EPA.   1984.   Health  Effects Assessment for Glycol  Ethers.   Prepared  by
the  Office of  Health  and  Environmental  Assessment, Environmental  Criteria
and  Assessment  Office,  Cincinnati, OH  for  the  Office  of  Solid Waste  and
Emergency Response, Washington, DC.  EPA 540/1-86-052.

Pyrene
U.S.  EPA.   1984.  Health  Effects   Assessment  for Pyrene.   Prepared by  the
Office  of  Health  and  Environmental Assessment,  Environmental Criteria  and
Assessment Office, Cincinnati,  OH  for  the  Office of Emergency and  Remedial
Response, Washington, DC.

U.S.  EPA.   1989.  Mouse  oral   subchronlc  toxldty  study of  pyrene.   Study
conducted by Toxldty  Research Laboratories,  Muskegon,  MI for the Office  of
Solid Waste, Washington, DC.

PyMdlne
U.S.  EPA.   1986a.    Health  and  Environmental Effects Profile for  Pyrldlne.
Prepared by  the Office  of  Health and  Environmental  Assessment, Environmental
Criteria  and Assessment  Office,  Cincinnati.  OH  for  the Office  of  Solid
Waste, Washington,  DC.

U.S.  EPA.    1986b.   Pyrldlne.   90-Day  subchronlc  oral   toxldty  In  rats.
Sponsored by Office of  Solid Waste, Washington,  DC.

U.S.  EPA.   1990.    Integrated  Risk   Information  System  (IRIS).    Online.
Office  of  Health and  Environmental Assessment,  Environmental Criteria  and
Assessment Office,  Cincinnati,  OH.

RDX
Levlne,  B.S.,  E.M.  Furedl, V.S.  Rae,  D.E.  Gordon  and  D.M.  Llsh.   1984.
Determination of the chronic mammalian  lexicological  effects of  RDX:  Twenty-
four  month   chronic  toxlclty/cardnogenlclty   study   of   hexahydro-1,3,5-
tr1n1tro-l,3,5-tr1azlne  (RDX)   In  the  Fischer  344   rat.   NTIS  AD-A160774.
Vol. 1.  347 p.

U.S.  EPA.   1989.    Health  and   Environmental   Effects   Document   for   RDX
(Cyclonlte).   Prepared  by  the Office of  Health and  Environmental  Assessment,
Environmental Criteria   and  Assessment  Office,  Cincinnati, OH  for the  Office
of Solid Waste and  Emergency Response,  Washington,  DC.
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U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

Ronnel
McColllster, O.D.,  F.  Oyen and  V.K.  Rowe.   1959.  lexicological  studies of
0,0-d1methyl-o-(2.4,5-tr1chlorophenyl)phosphoth1oate  (ronnel)  In  laboratory
animals.  J. Agrlc. Food Chem.  7: 689.

U.S.  EPA.   1984.   Health  and  Environmental  Effects  Profile for  Ronnel.
Prepared  by  the  Office  of  Health and Environmental  Assessment, Environmental
Criteria  and  Assessment  Office,  Cincinnati,   OH  for  the  Office of  Solid
Waste, Washington. DC.

Selenourea
U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

Yang, G..  S. Wang, R.  Zhou and  S.  Sun.   1983.  Endemic  selenium Intoxica-
tion of humans 1n China.  Am.  J. Clln. Nutr.  37:  872-881.

Selenous add
U.S. EPA.  1989.   Health and  Environmental  Effects  Document for Selenium and
Compounds.   Prepared  by the  Office  of Health  and  Environmental Assessment,
Environmental Criteria  and  Assessment Office,   Cincinnati,  OH for  the Office
of Solid Waste and Emergency Response, Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office. Cincinnati, OH.

Yang, G., W. Shuzhen, R. Ahou  and  S.  Sun.   1983.   Endemic selenium Intoxica-
tion of humans In China.  Am.  J. Cl1n. Nutr.  37:  872-888.

Silver
Blumberg, H.  and  T.N.  Carey.   1934.   Argyremla:   Detection  of unsuspected
and  obscure  argurla  by   the   spectrographlc   demonstration   of  high  blood
Silver.   J.  Am. Med. Assoc.   103: 1521-1524.

East, B.W.,  K.  Boddy.  E.D. Williams,  D.  Maclntyre and  A.L.C. MeLay.  1980.
Silver  retention,   total  body  silver and  tissue  silver  concentrations  In
argyrla associated with exposure  to  an  anti-smoking  remedy containing silver
acetate.  Cl1n. Exp. Dermatol.  5: 305-311.

Gaul, L.E. and A.N. Staud.   1935.  Clinical spectroscopy.  Seventy  cases of
generalized  argyrla following organic and  colloidal   silver  medication.   J.
Am. Med. Assoc.  104:  1387-1390.

U.S.  EPA.   1990.    Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health  and  Environmental   Assessment,  Environmental  Criteria  and
Assessment Office,  Cincinnati, OH.
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Silver cyanide
Howard.  J.W.  and  R.F.  Hanzal.   1955.   Chronic  toxlclty for  rats of  food
treated with hydrogen cyanide.   Agrlc.  Food Chem.   3:  325-329.

PhllbMck, D.J.,  J.B.  Hopkins,  D.C. Hill,  J.C.  Alexander and  R.G.  Thomson.
1979.   Effects  of prolonged  cyanide and  thlocyanate feeding  In  rats.   J.
Toxlcol. Environ. Health.   5:  579-592.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).    Online.
Office  of  Health  and  Environmental Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati,  OH.
Slmazlne
C1ba-Ge1gy Corporation.
1988.  MRID No.  40614405.
U.S.  EPA.   1984.   Health  and  Environmental  Effects  Profile for  Slmazlne.
Prepared by the Office of Health and  Environmental  Assessment,  Environmental
Criteria  and  Assessment  Office.   Cincinnati,  OH  for  the  Office  of  Solid
Waste, Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk   Information  System  (IRIS).    Online.
Office  of  Health and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati,  OH.
Sodium cyanide
Howard,  J.U.  and  R.F.  Hanzal.   1955.   Chronic  toxlclty for
treated with hydrogen cyanide.   Agrlc.  Food Chem.   3:  325-329.
                                       rats of  food
U.S. EPA.  1984.  Health Effects Assessment  for  Sodium  Cyanide.   Prepared by
the  Office  of  Health  and  Environmental  Assessment.  Environmental  Criteria
and  Assessment   Office.  Cincinnati,  OH  for  the Office  of  Emergency  and
Remedial Response, Washington,  DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).    Online.
Office  of  Health and  Environmental  Assessment,  Environmental Criteria  and
Assessment Office. Cincinnati.  OH.

Sodium dlethyldlthlocarbamate
Sunderman, F.W..  O.E.  Paynter  and  R.B.  George.   1967.   The  effects  of  the
protracted administration of the chelatlng  agent, sodium dlethyldlthlocarba-
mate (dlthlocarb).  Am. J.  Med. Sc1.   254:  46-56.

U.S.  EPA.    1988.   Health  and  Environmental   Effects   Document  for  Sodium
Dlethyldlthlocarbamate.  Prepared by  the Office  of Health  and Environmental
Assessment.  Environmental Criteria and Assessment Office,  Cincinnati,  OH  for
the Office of Solid Waste and Emergency Response, Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).    Online.
Office  of  Health and  Environmental  Assessment,  Environmental Criteria  and
Assessment Office, Cincinnati,  OH.

Sodium metavanadate
Domingo, J.L.,  J.L.  Llobet,  J.M. Tomas  and J.  Corbella.   1985.   Short-term
toxlclty studies of vanadium In rats.  J. Appl. Toxlcol.   5(6): 418-421.
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U.S.  EPA.   1987.   Health  Effects  Assessment  for  Vanadium and  Compounds.
Prepared by the Office of Health  and  Environmental  Assessment,  Environmental
Criteria and  Assessment  Office,  Cincinnati, OH  for the Office  of  Emergency
and Remedial Response, Washington. DC.  ECAO-CIN-H108.

Strychnine
Seldl, I. and  G.  Zblnden.   1982.   Subchronlc oral  toxlclty  of  strychnine In
rats.  Arch. Toxlcol.   51(3):  267-271.

U.S.  EPA.   1990.   Integrated  Risk   Information  System  (IRIS).    Online.
Office of  Health and  Environmental   Assessment.  Environmental   Criteria  and
Assessment Office, Cincinnati, OH.

Styrene
Quast,  J.F.,   C.G.  Humlston,  R.T.  Kalnlns,  et  al.   1979.   Results  of  a
Toxlclty Study  of MonomerIc Administered to Beagle Dogs by  Oral  Intubation
for  19 Months.   Toxicology  Research Laboratory,  Health  and  Environmental
Sciences, Dow Chemical Co.,  Midland, MI.   Final  Report.

U.S.  EPA.   1984.   Health  and Environmental  Effects  Profile   for  Styrene.
Prepared by the Office of Health  and  Environmental  Assessment,  Environmental
Criteria  and   Assessment  Office,  Cincinnati,  OH  for  the  Office  of  Solid
Waste, Washington. DC.

U.S.  EPA.   1989.   Health Effects  Assessment for  Styrene.   Prepared by  the
Office of  Health and  Environmental   Assessment.  Environmental   Criteria  and
Assessment  Office. Cincinnati,  OH for the  Office of Emergency  and  Remedial
Response, Washington,  DC.  ECAO-CIN-H115.

U.S.  EPA.   1990.   Integrated  Risk   Information  System  (IRIS).    Online.
Office of  Health and  Environmental   Assessment.  Environmental   Criteria  and
Assessment Office, Cincinnati, OH.

Succlnonltrlle
U.S.  EPA.   1987.  Health   and  Environmental Effects  Document   for  Selected
NUMles.   Prepared  by  the Office  of Health  and  Environmental  Assessment,
Environmental   Criteria and  Assessment Office,  Cincinnati, OH for  the Office
of Solid Waste and Emergency Response, Washington, DC.

Sulfurlc acid
Carson,  B.L.,  B.L.  Herndon.  H.V. Ellis  III,  et  al.   1981.   Sulfurlc  Acid
Health  Effects.  Prepared  under  Contract  68-03-2928   by  Midwest  Research
Institute,  Kansas  CUy,  MO.   Prepared  for   Emission  Control  Technology
Division, Office  of  Mobile  Source Air   Pollution  Control.  U.S.  EPA,  Ann
Arbor HI.  EPA 460/3-81-025.  NTIS PB82-113135.

U.S.  EPA.   1984.  Health Effects  Assessment for Sulfurlc  Acid.   Prepared by
the  Office  of  Health  and  Environmental  Assessment. Environmental  Criteria
and  Assessment  Office,  Cincinnati,  OH  for  the  Office  of  Emergency  and
Remedial Response. Washington, DC.

Temephos
Galnes, T.B..  R.D.  Klmbrough  and E.R. Law,  Jr.  1967.  Toxicology  of  abate
In laboratory animals.  Arch.  Environ. Health.   14:  283-288.
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U.S.  EPA.   1984.   Health and  Environmental  Effects  Profile  for  Temephos.
Prepared by the  Office of  Health  and  Environmental  Assessment, Environmental
Criteria  and  Assessment  Office,  Cincinnati,   OH  for  the  Office  of  Solid
Waste, Washington, DC.

Terbufos
U.S.  EPA.   1984.   Health and  Environmental  Effects  Profile  for  Terbufos.
Prepared by the  Office of  Health  and  Environmental  Assessment, Environmental
Criteria  and  Assessment  Office,  Cincinnati,   OH  for  the  Office  of  Solid
Waste, Washington, DC.

Terephthallc acid
U.S.  EPA.   1984.   Health  and Environmental  Effects  Profile for Terephthallc
Add.   Prepared  by  the   Office   of  Health  and  Environmental  Assessment,
Environmental  Criteria and  Assessment Office,  Cincinnati,  OH  for  the Office
of Solid Waste,  Washington, DC.

1.2.4.5.-Tetrach1orobenzene
Chu,  I.,  D.C.  Vllleneuve. V.E.  Valll  and  V.E. Secours.   1984.   Toxlclty of
1,2,3,4-, 1,2,3,5-  and  1,2,4,5-tetrachlorobenzene  In the  rat:   Results  of a
90-day feeding study.  Drug Chem.  Toxlcol.   7:  113-127.

U.S.  EPA.   1990.   Integrated   Risk   Information   System  (IRIS).    Online.
Office  of  Health and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

Tetrachloroazoxybenzene (TCAOB)
U.S.  EPA.   1985.   Health  and Environmental  Effects  Profile for  TCAB,  TCAOB
and  TCHB.   Prepared by the  Office of  Health  and Environmental  Assessment,
Environmental  Criteria and  Assessment Office,  Cincinnati,  OH  for  the Office
of Solid Waste and Emergency Response, Washington,  DC.

Tetrachlorocyclopentadlene
U.S.  EPA.   1988.   Health  and Environmental  Effects  Document  for Chlorinated
Cyclopentadlenes.   Prepared  by  the   Office  of  Health  and  Environmental
Assessment,  Environmental  Criteria  and  Assessment Office.  Cincinnati, OH for
the Office of  Solid Waste  and Emergency Response.  Washington, DC.

Tetrachloroethylene (perch!oroethylene)
Buben, J.A.  and  E.J.  O'Flaherty.   1985.  Delineation of  the  role of  metabo-
lism  In  the  hepatoxlclty   of  trlchloroethylene  and  perchloroethylene:  A
dose-effect  study.  Toxlcol.  Appl. Pharmacol.  78:  105-122.

U.S.  EPA.   1988.   Updated  Health  Effects   Assessment   for  Tetrachloro-
ethylene.   Prepared  by the  Office of  Health  and Environmental  Assessment,
Environmental  Criteria and  Assessment Office.  Cincinnati,  OH  for  the Office
of Emergency and Remedial  Response, Washington, DC.

U.S.  EPA.   1990.   Integrated   Risk   Information   System  (IRIS).    Online.
Office  of  Health and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office. Cincinnati. OH.
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Tetrachlorohvdrazobenzene (TCHB1
U.S.  EPA.   1985.  Health and  Environmental  Effects Profile  for  TCAB, TCAOB
and  TCHB.   Prepared by  the Office  of  Health and  Environmental  Assessment.
Environmental  Criteria  and  Assessment Office, Cincinnati,  OH for the Office
of Solid Waste and Emergency Response, Washington, DC.
2.3.4.6-Tetrachlorophenol
U.S.   EPA.    1986.    2,3,4.6-Tetrachlorophenol.    90-day   Subchronlc
Toxlclty Study In Rats Office of Solid Waste, Washington, DC.
                                                Oral
U.S.  EPA.   1987.   Health and Environmental  Effects  Document for Chlorinated
Phenols.   Prepared by  the  Office  of  Health  and  Environmental Assessment,
Environmental  Criteria  and Assessment Office, Cincinnati,  OH for the Office
of Solid Waste and Emergency Response, Washington. DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System   (IRIS).   Online.
Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office. Cincinnati, OH.

Tetrachlorophenol 2.3.4.5-. 2.3.5.6-
U.S.  EPA.   1987.   Health and Environmental  Effects  Document for Chlorinated
Phenols.   Prepared by  the  Office  of  Health  and  Environmental Assessment,
Environmental  Criteria  and Assessment Office, Cincinnati,  OH for the Office
of Solid Waste and Emergency Response, Washington. DC.
1.1.2.3-Tetrachloropropene
U.S.  EPA.   1983.    Health  and  Environmental
propenes.   Prepared  by  the  Office of  Health
Environmental Criteria  and  Assessment Office,
of Solid Waste, Washington,  DC.

Tetrachlorovlnphos (Stlrofos)
Shell  Chemical  Company.   1968.   Confidential
llshed study.  Accession No. 115684.
                       Effects   Profile  for  Chloro-
                      and  Environmental  Assessment,
                      Cincinnati, OH  for  the Office
                       Business  Information;  unpub-
U.S.  EPA.   1984.   Health and  Environmental  Effects  Profile  for  Stlrofos.
Prepared by the  Office  of  Health  and  Environmental  Assessment, Environmental
Criteria  and  Assessment  Office,   Cincinnati,   OH  for  the  Office  of  Solid
Waste, Washington. DC.

U.S.  EPA.   1990.   Integrated  Risk   Information  System  (IRIS).    Online.
Office  of  Health and  Environmental Assessment,  Environmental  Criteria  and
Assessment Office. Cincinnati,  OH.
Tetraethyl dlthlopyrophosphate
Klmmerle,  G.  and  O.R.  Kllmmer.   1974.
Sulfotep.  Arch. Toxlcol.   33(1):  1-16.
                 Acute  and  subchronlc  toxldty  of
U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office of  Health and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati,  OH.
Tetraethyl lead
Schepers,  G.W.    1964.
Health.   8: 277-295.
Tetraethyl  and  tetramethyl  lead.   Arch.  Environ.
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U.S.  EPA.   1990.    Integrated  Risk  Information  System  (IRIS).    Online.
Office of  Health and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office.  Cincinnati,  OH.

Thallium and Compounds:
Thallium (In salts). Thallium!I) oxide  FThalllc  oxldel.  ThalHum(I)  acetate.
ThalHum(I) carbonate. ThalHumd) chloride.  Thallium (I)  nitrate.  Thallium
selenlte (T1?Se). Thalllum(I)  sulfate
MRI (Midwest Research  Institute).  1986.  Subchronlc  (90-day)  toxlclty  study
of  thallium sulfate In  Sprague-Dawley rats.   Office of  Solid Waste,  U.S.
EPA, Washington, DC.  (Cited In U.S.  EPA,  1987a)

U.S.  EPA.   1986.  Subchronlc   (90-day)  toxlclty  of thalllum(I) sulfate  (CAS
No.  7446-18-6)   In  Sprague-Dawley  rats.   Final  Report.   Prepared  for  the
Office of Solid Waste,  U.S.  EPA, Washington.  DC.   Project No.  8702-1  (18).

U.S. EPA.   1988.  Health and Environmental Effects  Document  for Thallium and
Compounds.  Prepared by  the Office  of  Health and  Environmental  Assessment,
Environmental  Criteria and  Assessment  Office, Cincinnati, OH for  the  Office
of Solid Waste and  Emergency Response,  Washington, DC.

U.S.  EPA.   1990.    Integrated  Risk  Information  System  (IRIS).    Online.
Office of  Health and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office,  Cincinnati.  OH.

2-(Th1ocyanomethylth1o)benzoth1azole  (TCMTB)
U.S.  EPA.   1984.    Health  and  Environmental  Effects  Profile  for  TCMTB.
Prepared by the  Office of Health and Environmental  Assessment,  Environmental
Criteria  and  Assessment  Office,  Cincinnati,  OH  for  the Office  of  Solid
Waste, Washington,  DC.

Thlofanox
U.S.  EPA.   1989.  Health and  Environmental  Effects Document for  Thlofanox.
Prepared by the  Office of Health and Environmental  Assessment,  Environmental
Criteria and Assessment Office, Cincinnati, OH for  the Office  of  Solid  Waste
and Emergency  Response, Washington, DC.

Thlram
Hornshaw,  T.C.,  R.J.  Aulerlch  and R.K. Ringer.   1987.   Toxlclty of  thlram
(tetramethylthlnoram  dlsulflde)   to   mink   and  European   ferrets.    Bull.
Environ.  Contam. Toxlcol.   38(4): 618-626.

U.S.  EPA.   1989.   Health  and  Environmental  Effects Document  for  Thlram.
Prepared by the  Office of Health and Environmental  Assessment,  Environmental
Criteria and Assessment Office, Cincinnati. OH for  the Office  of  Solid  Waste
and Emergency  Response, Washington, DC.

U.S.  EPA.   1990.    Integrated  Risk  Information  System  (IRIS).    Online.
Office of  Health and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office,  Cincinnati,  OH.
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Tin and compounds
NTP  (National   Toxicology   Program).    1982.    Carclnogenesls  bloassay  of
stannous chloride (CAS No. 7772-99-8)  In  F344/N  rats  and B6C3F1/N mice (feed
study).  NCI/NTP Tech. Rep.  Ser. No.  231.   Also  publ.  as DHHS (NIH) publ Iss
NIH 82-1787 and NTIS PB 82-242-553.

U.S. EPA.  1987.  Health Effects Assessment  for  Tin.   Prepared by the Office
of  Health  and Environmental Assessment.  Environmental  Criteria  and  Assess-
ment Office,  Cincinnati,  OH for  the Office  of Solid  Waste and  Emergency
Response, Washington, DC.

Toluene
Andersen,  I.,  G.R.  Lundqvlst,  L.  Molhave,  O.F.  Pedersen,  D.F.  Proctor,  M.
Veath,  and P  P.  Wyon.  1983.  Human  response to  controlled  levels of  toluene
1n six-hour exposure.  Scand. J. Work Environ.  Health 9:   405-418.

CUT  (Chemical   Industry Institute  of  Toxicology).   1980.   A  twenty-four
month  Inhalation toxicology  study  In  Flscher-344 rats  exposed to atmospheric
toluene.   Executive  Summary  and Data  Tables.  October 15,  1980.   (Cited  In
U.S. EPA, 1985)

U.S. EPA.   1984.  Health Effects  Assessment for Toluene.   Prepared  by  the
Office  of  Health and  Environmental   Assessment,  Environmental  Criteria  and
Assessment Office,  Cincinnati,  OH  for the  Office of  Emergency  and Remedial
Response, Washington, DC.

U.S. EPA.  1985.  Drinking Water Criteria  Document  for Toluene.   Prepared  by
the  Office of Health  and Environmental  Assessment,   Environmental  Criteria
and  Assessment   Office,  Cincinnati.   OH  for the Office  of  Drinking  Water,
Washington, DC.  Final Draft (on Public Comment).  EPA 600/X-84-188-2.

U.S.  EPA.   1990.    Integrated   Risk  Information  System  (IRIS).    Online.
Office  of  Health and  Environmental   Assessment,  Environmental  Criteria  and
Assessment Office,  Cincinnati,  OH.

Wolf. M.A., V.K. Rowe, D.D.  McColllster  et  al.   1956.  Toxlcologlcal  studies
of  certain alkylated  benzenes  and benzene.   Arch. Ind.  Health.  14:  387.
(Cited In U.S. EPA,  1985)

Toluenedlamlne (2.3-; 3.4-)
U.S.  EPA.   1984.   Health  and  Environmental  Effects Profile  for  Selected
Toluenedlamlnes.   Prepared by the  Office  of  Health  and Environmental  Assess-
ment,  Environmental  Criteria and  Assessment Office,  Cincinnati, OH  for  the
Office of Solid Waste. Washington.  DC.

To1uene-2.5-d1am1ne
NCI  (National Cancer  Institute).    1978.    Bloassay   of  Toluene-2,5-dlam1ne
Sulfate  for  Possible  Carclnogenlclty.   NCI Carclnogenesls  Tech.  Rep.  Ser.
No. 126.

U.S.  EPA.   1984.   Health  and  Environmental  Effects Profile  for  Selected
Toluenedlamlnes.   Prepared by the  Office  of  Health  and Environmental  Assess-
ment,  Environmental  Criteria and  Assessment Office,  Cincinnati, OH  for  the
Office of Solid Waste, Washington.  DC.
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To1uene-2.6-d1am1ne
NCI  (National  Cancer   Institute).    1980.   Bloassay  of  2,6-Toluenedlamlne
Dlhydrochlorlde for Possible  Carclnogenlclty.   NCI  Cardnogenesls Tech. Rep.
Ser. No. 200.

U.S.  EPA.    1984.   Health  and  Environmental  Effects  Profile  for  Selected
Toluenedlamlnes.  Prepared by  the Office  of  Health  and Environmental Assess-
ment,  Environmental  Criteria  and Assessment  Office,  Cincinnati,  OH  for  the
Office of Solid Waste.  Washington, DC.

m-Toluldlne
U.S.  EPA.   1984.   Health and  Environmental  Effects Profile  for Toluldlnes.
Prepared by  the Office  of Health and  Environmental  Assessment, Environmental
Criteria  and Assessment  Office, Cincinnati.   OH  for  the  Office of  Solid
Waste. Washington. DC.

Trlallate
Monsanto  Company.   1979.   Confidential  Business  Information;  unpublished
study.  Accession No.  242057.

U.S.  EPA.   1983.   Health  and Environmental  Effects  Profile  for Trlallate.
Prepared by  the Office  of Health and  Environmental  Assessment, Environmental
Criteria  and Assessment  Office, Cincinnati,   OH  for  the  Office of  Solid
Waste, Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk   Information  System  (IRIS).   Online.
Office  of  Health and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

1.2.4-Tr1bromobenzene
Carlson, G.P.  and R.G. Tardlff.  1977.   Effect of 1,4-d1bromod1benzene  and
l.2,4-tr1bromobenzene on  xenoblotlc  metabolism.   Toxlcol. Appl.  Pharmacol.
42: 189-196.

U.S.  EPA.   1984.  Health  and  Environmental Effects  Profile  for  Bromoben-
zenes.   Prepared  by  the  Office of   Health and  Environmental  Assessment,
Environmental Criteria  and  Assessment Office,  Cincinnati, OH  for the Office
of Solid Waste and Emergency Response, Washington,  DC.

U.S.  EPA.   1990.   Integrated  Risk   Information   System  (IRIS).   Online.
Office  of  Health and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

1,2.4-Trlchlorobenzene
Carlson, G.P.  and R.G. Tardlff.  1976.   Effect of  chlorinated  benzenes  on
the metabolism of foreign organic compounds.  Toxlcol.  Appl.  Pharmacol.  36:
383-394.

U.S.  EPA.    1987.  Health  Effects   Assessment  for  1.2,4-Trlchlorobenzene.
Prepared by  the Office  of Health  and  Environmental  Assessment, Environmental
Criteria and  Assessment  Office,  Cincinnati,  OH  for  the Office  of Emergency
and Remedial Response,  Washington, DC.
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Watanabe, P.G., R.J.  Koclba,  R.E.  Hefner et al.   1978.   Subchronlc toxlclty
studies  of  1,2,4-trlchlorobenzene  In  experimental  animals.  Toxlcol.  Appl.
Pharmacol.  45(1): 322-333.

Trlchlorocyclopentadlene
U.S. EPA.   1988.   Health and Environmental Effects  Document for Chlorinated
Cyclopentadlenes.    Prepared  by  the  Office  of  Health  and  Environmental
Assessment,  Environmental  Criteria and Assessment  Office,  Cincinnati.  OH for
the Office of Solid Waste and Emergency Response, Washington, DC.

1.1,1-Trlchloroethane
Torkelson, R.R., F. Oyen,  D.D.  HcColllster  and  V.K.  Rowe.   1958. Toxlclty of
1,1.1-trlchloroethane   as   determined    on   laboratory  animals   and   human
subjects.  Am.  Ind. Hyg. Assoc.  J.   19: 353-362.

U.S.  EPA.   1984.   Health  Effects   Assessment  for  1,1,1-Trlchloroethane.
Prepared by the Office  of  Health and Environmental Assessment. Environmental
Criteria and Assessment Office. Cincinnati, OH  for  the Office  of Emergency
and Remedial Response, Washington,  DC.

U.S.  EPA.   1990.   Integrated   Risk  Information  System  (IRIS).   Online.
Office  of  Health   and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office. Cincinnati, OH.

1.1,2-Trlchloroethane
Sanders,  V.M.,  K.L.  White  Jr.,   G.M.   Shopp  Jr.  and  A.E.  Munson.   1985.
Humoral and cell  mediated  Immune  status  of mice  exposed  to 1,1,2 trlchloro-
ethane Drug  Chem Toxlcol.  8(5): 357-372.

U.S.  EPA.   1984.   Health  Effects   Assessment  for  1,1,2-Trlchloroethane.
Prepared by the Office  of  Health and Environmental Assessment, Environmental
Criteria and Assessment Office, Cincinnati, OH  for  the Office  of Emergency
and Remedial Response, Washington,  DC.

U.S.  EPA.   1990.   Integrated   Risk  Information  System  (IRIS).   Online.
Office  of  Health   and  Environmental  Assessment.  Environmental  Criteria  and
Assessment Office, Cincinnati. OH.

White,  K.L.  Jr.,   V.M.   Sanders,  V.W.  Barnes,  G.M.  Shopp  and  A.E.  Munson.
1985.   Toxicology  of   1,1,2   trlchloroethane   In  the  mouse.    Drug  Chem
Toxlcol.  8(5):  333-355.

Trlchlorofluoromethane
Jenkins,  L.J.,  R.A.   Jones.  R.A.  Coon  and J.  Slegal.  1970.   Repeated  and
continuous  exposures   of   laboratory   animals   to   tMchlorof luoromethane.
Toxlcol. Appl.  Pharmacol.  16: 133-142.

NCI  (National Cancer  Institute).   1978.   Bloassay of  Trlchlorofluoromethane
for  Possible Cardnogenlclty.   NCI  Carclnogenesls Tech.  Rep. Ser.  No.  106.
(Also publ as DHEW (NIH) 78-1356)

U.S. EPA.   1987.   Health Effects  Assessment for  Fully Halogenated Methanes.
Prepared by  the Office  of  Health and Environmental Assessment. Environmental
Criteria and Assessment Office. Cincinnati, OH  for  the Office  of Emergency
and Remedial Response. Washington,  DC.


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U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).    Online.
Office  of  Health and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati,  OH.

2.4.4'-Tr1ch1oro-2'-hvdroxyd1phenv1  ether
Lyman,  F.L. and  T.  Furla.   1969.  Toxicology  of 2,4,4'-Tr1chloro-2l-hydroxy-
dlphenyl ether.  Ind. Med.   38: 45-52.

U.S.  EPA.   1987.   Health  Effects and Environmental  Document  for  Haloethers.
Prepared by the  Office of  Health and Environmental  Assessment,  Environmental
Criteria and Assessment Office, Cincinnati, OH  for  the  Office of  Solid Waste
and Emergency Response, Washington,  DC.

2.4.5-Tr1ch1orophenol
McColHster, D.D., D.T. Lockwood and V.K.  Rowe.   1961.   ToxUologlc  Informa-
tion on 2,4,5-tMchlorophenol.   Toxlcol.  Appl. Pharmacol.  3:  63-70.

U.S.  EPA.   1984.   Health  Effects  Assessment  for  2,4,5-TMchlorophenol.
Prepared by the  Office of  Health and Environmental  Assessment,  Environmental
Criteria and Assessment  Office,  Cincinnati,  OH  for the Office of  Emergency
and Remedial Response,  Washington,  DC.

U.S.  EPA.   1987.   Health  and Environmental Effects  Document  for  Chlorinated
Phenols.   Prepared  by  the Office  of  Health  and  Environmental  Assessment.
Environmental  Criteria and Assessment  Office, Cincinnati, OH for  the Office
of Solid Waste and Emergency Response,  Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).    Online.
Office  of  Health and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati.  OH.

Trlchlorophenol. 2.3.4-.  2.3.5-.  2.3.6-.  3.4.5-
U.S.  EPA.   1987.   Health  and Environmental Effects  Document  for  Chlorinated
Phenols.   Prepared  by  the Office  of  Health  and  Environmental  Assessment,
Environmental  Criteria and Assessment  Office, Cincinnati, OH for  the Office
of Solid Waste and Emergency Response,  Washington, DC.

2.4.5-Trlchlorophenoxy acetic add

Gehrlng. P.J.  and J.E. Betso.   1978.   Phenoxy  adds:   Effects and  fate  In
mammals.  Ecol. Bull. 27:   122-133.

Koclba,  R.S.,  D.G.  Keyes, R.W. Llsowe,  et  al.   1979.   Results of  2-year
chronic  toxldty  and oncogenldty  study  of rats Ingesting diets  containing
2,4,5-T.  Food Cosmet.  Toxlcol. 17:   205-222.

U.S.   EPA.    1989.    Health   and  Environmental   Effects   Document   for
2,4,5-TMchlorophenoxy Acetic  Acid.   Prepared  by  the  Office of  Health  and
Environmental  Assessment,   Environmental  Criteria   and  Assessment   Office,
Cincinnati.  OH  for   the   Office  of  Solid  Waste  and  Remedial   Response,
Washington. DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).    Online.
Office  of  Health and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati,  OH.
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2 (2.4.5-Tr1ch1orophenoxy) proplonlc add (2.4.5-TP).   (Sllvex)
Gehrlng, P.O.  and G.E. Betso.   1978.   Phenoxy  acids:   Effects and
mammals.   In:  Chlorinated  Phenoxy  Acids  and  Their  Dloxlns,  Vol.
Ramel, Ed.   Ecol. Bull.,  Stockholm,  p.  122-133.
                                  fate
                                  27,
      In
      C.
Mulllson, M.R.  1966.  Some lexicological aspects of  sllvex.   ln_:  Proc.  19th
Ann. Meet., Southern Weed Conference,  Jacksonville,  FL.   p. 420-435.

U.S.  EPA.   1990.   Integrated  Risk   Information  System  (IRIS).   Online.
Office  of  Health and  Environmental Assessment,  Environmental Criteria  and
Assessment Office. Cincinnati, OH.

1.1.1- and l.2.2-Tr1chloropropane
U.S.  EPA.   1987.   Health and  Environmental  Effects Document  for  Trlchloro-
propanes.   Prepared  by  the  Office of  Health  and  Environmental  Assessment,
Environmental Criteria and  Assessment  Office.  Cincinnati, OH  for  the Office
of Solid Waste and Emergency Response.  Washington, DC.

1.1,2-Trlchloropropane
U.S.  EPA.   1987.   Health and  Environmental  Effects Document  for  Trlchloro-
propanes.   Prepared  by  the  Office of  Health  and  Environmental  Assessment,
Environmental Criteria and  Assessment  Office.  Cincinnati. OH  for  the Office
of Solid Waste and Emergency Response.  Washington. DC.

U.S.  EPA.   1990.   Integrated  Risk   Information  System  (IRIS).   Online.
Office  of  Health and  Environmental Assessment.  Environmental Criteria  and
Assessment Office, Cincinnati, OH.

Vlllaneuve.  D.C.,  I.  Chu,   V.E.  Secours,  M.G.   Cotle.  G.L.  Plaa and  V.E.
VallL   1985.   Results  of a  90-day toxlclty study on  1.2,3-  and  1,1,2-trl-
chloropropane administered via the  drinking  water.  Scl.  Total Environ.   47:
421-426.
1,2.3-Tr1ch1oropropane
NTP  (National  Toxicology Program).   1983a.   Final
gavage  study  of  1,2,3-trlchloropropane  In Fischer
Hazelton Laboratories.
                 report  120-day  toxlclty
                 344 rats.   Performed  by
U.S.  EPA.   1987.   Health and  Environmental  Effects Document  for  Trlchloro-
propanes.   Prepared  by  the  Office of  Health  and  Environmental  Assessment,
Environmental Criteria and  Assessment  Office,  Cincinnati. OH  for  the Office
of Solid Waste and Emergency Response,  Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk   Information  System  (IRIS).   Online.
Office  of  Health and  Environmental  Assessment,  Environmental Criteria  and
Assessment Office. Cincinnati,  OH.

1,2.3-Trlchloropropene
McKenna,  M.J.,  J.F.  Quast  and  G.A.  Stevens.   1978.   Results  of a  90-day
Inhalation  toxlclty  study of  1,2,3-trlchloropropene  In  laboratory  animals.
Toxlcol. Appl. Pharmacol.  45:  249.
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U.S.  EPA.    1983.   Health  and  Environmental   Effects   Profile  for  Chloro-
propenes.   Prepared  by the  Office of  Health  and  Environmental  Assessment.
Environmental Criteria and  Assessment  Office,  Cincinnati, OH  for  the Office
of Solid Waste,  Washington.  DC.

2.3.6-Tr1chlorotoluene
Chu.  I..  S.Y. Shen,  D.C.  Vllleneuve,  V.E.  Secours  and V.E. Vain.   1984.
ToxIcUy of  trlchlorotoluene  Homers:  A 28-day  feeding study In  the  rat  J.
Environ. Scl.  Health  Part  B. Pestle  Food conterm.  Agrlc.  Wastes.   19(2):
183-192.

U.S.  EPA.   1987.   Health  and Environmental Effects  Document  for  Chlorinated
Toluenes.   Prepared  by the  Office of  Health  and  Environmental  Assessment,
Environmental Criteria and  Assessment  Office,  Cincinnati, OH  for  the Office
of Solid Waste and Emergency Response.  Washington, DC.

g.2.6-Tr1ch1orotoluene
Chu.  I..  S.Y. Shen.  D.C.  Vllleneuve.  V.E.  Secours  and V.E. Valll.   1984.
Toxldty of  trlchlorotoluene  Isomers:  A 28-day  feeding study 1n  the  rat  J.
Environ. Sd.  Health  Part  B. Pestle  Food conterm.  Agrlc.  Wastes.   19(2):
183-192.

U.S.  EPA.   1987.   Health  and Environmental Effects  Document  for  Chlorinated
Toluenes.   Prepared  by the  Office of  Health  and  Environmental  Assessment,
Environmental Criteria and  Assessment  Office,  Cincinnati, OH  for  the Office
of Solid Waste and Emergency Response.  Washington. DC.

1.1.2-Trlchloro-l.2.2-tr1fluoroethane
Imbus,  H.R.  and  C. Adklns.    1972.   Physical  examination of  workers  exposed
to trlchlorotrlfluoroethane.   Arch. Environ.  Health.  24: 257-261.

U.S.  EPA.   1983.   Health  Assessment Document  for 1.1.2-Trlchloro-l,2,2-trl-
fluoroethane  (Chlorofluorocarbon  CFC-113).  Office  of  Health and  Environ-
mental  Assessment,  Environmental  Criteria and  Assessment Office,  Research
Triangle Park. NC.  EPA 600/8-82-002F.   NTIS  PB84-118843.

U.S.  EPA.    1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health  and  Environmental Assessment,  Environmental Criteria  and
Assessment  Office. Cincinnati. OH.
Trlfluralln
Hoechst  Aktlengesellschaft.    1984.
unpublished study.  MRID No. 00151908.
    Confidential   Business   Information;
U.S. EPA.   1984.   Health  and Environmental Effects Profile  for  Trlfluralln.
Prepared by the Office of Health and  Environmental  Assessment.  Environmental
Criteria  and  Assessment  Office.   Cincinnati.  OH  for  the  Office  of  Solid
Waste.  Washington. DC.

U.S.  EPA.   1990.   Integrated  Risk   Information  System  (IRIS).    Online.
Office   of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office. Cincinnati.  OH.
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Trlmethylbenzenes
U.S.  EPA.   1987.   Health  Effects  Assessment  for Trlmethylbenzenes.  Prepared
by  the  Office  of  Health and Environmental  Assessment. Environmental Criteria
and  Assessment  Office,   Cincinnati,  OH  for  the  Office  of  Emergency  and
Remedial Response, Washington, DC.

1.3.5-TrlnUrobenzene
Cody, T.E.,  S. WUherup,  L.  Hastings,  K.  Stemmer  and  R.T. Chustlon.   1981.
l,3-D1n1trobenzene:  Toxic  effects  \n_ vitro.   J.  Toxlcol.  Environ.  Health.
7: 829-847.

U.S.  EPA.   1989.   Health and Environmental  Effects  Document  for  1,3,5-Trl-
nltrobenzene.   Prepared  by  the  Office of  Health and  Environmental  Assess-
ment, Environmental  Criteria and  Assessment  Office,  Cincinnati,  OH  for  the
Office of Solid Waste and  Emergency Response, Washington. DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

Trlnltrophenols
U.S.  EPA.   1984.   Health  and  Environmental  Effects  Profile for  Trlnltro-
phenols.   Prepared by  the   Office  of Health  and  Environmental  Assessment,
Environmental  Criteria and  Assessment Office, Cincinnati,  OH  for  the  Office
of Solid Waste, Washington,  DC.

Vanadium
Schroeder.  J.A.,  M.  HHchener and  A.P.  Nason.   1970.  Zirconium,  niobium,
antlum.  antimony,  vanadium  and lead  In rats:  Life term  studies.   J.  Nutr.
100(1):  59-68.

U.S.  EPA.   1987.   Health  Effects Assessment  for  Vanadium  and  Compounds.
Prepared by the Office of Health  and  Environmental  Assessment, Environmental
Criteria and Assessment Office,  Cincinnati, OH  for the  Office  of Emergency
and Remedial Response. Washington. DC.  ECAO-CIN-H108.

Vanadium pentoxlde
Stoklnger.  H.E.,   W.D.  Wagner,  J.T.  Mountain  et  al.   1953.   Unpublished
results.  D1v.  Occup. Health, Cincinnati,  OH.   (Cited In Stoklnger, 1981)

U.S.  EPA.   1987.   Health  Effects Assessment  for  Vanadium  and  Compounds.
Prepared by the Office of Health  and  Environmental  Assessment, Environmental
Criteria and Assessment Office,  Cincinnati, OH  for the  Office  of  Emergency
and Remedial Response. Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health  and  Environmental  Assessment,  Environmental Criteria  and
Assessment Office, Cincinnati, OH.
Vanadyl sulfate
Schroeder, O.A.,  M.  Mltchener  and A.P.
antlum, antimony,  vanadium  and lead  In
100(1): 59-68.
      Nason.   1970.   Zirconium,  niobium,
      rats:  Life term  studies.   J.  Nutr.
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U.S.  EPA.    1987.   Health  Effects  Assessment  for  Vanadium and  Compounds.
Prepared by  the Office  of  Health  and  Environmental Assessment,  Environmental
Criteria and  Assessment Office,  Cincinnati, OH  for the Office  of  Emergency
and Remedial Response, Washington, DC.  ECAO-CIN-H108.

Vernolate
Stauffer Chemical Company.   1983.   Confidential  Business Information; unpub-
lished study.  Accession Nos. 249703-249704.

U.S.  EPA.   1983.    Health  and Environmental  Effects Profile for  Vernolate.
Prepared by  the Office  of  Health  and  Environmental Assessment,  Environmental
Criteria  and Assessment  Office.   Cincinnati,  OH   for  the  Office  of  Solid
Waste, Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk   Information  System  (IRIS).    Online.
Office  of  Health and  Environmental  Assessment,  Environmental   Criteria  and
Assessment Office. Cincinnati, OH.

4-V1nyl-l-Cyclohexene
U.S.  EPA.   1983.    Health  and Environmental  Effects Profile for  4-V1nyl-l-
cyclohexene.  Prepared  by  the  Office  of  Health and Environmental Assessment,
Environmental Criteria  and Assessment Office.  Cincinnati, OH for  the Office
of Solid Waste,  Washington, DC.

m-Xylene
NTP  (National Toxicology  Program).   1986.   NTP  Technical  Report  on  the
Toxicology  and  Cardnogenesls  of  Xylenes  (Mixed)  (60.2%  m-Xylene,  13.6%
p-Xylene. 17.0% Ethylbenzene and 9.1% o-Xylene)  (CAS No.  133-20-7)  In F344/N
Rats and B6C3F1  Mice (Gavage Studies).  NTP TR  327, NIH Publ. No. 86-2583.

Tatral,  E.,  G.  Ungvary, I.R.  Cseh, et  al.  1981.   The  effects  of  long-term
Inhalation of o-xylene  on  the liver.   End. Environ.  Xenoblotlcs, Proc.  Int.
Conf.  p. 293-300.

U.S. EPA.   1986.  Health  and Environmental Effects  Profile  for  Xylenes  (o-,
m-.  p-).   Prepared  by  the  Office  of Health  and  Environmental  Assessment,
Environmental Criteria  and Assessment Office,  Cincinnati, OH for the Office
of Solid Waste and Emergency Response, Washington,  DC.

U.S.  EPA.   1989.   Updated Health  Effects  Assessment for  Xylenes.   Prepared
by the Office of  Health and  Environmental  Assessment,  Environmental  Criteria
and  Assessment  Office,  Cincinnati,  OH  for   the   Office  of  Emergency  and
Remedial Response, Washington. DC.

o-Xylene
NTP  (National Toxicology  Program).   1986.   NTP  Technical  Report  on  the
Toxicology  and  Cardnogenesls  of  Xylenes  (mixed)  (60.2%  m-xylene.  13.6%
p-xylene,  17.0%   ethylbenzene  and  9.1%  o-xylene)  (CAS  No.  1330-20-7)  In
F344/N  rats  and   B6C3F1  mice  (gavage  studies).   U.S.  DHHS.  PHS, NIH,  NIP,
Research Triangle  Park,  NC.  NTP TR  327,  NIH Publ.  No. 86-2583.

Tatral.  E.,  G. Ungvary, I.R. Cseh, et  al.  1981.   The  effects  of  long-term
Inhalation of o-xylene  on  the liver.   End. Environ.  Xenoblotlcs, Proc.  Int.
Conf.  p. 293-300.
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Ungvary, 6.,  E.  Tatral,  A. Hudak. et  al.   1980.   The embryotoxlc effects of
o-, m- and p-xylene.  Toxicology.  18(1): 61-74.

U.S. EPA.   1986.   Health  and Environmental Effects  Profile  for Xylenes (o-,
m-,  p-).   Prepared  by  the  Office  of  Health  and  Environmental  Assessment,
Environmental  Criteria and Assessment Office, Cincinnati, OH  for the Office
of Solid Waste and Emergency Response, Washington, DC.

U.S. EPA.   1989.  Updated  Health Effects Assessment  for  Xylenes.   Prepared
by the Office  of  Health and Environmental Assessment, Environmental Criteria
and  Assessment  Office,   Cincinnati,   OH  for  the  Office  of   Emergency  and
Remedial Response. Washington, DC.

p-Xylene
Hake,  C.L.,  R.D.  Steward,  A. Wu et  al.  1981.   Development  of a biologic
standard  for  the  Industrial worker   by  breath  analysis.   NIOSH-HCOW-ENUM-
XY-77-3.  NTIS PB82-152844.

U.S. EPA.   1987.  Updated  Health Effects Assessment  for  Xylenes.   Prepared
by the Office  of  Health and Environmental Assessment, Environmental Criteria
and  Assessment  Office,   Cincinnati.   OH  for  the  Office  of   Emergency  and
Remedial Response. Washington, DC.

Xylenes. mixed
Carpenter, C.P.,  E.R.  Klnhead,  D.L.  Geary,  et al.   1975.   Petroleum hydro-
carbon toxlclty  studies.   V. Animal  and human  response to vapors  of mixed
xylenes.  Toxlcol. Appl.  Pharmacol.   33(3):  543-558.

Litton Blonetlcs.  1978.   Teratology  study  In  rats:  Xylene.   Final  Report to
American  Petroleum  Institute,  Washington,  DC.   LBI  Project No.  20698-5.
FYI-AX-0183-0231.

Hake,  C.L..  R.D.  Steward,  A. Wu et  al.  1981.   Development  of a biologic
standard  for  the  Industrial worker   by  breath  analysis.   NIOSH-MCOW-ENUM-
XY-77-3.  NTIS PB82-152844.

NTP  (National Toxicology  Program).   1986.   NTP  Technical  Report   on  the
Toxicology  and  Carclnogenesls  of  Xylenes  (Mixed)  (60.2%  m-Xylene,  13.6%
p-Xylene, 17.0% Ethylbenzene and  9.1%  o-Xylene)  (CAS No.  133-20-7)  In F344/N
Rats and B6C3F1 Mice (Gavage Studies).  NTP TR 327, NIH Publ. No. 86-2583.

U.S. EPA.   1989.  Updated  Health Effects Assessment  for  Xylenes.   Prepared
by the Office  of  Health and  Environmental Assessment, Environmental Criteria
and  Assessment  Office,   Cincinnati,   OH  for  the  Office  of  Emergency  and
Remedial  Response. Washington. DC.

U.S.  EPA.   1990.   Integrated   Risk  Information  System   (IRIS).    Online.
Office of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati. OH.

Zinc
Porles, W.J.,  J.H. Henzel, C.G. Rob and  W.H.  Strain.  1967.   Acceleration of
wound healing  In  man with  zinc sulfate given by mouth.  Lancet.  1:  121-124.
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Prasad, A.S., E.B.  Schoomaker,  J. Ortega  et  al.   1975.   Zinc  deficiency  1n
sickle cell disease.  Clln.  Chem.   21:  582-587.

U.S.  EPA.   1984.   Health  Effects  Assessment  for  Zinc.    Prepared  by  the
Office of  Health and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office,  Cincinnati,  OH for  the  Office of Emergency and  Remedial
Response,  Washington,  DC.

Zinc cyanide
Howard, J.W.  and  R.F.  Hanzal.   1955.   Chronic  toxlclty  for  rats  of  food
treated with hydrogen  cyanide.   Agrlc.  Food Chem.   3: 325-329.

Phllbrlck, D.J.,  J.B.  Hopkins,  D.C.  Hill,  J.C.  Alexander  and  R.G.  Thomson.
1979.  Effects  of  prolonged  cyanide  and  thlocyanate  feeding  In rats.   J.
Toxlcol.  Environ. Health.   5:  579-592.

U.S.  EPA.   1990.   Integrated  Risk   Information  System  (IRIS).    Online.
Office of  Health and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati,  OH.

Zinc phosphide
Bal.  K.M.,  M.K.  KMshnakumarl,  J.P.  Ramesh,  T.  Shlvanandappa  and  S.K.
HaJunder.    1980.   Short-term  toxlclty study  of  zinc  phosphide In  albino
rats.  Indian J. Exptl.  Blol.   18: 854-857.

U.S.  EPA.   1990.   Integrated  Risk   Information  System  (IRIS).    Online.
Office of  Health and  Environmental  Assessment.  Environmental  Criteria  and
Assessment Office. Cincinnati,  OH.

Zlneb
Blackwell-Smlth,  R.J.,  Jr.    J.K.  Flnnegan,  P.S.  Larson,  et  al.   1953.
Toxlcologlc  studies  on  zinc  and  dlsodlumethyleneblsdlthlocarbamates.   J.
Pharmacol. Exp.  Ther.   109:  159-166.

U.S.  EPA.   1984.  Health  and   Environmental  Effects  Profile  for  Zlneb.
Prepared by the  Office  of Health  and Environmental  Assessment.  Environmental
Criteria  and  Assessment  Office,   Cincinnati,  OH  for  the  Office  of  Solid
Waste. Washington. DC.

U.S.  EPA.   1990.   Integrated  Risk   Information  System  (IRIS).    Online.
Office of  Health and  Environmental  Assessment.  Environmental  Criteria  and
Assessment Office. Cincinnati,  OH.
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                       HEA SUMMARY TABLE B:  CARCINOGENS

Acephate
Chevron Chemical Company.   1982.   MRID No.  00105197

U.S.  EPA.   1984.   Health and  Environmental  Effects  Profile  for  Acephate.
Prepared by the Office of  Health  and  Environmental Assessment,  Environmental
Criteria  and  Assessment  Office.   Cincinnati,  OH  for  the  Office  of  Solid
Waste, Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk   Information  System  (IRIS).    Online.
Office  of  Health and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati. OH.

Acroleln
U.S.  EPA.   1987.   Health  Effects Assessment  for  Acroleln.  Prepared  by  the
Office  of  Health and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office,  Cincinnati,  OH for  the  Office of Emergency and  Remedial
Response, Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk   Information  System  (IRIS).    Online.
Office  of  Health and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati. OH.

Acrylamlde
Johnson, K., S.  Gorzlnskl.  K.M.  Bodner, et al.   1986.   Chronic toxlclty  and
oncogenlclty  study   on  acrylamlde  Incorporated  In  the  drinking  water  of
Fisher 344 rats.  Dow Chemical. U.S.A.. Midland.  MI.

U.S.  EPA.   1985.   Health  and  Environmental  Effects Profile  for  Acrylamlde.
Prepared by the Office of  Health  and  Environmental Assessment,  Environmental
Criteria and Assessment Office, Cincinnati, OH for the  Office  of  Solid Waste
and Emergency Response,  Washington,  DC.

U.S.  EPA.   1990.   Integrated  Risk   Information  System  (IRIS).    Online.
Office  of  Health and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

Acrylonltrlle
Bio/dynamics,  Inc.   1980a.  A  24-month oral  toxIcUy/carclnogenlclty study
of acrylonltrlle  administered  to  Spartan  rats In  the drinking  water.   Final
Report.  Vol. 1  and  2.   Prepared  by Bio/dynamics.  Inc.,  Division of  Biology
and  Safety  Evaluation,  East  Millstone, NJ,  under  Project  No.  77-1745  for
Monsanto Company, St. Louis,  MO.   (Cited In U.S.  EPA. 1983a)

Bio/dynamics,  Inc.   1980b.  A  24-month oral  toxlcHy/carclnogenlcHy study
of acrylonltrlle  administered  In  drinking  water  to  Fischer  344 rats.   Final
Report.  Vol. 1-4.   Prepared  by  B1o/dynam1cs. Inc., Division of  Biology  and
Safety Evaluation, East Millstone, NJ,  under  Project No.  77-1744  (BDN-77-27)
for Monsanto Company, St.  Louis,  MO.   (Cited In  U.S. EPA, 1983a)

O'Berg, M.  1980.   Epldemlologlc  study of workers  exposed to  acrylonltrlle.
J. Occup. Med.   22:  245-252.
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Quast, J.F.,  C.E.  Wade,  C.G. Humlston  et  al.   1980.  A  2-year  toxlclty  and
oncogenlclty  study with  acrylonltrlle  Incorporated In the drinking  water  of
rats.  Prepared  by the Toxicology  Research  Laboratory.   Health  and  Environ-
mental Research,  Dow Chemical USA,  Midland, MI,  for  the Chemical  Manufac-
turers Association. Washington,  DC.   (Cited In  U.S. EPA.  1983a)

U.S. EPA.  1983.   Health Assessment  Document for  Acrylonltrlle.   Prepared  by
the  Office  of Health  and  Environmental  Assessment, Environmental  Criteria
and Assessment Office, Research Triangle Park,  NC.   EPA  600/8-82-007F.   NTIS
PB84-149152.

U.S. EPA.   1987.   Health  Effects  Assessment for  Acrylonltrlle.   Prepared  by
the  Office  of Health  and  Environmental  Assessment, Environmental  Criteria
and  Assessment  Office,  Cincinnati,  OH  for  the  Office of  Emergency  and
Remedial  Response, Washington, DC.

U.S.  EPA.   1990.   Integrated   Risk  Information  System  (IRIS).   Online.
Office of  Health  and  Environmental Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

Alachlor
U.S.  EPA.   1984.   Health  and  Environmental Effects  Profile for  Alachlor.
Prepared  by the Office of Health and Environmental Assessment, Environmental
Criteria   and   Assessment  Office,  Cincinnati,   OH  for  the Office of  SOUd
Waste, Washington, DC.

U.S.  EPA.   1988.   Carcinogen Risk  Assessment   Verification Endeavor  (CRAVE)
Work  Group.    Verified,  pending  concurrence  on  final  coversheet and  Input
onto IRIS.

Aldrln
Davis, K.J.   1965.  Pathology report  on mice  for aldrln, dleldrln,  hepta-
chlor, or heptachlor epoxlde  for  two years.  Int.  Food.  Drug  Admin.

Davis, K.J. and  O.G.  Fltzhugh.   1962.   Tumor 1 gen1c potential of  aldrln  and
dleldrln  for mice.  Toxlcol.  Appl.  Pharmacol.  4:  187-189.

Epstein,  S.S.  1975.   The carclnogenlclty  of dleldrln.    Part  I.   Scl.  Total
Environ.   4: 1-52.

NCI  (National  Cancer  Institute).   1977.  Bloassays  of  aldrln  and  dleldrln
for  possible  carclnogenlclty.  NCI  Cardnogenesls Tech.  Rep. Sen. No.  21.
(Also published as NTIS PB-275-666)

U.S.  EPA.    1986.   Carclnogenlclty  Assessment   of  Aldrln   and  Dleldrln.
December  1986  Review  Draft.   Office of Health  and  Environmental Assessment,
Carcinogen Assessment Group,  Washington, DC.

U.S.  EPA.   1987.  Health  Effects   Assessment  for  Aldrln.   Prepared by  the
Office of  Health  and  Environmental Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati,  OH  for   the  Office of Emergency  and  Remedial
Response. Washington, DC.
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U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of Health  and  Environmental Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

Ally! chloride
U.S.   EPA.    1983.     Health   and   Environmental   Effects   Profile   for
Chloropropenes.    Prepared   by   the  Office  of   Health   and  Environmental
Assessment, Environmental Criteria  and  Assessment  Office,  Cincinnati,  OH for
the Office of Solid Waste. Washington,  DC.

U.S.  EPA.   1989.  Carcinogen Risk  Assessment Verification  Endeavor  (CRAVE)
Work  Group.   Verified,  pending  concurrence on  final  coversheets  and  Input
onto IRIS.

Aniline
CUT  (Chemical  Industry Institute  of  Toxicology).  1982.   104-Week  chronic
toxlclty study In rats:  Aniline hydrochlorlde.   Final  Report.

U.S.  EPA.  1985.   Health  and   Environmental  Effects  Profile  for  Aniline.
Prepared  by the  Office  of Health and Environmental Assessment, Environmental
Criteria and Assessment  Office,  Cincinnati, OH for  the  Office of Solid Waste
and Emergency Response, Washington.  DC.

U.S.  EPA.   1990.   Integrated   Risk  Information  System  (IRIS).   Online.
Office  of Health  and  Environmental Assessment,  Environmental  Criteria  and
Assessment Office. Cincinnati. OH.

Aramlte
Oser,  B.L.  and  H.  Oser.  1962.  2-(p-tert-Butylphenoxy)1sopropyl  2-chloro-
ethyl  sulfHe  (aramlte).   II.   Carclnogenlclty.   Toxlcol. Appl.  Pharmacol.
4: 70-88.

Popper. H.. S.S.  Steinberg.  B.L. Oser  and M. Oser.   1960.  The carcinogenic
effect of aramlte In rats.  Cancer.   13(5):  1035-1046.

U.S.  EPA.   1989.   Health and  Environmental  Effects  Document  for  Aramlte.
Prepared by the  Office  of Health and Environmental  Assessment, Environmental
Criteria and Assessment  Office,   Cincinnati, OH for  the  Office of Solid Waste
and Emergency Response, Washington.  DC.

Arsenic
Brown. C.C. and  K.C.  Chu.   1983a.   Approaches  to epldemlologlc  analysis  of
prospective and  retrospective studies: Example  of  lung cancer  and  exposure
to  arsenic.    In.:  Risk  Assesment:   Proc.  SIMS  Conference on  Environmental
Epidemiology,  June 28-July 2, 1982,  Alta UT.   SIAM Publication.

Brown, C.C. and  K.C. Chu.   1983b.  Implications  of the multistage theory  of
carclnogenesls  applied   to  occupational  arsenic  exposure.   J.  Nat.  Cancer
Inst.  70: 455-463.

Brown, C.C. and  K.C.  Chu.   1983c.   A  new method for  the  analysis  of  cohort
studies;  Implications of the multistage theory of carclnogenesls  applied  to
occupational  arsenic  exposure.  Environ. Health Persp.   50: 293-308.
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Enterllne,  P.E.  and  6.M.  Marsh.   1982.   Cancer  among  workers  exposed  to
arsenic  and  other  substances In  a  copper smelter.   Am.  J. Epidemic!.  116:
895-911.

Hlgglns,  I.   1982.    Arsenic  and   respiratory  cancer   among  a   sample  of
Anaconda  smelter  workers.   Report  submitted  to  the   Occupational  Safety
Health  Administration  In  the  comments  of   the  Kennecott  Minerals  on  the
Inorganic arsenic rulemaklng  (Exhibit 203-5).

Lee-Feldsteln, A.   1983.   Arsenic  and  respiratory cancer  In  man:  Follow-up
of an  occupational study.   In:  Arsenic: Industrial.  Blomedlcal, and Environ-
mental  Perspectives,   VI.  Lederer  and  R.  Fensterhelm,   Eds.    Van Nostrand
Relnhold, New York.

U.S.  EPA.   1984a.   Health  Effects  Assessment for  Arsenic.   Prepared  by the
Office  of  Health  and Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati,  OH for  the  Office  of  Emergency and Remedial
Response, Washington,  DC.

U.S.  EPA.  1984b.  Health Assessment  Document for  Inorganic Arsenic.  Office
of Health  and Environmental  Assessment,  Environmental Criteria and Assess-
ment  Office, Research  Triangle  Park,  NC.   EPA-600/8/83-021F.   NTIS  PB84-
190891.

U.S.  EPA.   1990.    Integrated  Risk  Information   System   (IRIS).   Online.
Office  of  Health  and Environmental  Assessment.  Environmental  Criteria  and
Assessment Office,  Cincinnati, OH.

Asbestos
NTP  (National Toxicology  Program).   1985.    Toxicology  and  carclnogenesls
studies  of   chrysotlle  asbestos  (CAS  No.  1200-29-5) In  F344/N  rats  (feed
studies) technical  report series No. 295.

U.S.  EPA.   1985.  Drinking Water Criteria  Document  for  Asbestos.  Prepared
by the  Office of Health  and Environmental Assessment, Environmental Criteria
and  Assessment  Office,  Cincinnati,  OH  for  the  Office  of Drinking  Water,
Washington,  DC.   Final Draft.   NTIS  PB 86-118262.

U.S.  EPA.   1986.  Airborne Asbestos  Health  Assessment Update.   Prepared  by
the  Environmental  Criteria and  Assessment  Office,  Research  Triangle  Park,
NC.  EPA 600/8-84/003F.

U.S.   EPA.    1990.    Integrated   Risk  Information   System   (IRIS).   Online.
Office  of  Health  and  Environmental Assessment,  Environmental  Criteria  and
Assessment Office,  Cincinnati, OH.

Azobenzene
NCI  (National Cancer  Institute).  1979.   Bloassay  of  azobenzene for possible
carclnogenlclty.   NCI  Carclnogenesls Technical Report Series.   No. 154.  U.S.
DHEW Publ.  No. (NIH)  79-1710.   p.  112.
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U.S.  EPA.   1985.  Health  and  Environmental Effects  Profile  for Azobenzene.
Prepared by  the  Office  of  Health and Environmental Assessment, Environmental
Criteria  and  Assessment  Office,  Cincinnati,   OH  for  the  Office  of  Solid
Waste. Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.
Benzene
Ott, M.G..  J.C.  Townsend.  W.A.  Flshbeck and  R.A.  Langner.
among  workers occupatlonally  exposed  to  benzene.   Arch.
33: 3-10.
                         1978.  Mortality
                         Environ.  Health.
Rlnsky,  R.A..  R.J.  Young  and   A.B.  Smith.   1981.   Leukemia  In  benzene
workers.  Am. J. Ind. Med.  2: 217-245.

U.S.  EPA.   1985.   Interim Quantitative  Cancer  Unit  Risk Estimates  Due  to
Inhalation of  Benzene.   Prepared by  the  Office of  Health and Environmental
Assessment,  Carcinogen  Assessment..  Group,  Washington,  DC  for  the  Office  of
Air Quality Planning and Standards,  Washington. DC.
U.S. EPA.   1987.   Memorandum from J. Orme HEB,
and Standards Division, ODW, June, 1987.
             CSD/ODW to C. Vogt. Criteria
U.S.  EPA.   1989.   Updated  Health  Effects Assessment  for  Benzene.   Prepared
by  the Office of  Health  and Environmental Assessment, Environmental Criteria
and  Assessment  Office,  Cincinnati.  OH  for  the  Office   of  Emergency  and
Remedial Response, Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office of  Health   and  Environmental Assessment,  Environmental  Criteria  and
Assessment Office. Cincinnati, OH.

Wong, 0.. R.W.  Morgan  and  M.D. Whorton.  1983.   Comments  on  the NIOSH study
of  leukemia  In  benzene workers.   Technical  report  submitted  to  Gulf Canada,
Ltd., by  Environmental Health Associates,  August  31.   (Cited  In  U.S.  EPA,
1985)

Benzldlne
U.S.  EPA.   1980.    Ambient  Water  Quality Criteria Document  for  Benzldlne.
Prepared by the Office of Health and Environmental  Assessment, Environmental
Criteria  and  Assessment  Office,   Cincinnati,  OH   for  the Office   of  Water
Regulations   and  Standards,  Washington,   DC.    EPA-440/5-80-023.   NTIS  PB
81-117343.

U.S.  EPA.   1986.   Health  and Environmental Effects  Profile  for  Benzldlne.
Prepared by the Office of Health and Environmental  Assessment, Environmental
Criteria and Assessment Office, Cincinnati, OH for  the Office of Solid Waste
and Emergency Response, Washington, DC.
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U.S. EPA.  1987.   Health  Effects  Assessment for BenzlcMne.   Prepared  by the
Office of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office,  Cincinnati,  OH for  the  Office  of Emergency  and  Remedial
Response, Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information   System  (IRIS).   Online.
Office of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati,  OH.

Zavon, M.R., U.  Hoegg  and E.  Blngham.  1973.   Benzldlne  exposure as a cause
of bladder tumors.  Arch.  Environ. Health.  27: 1-73.

Benzo(a)anthracene
U.S. EPA.  1984.   Health  Effects  Assessment for Selected  PAHs.   Prepared by
the  Office  of  Health  and Environmental  Assessment, Environmental  Criteria
and  Assessment  Office,   Cincinnati,  OH  for  the   Office  of  Emergency  and
Remedial  Response, Washington,  DC.

U.S. EPA.   1990.  Carcinogen  Risk  Assessment  Verification  Endeavor (CRAVE)
Work  Group.   Verified, pending  concurrence  on final  coversheet and  Input
onto IRIS.

Benzo(a)pyrene
Neal, J.  and R.H.  Rlgdon.   1967.  Gastric  tumors  In mice fed benzo[a]pyrene:
A quantitative study.  Tex. Rep. Blol.  Med.  25: 553.

Thyssen,  3., J.  Althoff,  G. Klmmerle and  U.  Mohr.   1981.   Inhalation studies
with  benzo[a]pyrene  In   Syrian  golden  hamsters.   J.  Natl.  Cancer  Inst.
66(3): 575-577.

U.S. EPA.   1980.   Ambient  Water  Quality  Criteria  Document  for  Polynuclear
Aromatic  Hydrocarbons.  Prepared  by the  Office of Health and Environmental
Assessment,  Environmental  Criteria and  Assessment Office,  Cincinnati,  OH for
the  Office  of  Water Regulations  and Standards, Washington.  DC.   EPA-440/5-
80-069.   NTIS PB 81-117806.

U.S.  EPA.   1990.   Integrated  Risk  Information   System  (IRIS).   Online.
Office of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati,  OH.

Benzo(b)f1uoranthene
U.S. EPA.  1984.   Health  Effect Assessment  for  PAHs.   Prepared by the Office
of   Health   and   Environmental  Assessment.   Environmental  Criteria   and
Assessment Office,  Cincinnati,  OH for  the  Office  of Emergency  and  Remedial
Response, Washington, DC.

U.S. EPA.   1990.  Carcinogen  Risk  Assessment  Verification  Endeavor (CRAVE)
Work Group.   Verified, pending  concurrence  on final  coversheet and  Input
onto IRIS.
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 Benzo(k)fluoranthene
 U.S.  EPA.   1987.   Health  and  Environmental  Effects Profile  for  Benzo(k)-
 fluoranthene.   Prepared, by  the Office  of  Health and  Environmental  Assess-
 ment,  Environmental  Criteria and  Assessment Office, Cincinnati, OH  for the
 Office of Solid Waste and Emergency Response, Washington, DC.

 BenzotMchlorlde
 Fukuda, K.,  H.  Metsushlta and K.  Takemoto.   1978.  Carclnogenlclty of benzo-
 trlchlorlde  by  the oral route  of  administration (J-4774).   In:   Proc.  52nd
 Ann.  Meet.   Japanese  Industrial Health  Assoc.   TSCA 8E  Submission Document
 No. 88-8000360, Flche #204867.  p. 516-517.

 U.S.  EPA.   1986.   Health  and  Environmental  Effects Profile  for  Benzotrl-
 chlorlde.   Prepared  by  the Office of  Health and  Environmental  Assessment,
 Environmental Criteria  and  Assessment Office, Cincinnati,  OH for  the Office
 of Solid Waste and Emergency Response. Washington, DC.

 U.S.  EPA.   1989.   Carcinogen Risk Assessment Verification Endeavor  (CRAVE)
 Work  Group.   Verified,  pending concurrence on  final  coversheet  and  Input
 onto IRIS.

 Benzyl Chloride
 Lljlnskl, W.   1986.   Chronic bloassay  of benzyl  chloride  In  F344 rats and
 (C57BL/6J x BALB/OF] mice.   J.  Natl.  Cancer  Inst.  76:1231-1236.

 U.S.  EPA.   1986.    Health   and Environmental   Effects   Profile  for  Benzyl
 Chloride.   Prepared  by  the Office of  Health and  Environmental  Assessment,
 Environmental Criteria  and  Assessment Office, Cincinnati,  OH for  the Office
 of Solid Waste and Emergency Response, Washington, DC.

 U.S.  EPA.   1990.    Integrated   Risk   Information  System   (IRIS).    Online.
 Office  of Health  and  Environmental   Assessment,  Environmental Criteria  and
 Assessment Office,  Cincinnati, OH.

 Beryllium
 Schroeder. H.A. and M. Kitchener.  1975.  Life-term  studies In rats:  Effects
 of aluminum, barium,  beryllium and tungsten.   J.  Nutr.  105(4): 421-427.

 U.S. EPA.   1986.   Drinking  Water  Criteria Document  for  Beryllium.   Prepared
 by the Office of Health  and Environmental  Assessment, Environmental Criteria
 and  Assessment  Office,  Cincinnati,   OH  for   the  Office  of  Drinking  Water,
 Washington,  DC.

 U.S.  EPA.   1987.   Health  Assessment  Document   for  Beryllium.   Office  of
 Health and  Environmental Assessment,  Environmental  Criteria  and  Assessment
 Office, Research Triangle Park,  NC. EPA-600/8-84-026F.

 U.S.  EPA.   1990.    Integrated   Risk   Information  System  (IRIS).    Online.
 Office of  Health   and  Environmental   Assessment,  Environmental Criteria  and
 Assessment Office,  Cincinnati, OH.

Wagoner,   J.K.,  P.F.  Infante  and   D.L.  Bayllss.   1980.   Beryllium:   An
 etlologlc  agent  In the  Induction  of  lung cancer, nonneoplastlc  respiratory
disease,   and heart  disease among  Industrially   exposed  workers.   Environ.
 Res.   21:  15-34.


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B1s (2-ch1oroethy1)ether
Innes, J.R.M.,  B.M.  inland,  M.G. Valeric  et  al.  1969.   Bloassay  of  pesti-
cides  and  Industrial  chemicals  for  tumorlgenlclty  In  mice: A  preliminary
note.  J. Natl. Cancer Inst.   42: 101-1114.

U.S.  EPA.   1980.   Ambient  Mater Quality  Criteria  Document  for  Chloroalkyl
Ethers.   Prepared  by  the  Office  of  Health  and  Environmental  Assessment,
Environmental Criteria  and  Assessment  Office, Cincinnati, OH  for  the  Office
of Mater Regulations and  Standards, Washington,  DC.   EPA-440/5-80-030.   NTIS
PB 81-117418.

U.S.  EPA.    1987.   Health  Effects  Assessment  for  B1s(2-Chloroethyl)Ether.
Prepared by  the Office  of Health and  Environmental  Assessment, Environmental
Criteria and  Assessment  Office,  Cincinnati,  OH  for  the Office of  Emergency
and Remedial  Response, Mashlngton,  DC.

U.S.  EPA.    1990.    Integrated  Risk   Information   System  (IRIS).    Online.
Office of  Health  and  Environmental  Assessment,  Environmental Criteria  and
Assessment Office.  Cincinnati, OH.

B1s(choromethy1)ether
Kuschner, M.,  S.  Laskln, R.T.  Drew,  et al.   1975.   Inhalation  carclnogen-
Iclty  of alpha halo ethers:  III.  Lifetime  and  limited  period  Inhalation
studies  with bls(chloromethyl)  ether  at  0.1 ppm.   Arch. Environ.  Health.
30(2): 73-77.

U.S.  EPA.    1990.    Integrated  Risk   Information   System  (IRIS).    Online.
Office of  Health  and  Environmental  Assessment,  Environmental Criteria  and
Assessment Office.  Cincinnati, OH.

B1s(2-ch1oro-l-methy1ethyl)ether
NTP  (National  Toxicology Program).   1982.   Carcinogenic  Bloassay  of  B1s(2-
Chloro-1-Methylethyl)   Ether   (=70%)   Containing   2-Chloro-l-Ethylethyl-(2-
Chloropropyl) Ether  (=30%)  1n B6C3F1  Mice (Gavage Study).   NCI  Carcinogen.
Tech. Rep.  Ser. No.  239.  105 p.   [Also publ.  as  DHHS (NIH) 83-1795.]

U.S.  EPA.  1987.  Health and Environmental Effects Document  for  Haloethers.
Prepared by  the Office  of Health and  Environmental  Assessment, Environmental
Criteria and Assessment Office,  Cincinnati, OH for  the Office of  Solid  Maste
and Emergency Response,  Mashlngton,  DC.

B1s(2-ethy1hexy1)  phthalate
NTP   (National  Toxicology   Program).    1982.    Carclnogenesls bloassay  of
d1(2-ethylhexyl) phthalate  (CAS  No.  117-81-7) In  F344 rats and  B6C3F1  mice
(feed study).  NTP  Tech. Report.  Ser.  No. 217. NIH/PUB-82-1773.

U.S. EPA.  1986.  Health and  Environmental  Effects  Profile for Phthallc  Add
Alkyl, Aryl  and Alkyl/Aryl  Esters.   Prepared  by  the  Office of  Health  and
Environmental  Assessment,  Environmental  Criteria  and  Assessment  Office,
Cincinnati,   OH for   the Office of  Solid  Maste  and  Emergency  Response,
Mashlngton,  DC.
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 U.S.   EPA.   1987.   Health  Effects   Assessment   for  Selected  PhthaHc  Acid
 Esters.   Prepared  by  the  Office  of  Health and  Environmental  Assessment,
 Environmental  Criteria and  Assessment  Office,  Cincinnati, OH for  the  Office
 of Emergency and  Remedial  Response, Washington,  DC.

 U.S.   EPA.   1990.    Integrated   Risk  Information   System  (IRIS).   Online.
 Office of  Health and  Environmental  Assessment, Environmental  Criteria  and
 Assessment  Office,  Cincinnati, OH.

 Bromodlchloromethane
 NTP  (National  Toxicology  Program).    1986.   NTP   technical  report  on  the
 toxicology  and   carclnogenesls   studies  of  bromodlchloromethane  (CAS  No.
 75-27-4)  In F344 rats and  B6C3F1 mice  (gavage  studies).  Board Draft.   NTP,
 Research  Triangle Park, NC.  NTP  TR 321.

 U.S.   EPA.   1987.  Health  Effects  Assessment  for  Trlhalogenated  Methanes.
 Prepared  by the  Office of Health and Environmental  Assessment,  Environmental
 Criteria  and  Assessment Office,  Cincinnati,  OH  for  the  Office  of  Emergency
 and Remedial Response. Washington, DC.  ECAO-CIN-H083.

 U.S.  EPA.  1990.   Carcinogen  Risk  Assessment  Verification  Endeavor (CRAVE)
 Work  Group.   Verified,  pending  concurrence  on  final  coversheet  and   Input
 onto  IRIS.

 Bromoethene
 Benya,  T.J.,  W.M.  Basey,  M.A.  Dorato  and  P.E.  Berteau.   1982.   Inhalation
 carclnogenlclty   bloassay   of  vinyl   bromide    In   rats.   Toxlcol.   Appl.
 Pharmacol.  64:367-379.

 U.S.  EPA.  1984.   Health and Environmental Effects  Profile  for  Bromoethene.
 Prepared  by the  Office of  Health  and  Environmental  Assessment, Environmental
 Criteria  and   Assessment  Office,  Cincinnati,  OH for  the  Office  of   Solid
 Waste, Washington, DC.

 Bromoform
 NTP   (National   Toxicology  Program).    1988.    Technical   Report   on   the
 toxicology and carclnogenesls studies of  trlhalomethane (bromoform) (CAS  No.
 75-25-2)  In F344/N rats and B6C3F1 mice {gavage studies).  Board Draft.

 U.S.  EPA.  1989.   Health  and  Environmental  Effects  Document  for  Bromoform.
 Prepared  by the Office of  Health  and  Environmental  Assessment, Environmental
 Criteria  and Assessment Office, Cincinnati, OH  for  the  Office of Solid Waste
 and Emergency Response, Washington,  DC.

 U.S.  EPA.  1990.   Carcinogen Risk  Assessment Verification  Endeavor (CRAVE)
 Work  Group.   Verified,  pending   concurrence  on  final  coversheet  and   Input
 onto IRIS.

 1.3-Butadlene
 Hazleton  Laboratories.  1981.  The Toxldty and  Carclnogenlclty  of Butadiene
 Gas  Administered  to  Rats  by   Inhalation   for  Approximately   24  Months.
 Prepared  for the  International  Institute  of Synthetic  Rubber  Producers, New
 York,  NY.   Unpublished.  (Cited  In U.S.  EPA,  1985)
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U.S. EPA.   1985.   Mutagen1c1ty and  Carclnogenlclty Assessment  of  1,3-Buta-
dlene.   Office  of  Health  and Environmental Assessment. Washington.  DC.   EPA
600/8-85-004F.  NTIS PB86-125507.

U.S. EPA.   1989.    Health  and Environmental  Effects  Document  for  1,3-Buta-
dlene.    Prepared   by  the  Office  of  Health  and  Environmental  Assessment,
Environmental Criteria and  Assessment  Office, Cincinnati, OH  for  the Office
of Solid Waste and Emergency Response,  Washington,  DC.

U.S.  EPA.   1990.   Integrated  Risk  Information   System  (IRIS).    Online.
Office  of  Health   and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

Butyl benzyl phthalate
U.S.  EPA.   1987.   Health  Effects  Assessment   for  Selected  Phthallc  Add
Esters.   Prepared  by  the  Office  of  Health and  Environmental  Assessment,
Environmental Criteria and  Assessment  Office, Cincinnati. OH  for  the Office
of Emergency and Remedial  Response, Washington,  DC.

U.S.  EPA.   1990.   Integrated  Risk  Information   System  (IRIS).    Online.
Office  of  Health   and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

Cadmium
Thun,  M.J.,  T.M.   Schnorr.  A.B.  Smith  and W.E.  Halperln.  1985.  Mortality
among  a cohort of U.S.  cadmium  production  workers:  An  update.    J.  Natl.
Cancer Inst.  74(2): 325-333.

U.S. EPA.   1984.   Health Effects  Assessment  for  Cadmium.  Prepared  by  the
Office  of  Health   and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office,  Cincinnati,  OH  for  the  Office  of Emergency  and  Remedial
Response, Washington,  DC.

U.S.  EPA.   1985.   Updated  mutagenlclty  and Carclnogenlclty  Assessment  of
Cadmium: Addendum  to  the  Health Assessment Document  for  Cadmium  (May 1981,
EPA 600/8-81-023).  EPA 600/8-83-025F.

U.S. EPA.   1988.   Updated  Health  Effects  Assessment for  Cadmium.   Prepared
by  the  Office of  Health and Environmental  Assessment,  Environmental  Criteria
and  Assessment  Office,  Cincinnati,  OH  for   the   Office  of  Emergency  and
Remedial Response. Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information   System  (IRIS).    Online.
Office  of Health   and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

Captafol
U.S.  EPA.    1984.    Health   and  Environmental  Effects  Profile  for  Captafol.
Prepared by  the Office of Health and Environmental Assessment, Environmental
Criteria  and Assessment  Office,  Cincinnati, OH  for  the  Office   of  Solid
Waste, Washington, DC.
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Captan
U.S.  EPA.   1984.    Health  and  Environmental  Effects  Profile  for  Captan.
Prepared  by  the  Office  of  Health  and Environmental Assessment, Environmental
Criteria  and  Assessment  Office,  Cincinnati,  OH  for  the  Office of  Solid
Waste, Washington. DC.

U.S.  EPA.   1988.  Carcinogen  Risk  Assessment  Verification  Endeavor  (CRAVE)
Workgroup  Verified,  pending concurrence  on  final  coversheet  and Input onto
IRIS.

Carbazole
Tsuda, H.,  A.  Hazlwara, M. Shlbata.  M.  Ohslma and N.  Ito.   1982.  Carcino-
genic effect  of  carbazole  In  the  liver  of (C57BL/6N  x  C3H/HeN)Fi mice.   J.
Natl. Cancer Inst.  69:1383-1389.

U.S.  EPA.   1986.  Health  and Environmental  Effects  Profile  for Carbazole.
Prepared  by  the  Office  of  Health  and Environmental Assessment, Environmental
Criteria and Assessment Office, Cincinnati, OH  for the Office of Solid Waste
and Emergency Response, Washington.  DC.

Carbon tetrachlorlde
Delia  Porta,  6.B.,  B.  Terraclnl  and K.P.  Shublk.   1961.    Induction  with
carbon tetrachlorlde  of liver  cell  carcinomas  In  hamsters.   J.  Natl.  Cancer
Inst.  26: 855-863.

Edwards.  J.,  W.E.  Heston  and  H.A.   Dalton.   1942.  Induction  of the  carbon
tetrachlorlde hepatoma In  strain  L mice.   J.  Natl.  Cancer Inst.  3: 297-301.

NCI  (National  Cancer  Institute).    1976.   Report  on  the  Carclnogenesls
Bloassay  of  Chloroform.   Carclnogenesls  Program,  Division  of  Cancer  Cause
and Prevention, Washington. DC.

U.S.  EPA.   1984a.    Health  Assessment  Document  for  Carbon  Tetrachlorlde.
Office of  Health  and Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati,  OH.  EPA-600/8-82-001F.   NTIS PB 85-124196.

U.S.  EPA.   1984b.   Health Effects   Assessment   for  Carbon  Tetrachlorlde.
Prepared by the  Office  of  Health  and Environmental Assessment, Environmental
Criteria and  Assessment Office,  Cincinnati,   OH for  the Office  of Emergency
and Remedial Response, Washington. DC.

U.S.  EPA.   1990.    Integrated  Risk  Information   System  (IRIS).   Online.
Office of  Health  and Environmental  Assessment,  Environmental  Criteria  and
Assessment Office,  Cincinnati,  OH.

Chloranyl
BRL  (Blonetlcs   Research  Labs, Inc.).   1968.   Evaluation of  carcinogenic,
teratogenlc and  mutagenlc  activities  of  selected  pesticides  and Industrial
chemicals.  Volume I:  Carcinogenic  Study.  NTIS PB 223159.

U.S.  EPA.   1986.  Health  and  Environmental  Effects  Profile  for Chloranyl.
Prepared by the  Office of  Health  and  Environmental Assessment, Environmental
Criteria and Assessment Office, Cincinnati, OH  for the  Office of Solid Waste
and Emergency Response,  Washington,  DC.
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Chlordane
IROC  (International  Research  and  Development  Corporation).   1973.   Unpub-
lished report to Velslcol Chemical Corporation, Eighteen  Month  Oral  Carcino-
genic Study In Mice,  December 14.  1973.

NCI  (National Cancer  Institute).   1977.   Bloassay of Chlordane  for  Possible
Carclnogenlclty.   NCI Cardnogenesls  Tech.  Rep. Ser. No.  8.   Also  publ.  as
DHEW Publ. No. (NIH)  77-808.

U.S.  EPA.   1986.   Carclnogenlclty  Assessment of  Chlordane and  Heptachlor/
Heptachlor  Epoxlde.   Prepared  by  the  Office  of  Health and  Environmental
Assessment. Carcinogen  Assessment  Group,  Washington, DC.   EPA-600/6-87-004.
Final Report.

U.S. EPA.  1988.  Updated Health Effects Assessment  for  Chlordane.   Prepared
by the Office of Health and  Environmental Assessment, Environmental  Criteria
and  Assessment  Office,  Cincinnati,  OH  for   the  Office  of  Emergency  and
Remedial  Response,  Washington, DC.

U.S.  EPA.   1990.    Integrated  Risk  Information  System  (IRIS).    Online.
Office of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office,  Cincinnati, OH.

4-Ch1oroan111ne
NCI  (National  Cancer  Institute).    1979.   Bloassay  of  p-chloroan1l1ne  for
possible  Carclnogenlclty.  NCI  Cardnogenesls  Tech Rep.  Ser. No. 189.   NTIS
PB295896.

U.S.  EPA.   1987.   Health and Environmental  Effects Document  for  Chloro-
anlllnes.  Prepared  by  the  Office of  Health  and Environmental  Assessment,
Environmental  Criteria  and Assessment  Office,  Cincinnati, OH for the Office
of Solid  Waste and  Emergency  Response,  Washington.  DC.

Chlorodlbromomethane
NTP  (National  Toxicology  Program).   1985.   Toxicology  and  Cardnogenesls
studies  of Chlorodlbromomethane   (CAS  No.   124-48-1)  In  F/344/N  rats  and
B6C3F1 mice.   NTP  Tech.  Rep.  Ser.  No. 282.  DHHS No. NIH 85-2538.

U.S.  EPA.   1987.   Health Effects  Assessment  for Trlhalogenated  Methanes.
Prepared  by the Office  of Health and  Environmental Assessment,  Environmental
Criteria  and  Assessment  Office,  Cincinnati,  OH for  the  Office  of  Emergency
and Remedial  Response, Washington,  DC.   ECAO-CIN-H083.

Chloroform
Jorgenson, T.A., E.F. Melerhenry,  C.J.  Rushbrook   et al.   1985.   Carclnogen-
lclty of  chloroform In drinking water to male  Osborne-Mendel  rats and female
B6C3F1 mice.   Fund.  Appl.  Toxlcol.  (U.S.A.)   5(4):  760-769.

NCI  (National  Cancer  Institute).   1976.   Report   on Cardnogenesls  Bloassay
of Chloroform.   NTIS PB264-018.

U.S.  EPA.   1985.   Health Assessment  Document  for  Chloroform.   Office  of
Health and  Environmental  Assessment,  Environmental  Criteria and Assessment
Office, Cincinnati, OH Research Triangle Park,  NC.   EPA  600/8-84-004F.   NTIS
PB86-105004.
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U.S.   EPA.    1988.    Updated  Health  Effects   Assessment  for  Chloroform.
Prepared by the Office  of  Health  and Environmental  Assessment, Environmental
Criteria and  Assessment Office,  Cincinnati,  OH  for the  Office of  Emergency
and Remedial Response, Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).    Online.
Office  of  Health and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

Chloromethane
CUT  (Chemical  Industry Institute  of Toxicology).   1981.  Final  report  on
24-month Inhalation study  on  methyl  chloride.  Prepared by Battelle-Columbus
Laboratories,  Columbus, OH.  December 31.

NIOSH  (National  Institute  for   Occupational  Safety  and  Health).   1984.
Carcinogenic Risk Assessment  for  Occupational Exposure to Monohalomethanes.
NTIS PB85-111623.

U.S.  EPA.   1986.   Health and   Environmental   Effects   Profile  for  Methyl
Chloride.   Prepared  by  the  Office  of Health and  Environmental  Assessment,
Environmental  Criteria  and Assessment Office, Cincinnati, OH  for  the Office
of Solid Waste and Emergency Response, Washington, DC.

U.S. EPA.   1987.   Health Effects  Assessment  for  Chloromethane.  Prepared  by
the  Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria
and  Assessment  Office,  Cincinnati,  OH  for  the  Office of   Emergency  and
Remedial Response, Washington. DC.

4-Chloro-2-methy1an1l1ne
U.S. EPA.   1986.   Health  and  Environmental  Effects Profile  for  4-Chloro-2-
methylanlUne  and  4-Chloro-2-methylan1l1ne  hydrochlorlde.   Prepared by  the
Office  of  Health and  Environmental  Assessment,  Environmental  Criteria  and
Assessment  Office,   Cincinnati,   OH  for  the  Office  of  Solid  Waste  and
Emergency Response,  Washington. DC.

Welsburger,  E.K.,  A.B.  Russfleld,  F.  Homburger, et  al.   1978.  Testing  of
twenty-one  environmental  aromatic   amines   or   derivatives   for   long-term
toxlclty or  carclnogenlclty.   J.  Environ. Pathol. Toxlcol.  2:325-356.

4-Chloro-2-methylan111ne hydrochlorlde
U.S. EPA.   1986.   Health  and  Environmental  Effects Profile  for  4-Chloro-2-
methylanlllne  and  4-Chloro-2-methylan111ne  hydrochlorlde.   Prepared by  the
Office  of  Health  and  Environmental  Assessment,  Environmental Criteria  and
Assessment  Office,   Cincinnati,   OH  for  the  Office  of  Solid  Waste  and
Emergency Response,  Washington, DC.

Welsburger,  E.K., A.B.  Russfleld,  F.  Homburger, et  al.   1978.  Testing  of
twenty-one  environmental  aromatic   amines   or   derivatives   for   long-term
toxlclty or  carclnogenlclty.   J.  Environ. Pathol. Toxlcol.  2:  325-356.

Chloromethyl methyl  ether
U.S. EPA.   1987.  Health and  Environmental  Effects  Document  for  Haloethers.
Prepared by the Office of  Health  and Environmental  Assessment, Environmental
Criteria and Assessment Office, Cincinnati,  OH for  the Office  of Solid  Waste
and Emergency  Response,  Washington,  DC.


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U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).    Online.
Office  of  Health and  Environmental  Assessment,  Environmental Criteria  and
Assessment Office, Cincinnati,  OH.

o-Chloronltrobenzene
U.S. EPA.   1985.   Health  and Environmental Effects Profile  for  Chloronltro-
benzenes.   Prepared  by the  Office of  Health  and  Environmental  Assessment,
Environmental Criteria and  Assessment  Office,  Cincinnati, OH  for  the Office
of Solid Waste and Emergency Response,  Washington, DC.

Welsburger,  E.K.,  A.B.  Russfleld,  F.  Homburger,  et al.   1978.   Testing  of
twenty-one  environmental   aromatic  amines  or   derivatives   for   long-term
toxldty or cardnogenldty.  J.  Environ.  Pathol.  Toxlcol.  2:325-356.

p-Chloron1trobenzene
U.S. EPA.   1985.   Health  and Environmental Effects Profile  for  Chloronltro-
benzenes.   Prepared  by the  Office of  Health  and  Environmental  Assessment,
Environmental Criteria and  Assessment  Office,  Cincinnati, OH  for  the Office
of Solid Waste and Emergency Response,  Washington, DC.

Welsburger,  E.K.,  A.B.  Russfleld,  F.  Homburger,  et al.   1978.   Testing  of
twenty-one  environmental   aromatic  amines  or   derivatives   for   long-term
toxldty or cardnogenldty.  J.  Environ.  Pathol.  Toxlcol.  2:325-356.

Chlorthalonll
NCI  (National   Cancer  Institute).    1978.   Bloassay  of  chlorothalonll  for
possible   cardnogenldty.   DHEW   Publ.   NIH-78-841,  NCI-C6-TR-41.    NTIS
PB-286369.

U.S.  EPA.   1984.   Health   and  Environmental  Effects  Profile  for  Chlor-
thalonll.   Prepared  by the  Office of  Health  and  Environmental  Assessment,
Environmental Criteria and  Assessment  Office,  Cincinnati, OH  for  the Office
of Solid Waste,  Washington,  DC.

Chromium (VI)
Hancuso,  T.F.    1975.   International   Conference   on  Heavy  Metals  In  the
Environment, Toronto, Canada, Oct.  27-31.   (Cited  In U.S.  EPA,  1984)

U.S.  EPA.    1984a.   Health  Assessment  Document   for  Chromium.   Office  of
Health  and  Environmental  Assessment,  Environmental Criteria  and  Assessment
Office, Cincinnati,  OH.  EPA-600/8-83-014F.  NTIS  PB 85-115905.

U.S.  EPA.   1984b.    Health Effects  Assessment   for   Hexavalent   Chromium.
Prepared by the Office of Health and Environmental  Assessment. Environmental
Criteria and Assessment Office,  Cincinnati,  OH for the Office of  Emergency
and Remedial Response,  Washington.  DC.

U.S. EPA.   1986.   Integrated Risk  Information  System (IRIS).  Risk estimate
for   cardnogenldty  for   chromlum(VI).    Online.     (Verification   date
06/26/86.)   Office   of  Health  and Environmental  Assessment,   Environmental
Criteria and Assessment Office, Cincinnati, OH.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).    Online.
Office  of  Health and  Environmental  Assessment,  Environmental Criteria  and
Assessment Office, Cincinnati.  OH.


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Chrysene
U.S.  EPA.    1984.   Health  and  Environmental  Effects  Profile  for  Chrysene.
Prepared by  the  Office  of Health  and Environmental Assessment, Environmental
Criteria  and  Assessment  Office,  Cincinnati,  OH  for  the  Office  of  Solid
Waste, Washington, DC.

U.S.  EPA.   1990.  Carcinogen  Risk Assessment  Verification  Endeavor  (CRAVE)
Work  Group.    Verified,  pending  concurrence  on  final  coversheet  and  Input
onto IRIS.

Coal tars
Mazumdar, S.,  C.  Redmond, W.  Solleclto and N.  Sussman.   1975.  An epldemlo-
loglcal  study  of  exposure  to  coal-tar-pitch volatlles   among   coke  oven
workers.  APCA 3.  25(4): 382-389.

Redmond, C.K., H.S. Wleand, H.E.  Rockette  et  al.   1979.   Long-term mortality
experience  of  steelworkers.    Prepared  under  Contract  No.  HSH-99-71-32.
NIOSH, Cincinnati, OH.  June.

U.S.  EPA.   1984.   Carcinogen  Assessment of  Coke  Oven Emissions.   Office of
Health  and  Environmental  Assessment,  Washington,  DC.   EPA-600/6-82-003F.
NTIS PB 84-170182.

Creosote
U.S.  EPA.   1990.   Integrated  Risk  Information  System   (IRIS).    Online.
Office  of  Health  and  Environmental Assessment,  Environmental Criteria  and
Assessment Office. Cincinnati, OH.

Cresol. Q-. m- and p-
U.S.  EPA.    1984.   Health  and Environmental   Effects  Profile for  Cresols.
Prepared by  the Office  of Health  and Environmental Assessment, Environmental
Criteria  and  Assessment  Office,   Cincinnati,  OH  for  the  Office  of  Solid
Waste, Washington, DC.

U.S.  EPA.   1990.   Carcinogen  Risk Assessment  Verification  Endeavor  (CRAVE)
Work  Group.    Verified,  pending  concurrence  on final  coversheet  and  Input
onto IRIS.

Crotonaldehyde
Chung, F.L., T. Tamaka  and S.S. Hecht.  1986.  Induction  of liver  tumors In
F344 rats by crotonaldehyde.  Can. Res.  46:  1285-1289.

U.S. EPA.   1989.   Health  and  Environmental Effects  Document for  Crotonalde-
hyde.   Prepared   by   the   Office   of  Health  and  Environmental  Assessment,
Environmental  Criteria  and  Assessment  Office, Cincinnati, OH  for  the Office
of Solid Waste and Emergency Response,  Washington,  DC.

ODD
Tomatls, L.,  V.   Turusov,  R.T.  Charles and  M. Bolcchl.   1974.    Effect  of
long-term   exposure   to    1,l-d1chloro-2,2-b1s(p-chlorophenyl)ethylene.   to
l,l-d1chloro-2.2-b1s(p-chlorophenyl)-ethane,   and   to   the    two   chemicals
combined on CF-1  mice.   J. Natl. Cancer Inst.   52(3): 883-891.
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U.S. EPA. 1990.   Integrated Risk  Information  System (IRIS).   Online.   Office
of   Health   and   Environmental   Assessment.   Environmental   Criteria   and
Assessment Office, Cincinnati. OH.

DDE
NCI  (National Cancer  Institute).   1978.   Bloassay of DDT. IDE  and p.p1  -DDE
for  possible  carclnogenlclty.  NCI  Report No.  131.   DHEW  Publ.  No.  (NIH)
78-1386.

Rossi.  L..  0.  Barb1er1t  M.  Sangulnetl.  J.R.P.  Cabral.  P.  Bruzzl  and  L.
Santl.   1983.   Carclnogenlclty  study  with  technical-grade  DDT  and DDE  In
hamsters.  Cancer Res.  43: 776-781.   (Cited In U.S. EPA. 1988)

Tomatls,  L.,  V.  Turusov,  R.T.  Charles  and  M.  Bolcchl.   1974.    Effect  of
long-term   exposure   to  l,l-d1chloro-2,2-b1s(p-chlorophenyl)ethylene,   to
l,l-d1chloro-2,2-b1s(p-chlorophenyl)-ethane,   and  to   the    two   chemicals
combined on CF-1 mice.  J.  Natl.  Cancer Inst.   52(3): 883-891

U.S. EPA. 1990.   Integrated Risk  Information  System (IRIS).   Online.   Office
of   Health   and   Environmental   Assessment,   Environmental   Criteria   and
Assessment Office. Cincinnati, OH.

DDT
U.S. EPA.  1984.  Health Effects  Assessment for  DDT.   Prepared by the Office
of  Health  and  Environmental  Assessment.  Environmental   Criteria  and  Assess-
ment  Office,   Cincinnati,   OH for  the  Office   of  Emergency  and  Remedial
Response. Washington. DC.  EPA 540/1-86-026.

U.S.  EPA.   1986.    The  Assessment   of   the   Carclnogenlclty  of  Dlcofol
(Kelthane). DDT,  DDE  and  ODD  (TDE).   Office of  Health  and  Environmental
Assessment. Washington. DC.  EPA/600/6-86/001.  NTIS PB87-110904.

U.S.  EPA.   1990.   Integrated  Risk   Information  System  (IRIS).   Online.
Office  of  Health and  Environmental  Assessment,  Environmental Criteria  and
Assessment Office, Cincinnati, OH.

Decabromodlphenyl oxide
U.S.  EPA.   1984.   Health  and Environmental  Effects Profile  for  Bromlnated
Dlphenyl  Ethers.   Prepared  by   the   Office   of  Health  and  Environmental
Assessment, Environmental  Criteria and Assessment Office,  Cincinnati,  OH for
the Office of  Solid Waste,  Washington,  DC.

U.S. EPA.   1987.   Health and  Environmental Effects  Profile  for Decabromodl-
phenyl  Oxide.   Prepared  by the  Office of  Health and  Environmental  Assess-
ment, Environmental  Criteria  and Assessment  Office,  Cincinnati,   OH  for  the
Office of Solid Waste. Washington  DC.

U.S.  EPA.   1990.   Integrated  Risk   Information  System  (IRIS).   Online.
Office  of  Health and  Environmental  Assessment,  Environmental Criteria  and
Assessment Office. Cincinnati, OH.
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Dlallate
BRL  (Blonetlcs  Research  Labs,  Inc.)   1968.   Evaluation  of  carcinogenic,
teratogenlc,  and  mutagenlc activities of  selected  pesticides and Industrial
chemicals,  Vol.  1, Carcinogenic Study.  Prepared  for  National  Cancer Insti-
tute, U.S.  Department of Commerce, Washington, DC.  NTIS PB-223159.

Innes,  J.R.M.,  B.M.  Ulland,  M.G. Valerlo, et  al.   1969.   Bloassay of pesti-
cides  and  Industrial  chemicals  for  tumorlgenldty In mice:   A preliminary
note.   J. Natl. Cancer Inst.  42:1101-1114.

U.S.  EPA.   1983.   Health and  Environmental  Effects  Profile  for  Dlallate.
Prepared  by the Office  of  Health and Environmental Assessment, Environmental
Criteria  and  Assessment   Office,  Cincinnati,  OH   for  the  Office  of  Solid
Waste,  Washington, DC.

D1benzo(a.h)anthracene
U.S.  EPA.  1990.   Carcinogen  Risk  Assessment  Verification  Endeavor  (CRAVE)
Work  Group.   Verified,  pending concurrence  on  final  coversheet and  Input
onto IRIS.

Dlbenzofuran
U.S.  EPA.  1989.   Carcinogen  Risk  Assessment  Verification  Endeavor  (CRAVE)
Work  Group.   Verified,  pending concurrence  on  final  coversheet and  Input
onto IRIS.

Dlbromochloromethane
NTP  (National  Toxicology  Program).   1985.    Toxicology   and  carclnogenesls
studies   of  chlorodlbromomethane  1n  F344/N  rats  and  B6C3F1  mice.    NTP
Technical Report Series No. 282.  NTIS/PB86-166675.

U.S.  EPA.   1987.   Health Effects  Assessment  for TMhalogenated  Methanes.
Prepared  by  the Office  of  Health and Environmental  Assessment,  Environmental
Criteria  and  Assessment  Office, Cincinnati,  OH  for the Office  of  Emergency
and Remedial Response, Washington,  DC.

U.S. EPA.   1989a.   Carcinogen Risk  Assessment  Verification  Endeavor  (CRAVE)
Work  Group.   Verified,  pending concurrence  on final  coversheet and  Input
onto IRIS.

U.S.  EPA.  1989b.  Health and Environmental  Effects  Document  for  Dlbromo-
chloromethane.  Prepared  by  the Office  of Health  and  Environmental  Assess-
ment, Environmental  Criteria  and Assessment  Office,  Cincinnati, OH  for  the
Office of Solid Waste and Emergency  Response,  Washington,  DC.

1.2-Dlbromo-3-chloropropane
SRC.   1982.   Review   of   Toxlcologlc  Data   In  Support  of  Evaluation  for
Carcinogenic  Potential  of  1,2-D1bromo-3-chloropropane.    TR-82-723.   (Cited
In U.S.  EPA, 1986)

U.S. EPA.   1985.   Drinking Water Criteria  Document  for  Dlbromochloropropane.
ECAO-CIN-410.

U.S. EPA.   1986.   Carcinogen Assessment Group (CAG)  Profiles.   Prepared  by
the Carcinogen Assessment Group.   Available through RCRA/Superfund Docket.
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1.2-Dlbromoethane
NCI  (National  Cancer  Institute).   1978.   Bloassay  of  1,2-dlbromoethane for
possible  carclnogenlclty.   NCI  Carclnogenesls  Technical  Report  Series No.
86. PB-288-428 [Also published as CHHA (NIH) 78-1336].  p. 64.

NTP   (National   Toxicology   Program).    1982.    Carclnogenesls  bloassay  of
1,2-dlbromoethane  In  F344   rats  and  B6C3F1  mice  (Inhalation Study),  NTP
Series No. 210.  NIH Pub. No. 82-1766.

U.S.  EPA.   1984.  Health and Environmental  Effects  Profile for l,2-D1bromo-
ethane.   Prepared by  the  Office  of  Health  and Environmental  Assessment,
Environmental  Criteria  and  Assessment Office, Cincinnati.  OH  for  the Office
of Solid Waste, Washington,  DC.

U.S.   EPA.    1987.    Health  Effects  Assessment   for   Ethylene  01 bromide.
Prepared by  the  Office  of Health  and Environmental Assessment, Environmental
Criteria and Assessment  Office, Cincinnati,  OH  for  the  Office of Emergency
and Remedial Response, Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health and  Environmental  Assessment,  Environmental  Criteria and
Assessment Office, Cincinnati, OH.

1.4-D1ch1orobenzene
NTP  (National Toxicology  Program).   1986.   Toxicology and  Carclnogenesls
Studies  of   1.4-D1chlorobenzene  In   F344/N  Rats  and B6C3F1  Mice   --  Galley
Draft.  U.S. DHHS, PHS. NIH  Tech.  Rep. Ser.  No. 319.

U.S.  EPA.   1987.  Health Effects Assessment  for  Dlchlorobenzenes.  Prepared
by the Office  of Health  and  Environmental  Assessment,  Environmental Criteria
and  Assessment  Office,  Cincinnati, OH  for  the  Office  of  Solid  Waste and
Emergency Response,  Washington, DC.

3.3'-Dlchlorobenzldlne
Stula, E.F., H.  Sherman. J.A. Zapp,  et al.   1975.   Experimental neoplasla In
rats  from  oral   administration  of  3,3'-d1chlorobenzld1ne,  4,4'-methylene-
b1s(2-chloroan1!1ne)   and  4,4'-methylene-b1s   (2-methylan1l1ne).    Toxlcol.
Appl. Pharmacol.   31: 159-175.

U.S.   EPA.    1988.  Health  and  Environmental  Effects  Document  for  3,3'-Dl-
chlorobenzldlne.   Prepared by the Office of  Health and  Environmental Assess-
ment,  Environmental  Criteria  and Assessment  Office, Cincinnati,  OH  for the
Office of Solid  Waste and Emergency  Response,  Washington,  DC.   EPA 600/8-89/
Oil.

1.4-D1chloro-2-butene
E.I.   Dupont  de  Nemours and  Co.   1986.   Long-term Inhalation   study  with
l,4-d1chlorobutene-2  (DCB)  In rats.   Final  report OTS 8(e) Flche 0509754.

U.S.   EPA.   1987.  Health and Environmental  Effects Document  for  Dlchloro-
butenes.   Prepared  by  the  Office  of Health  and Environmental  Assessment.
Environmental Criteria and Assessment  Office,  Cincinnati, OH  for  the  Office
of Solid Waste and Emergency  Response,  Washington.  DC.
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1.1-Dlchloroethane
NCI  (National  Cancer  Institute).   1978.  Bloassay  of  1,1-dlchloroethane  for
possible carclnogenldty.   NCI  Carclnogenesls Tech.  Rep.  Ser. No.  66,  DHEW
Publ. No. (NIH) 78-1316.

U.S.   EPA.    1984.   Health   Effects   Assessment   for   1,1-Dlchloroethane.
Prepared by the Office  of  Health  and  Environmental  Assessment, Environmental
Criteria and  Assessment Office,  Cincinnati, OH  for the Office of  Emergency
and Remedial Response, Washington, DC.

U.S.  EPA.   1985.   Health  and  Environmental  Effects  Profile for  Dlchloro-
ethanes.   Prepared by  the Office  of  Health  and  Environmental  Assessment,
Environmental  Criteria  and Assessment  Office.  Cincinnati, OH  for  the Office
of Solid Waste and Emergency Response,  Washington, DC.

1.2-D1ch1oroethane
NCI  (National  Cancer  Institute).   1978.  Bloassay  of  1,2-dlchloroethane  for
possible carclnogenldty.   NCI Carclnogenesls  Tech. Rep. Ser. No.  55,  DHEW
Publ. No. (NIH) 78-1361.

U.S.  EPA.   1985.    Health  Assessment  Document  for   1,2-Dlchloroethane.   EPA
600/8-84-006F.

U.S.  EPA.    1990.   Integrated  Risk   Information  System  (IRIS).    Online.
Office  of  Health  and  Environmental  Assessment,  Environmental Criteria  and
Assessment  Office, Cincinnati,  OH.

1.1-Dlchloroethylene
Maltonl, C.,  G. Lefemlne,  P.  Chleco  et al.  1985.   Experimental  research on
vlnylldene  chloride Carclnogenesls.  in:  Archives  of  Research on  Industrial
Carclnogenesls. Vol. 3, C. Maltonl and M. Mehlman,  Ed.   Princeton  Scientific
Publishers, Princeton, NJ.

NTP   (National  Toxicology  Program).   1982.    Carclnogenesls bloassay   of
vlnylldene  chloride (CAS  No.  75-35-4)  In  F344  rats and B6C3F1 mice (gavage
study).  NTP Tech. Rep.  Ser.  No.  228.  DHHS No.  NIH 82-1784.

U.S.  EPA.    1985.   Health  Assessment   Document  for   Vlnylldene   Chloride.
Office  of  Health  and  Environmental  Assessment,  Environmental Criteria  and
Assessment  Office,  Research  Triangle  Park, NC.   EPA-600/8-83-031F.   NTIS PB
86-100641.

U.S.  EPA.   1988.    Updated  Health Effects  Assessment  for  1.1-Dlchloroethy-
lene.   Prepared  by  the   Office  of  Health  and  Environmental   Assessment,
Environmental  Criteria  and  Assessment  Office.  Cincinnati, OH  for  the Office
of Emergency and Remedial  Response, Washington.  DC.

U.S.  EPA.    1990.   Integrated  Risk   Information  System  (IRIS).    Online.
Office  of  Health   and  Environmental  Assessment,  Environmental Criteria  and
Assessment  Office. Cincinnati,  OH.
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1,2-Dlchloropropane
NTP  (National   Toxicology  Program).   1986.   NTP  Technical  Report  on  the
Carclnogenesls   Studies  of  1,2-Dlchloropropane (Propylene  Dlchlorlde).   (CAS
No. 78-87-5) In F344/N rats and  B6C3F1  mice (gavage  studies).   NTP-82-092,
NIH Publ.  No.   84-2519,  NTP TR  263.   U.S.  DHHS,  PHS,  NIH.   August,  1986.
Draft.

U.S.  EPA.   1987.    Health  Effects  Assessment   for  1,2-Dlchloropropane.
Prepared by the Office  of Health  and  Environmental  Assessment,  Environmental
Criteria and Assessment Office, Cincinnati,  OH for  the Office of Solid Waste
and Emergency Response, Washington,  DC.

1.3-D1chloropropene
Lomax.  L.G..  W.T.  Stott.  K.A.  Johnson. L.L.  Calhoun, B.L.  Yano and  J.F.
Quast.   1989.   The chronic  toxlclty and  oncogenlcHy of  Inhaled  technical
grade  1,3-dlchloropropene   In  rats  and  mice.    Fund.  Appl.  Toxlcol.   12:
418-431.

NTP  (National   Toxicology  Program).   1985.  Toxicology and  carclnogenesis
studies of  telone  II  1n F344/N rats and B6C3F1 mice.   U.S.  Dept.  Health and
Human Services, Technical Report  Ser.  No. 269.

U.S. EPA.   1985.   Health and Environmental  Effects  Profile for  1,3-Dlchloro-
propene.   Prepared by  the  Office  of Health  and  Environmental  Assessment,
Environmental Criteria  and  Assessment  Office, Cincinnati, OH  for  the Office
of Solid Waste and Emergency Response.  Washington. DC.

U.S.   EPA.    1989.     Health   and   Environmental   Effects   Document   for
1,3-Dlchloropropene.   Prepared by  the  Office  of  Health  and  Environmental
Assessment, Environmental Criteria  and Assessment Office,  Cincinnati. OH for
the Office of Solid Waste and Emergency Response.  Washington. DC.

Dleldrln
Davis,  K.J.   1965.  Pathology report  on mice  fed  aldrln.  dleldrln. hepta-
chlor or heptachlor epoxlde for two years.   Int.  Food Drug Admin.

Melerhenrey, E.F., B.H.  Reuber, M.E. Gershwin et  al.   1983.  Dleldrlnlnduced
mallory bodies  In  hepatic  tumors  of mice of  different strains.   Hepatology.
3: 90-95.

NCI  (National  Cancer  Institute).   1978.   Bloassays  of aldrln  and  dleldrln
for  possible  carclnogenlclty.   National  Cancer   Institute  Carcinogen.  Tech.
Rep.  Ser.  No.  22.   NCI-CG-TR-22.   [Also  publ.   as  DHEW  Publ.  No.  (NIH)
78-882.]

Tennekes,  H.A.,  A.S.  Wright.  K.M.  Dlx  and J.H.  Koeman.   1981.   Effects of
dleldrln,  diet  and bedding  on  enzyme  function and tumor Incidences In livers
of male CF-1 mice.  Cancer  Res.  41: 3615-3620.

Thorpe,  E.  and A.I.   Walker.   1973.    Toxlclty  of   dleldrln   (HEOD).   II.
Comparative  long-term  oral  toxlclty  studies In  mice  with dleldrln,  DDT,
phenobarbltone,  beta-BHC  and  gamma-BHC.    Food  Cosmet.  Toxlcol.    11(3):
433-443.
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U.S.  EPA.   1987.   Health Effects  Assessment  for DleldMn.   Prepared  by the
Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria and
Assessment Office,  Cincinnati,  OH  for  the  Office of  Emergency and Remedial
Response, Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria and
Assessment Office, Cincinnati, OH.
Walker,
dleldrln
Toxlcol.
A.I.T.,  E.  Thorpe  and  D.E.  Stevenson.   1972.   The  toxicology of
 (HEOD):  I.  Long-term oral  toxldty studies  In  mice.   Food Cosmet.
 11: 415-432.
Dlethylstllbestrol
SRC.   1983.   levlew  of
Carcinogenic Potential of
                  Toxlcologlc  Data   In   Support   of   Evaluation  for
                 Dlethylstllbestrol.  TR-83-562.
U.S.  EPA.   1986.  Carcinogen  Assessment  Group (CAG)  Profiles.   Prepared by
the Carcinogen Assessment Group.  Available through RCRA/Superfund Docket.

3.3'-D1methoxybenz1d1ne
OSHA/NIOSH  (Occupational Safety  and  Health Administration/National Institute
for Occupational Safety and  Health).   1980.   Health hazard, alert benzldine,
o-tol1d1ne and o-dlanlsldlne based dyes.  DHHS (NIOSH) Publ. No. 81-106.

Sellakumar,  A.R..  R.  Montesano  and  A.  Safflotl.   1969.  Aromatic  amines
carclnogenlclty In hamsters.  Proc. Am. Assoc. Cancer Res.  10:78.

U.S.  EPA.    1987.   Health  and  Environmental  Effects  Profile  for  3,3'-D1-
methoxybenzldlne.   Prepared  by  the  Office  of  Health  and  Environmental
Assessment,  Environmental Criteria and Assessment  Office. Cincinnati,  OH for
the Office of Solid Waste and Emergency Response, Washington, DC.

2.4-D1methy1an1l1ne
U.S.  EPA.   1987.  Health and Environmental  Effects Profile for 2,4-Dlmethyl-
anlllne  and 2,4-Dlmethylanlllne  hydrochlorlde.   Prepared  by  the  Office of
Health  and Environmental  Assessment.  Environmental Criteria  and Assessment
Office, Cincinnati, OH for  the Office  of  Solid Waste and Emergency Response,
Washington, DC.
Welsburger,
twenty-one
toxlclty or
    E.K.,  A.B.  Russfleld,  F.  Homburger,
    environmental  aromatic  amines   or
   carclnogenlclty.   J. Environ. Pathol.
 et  al.   1978.   Testing of
derivatives  for  long-term
Toxlcol.  2:325-356.
2.4-Dlmethylan1l1ne hydrochlorlde
U.S. EPA.  1987.  Health and  Environmental  Effects  Profile for 2,4-Dlmethyl-
anlllne  and  2,4-D1methylan1llne hydrochlorlde.   Prepared  by  the  Office  of
Health  and  Environmental  Assessment,  Environmental  Criteria  and  Assessment
Office, Cincinnati, OH for the  Office  of  Solid  Waste and Emergency Response,
Washington,  DC.

Welsburger.  E.K.,  A.B.  Russfleld,  F.  Homburger,  et  al.   1978.   testing  of
twenty-one  environmental   aromatic  amines   or   derivatives   for   long-term
toxlclty or  carclnogenlclty.   J. Environ.  Pathol.  Toxlcol.  2:325-356.
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3.3'-D1methy1benz1d1ne
Grlswold,  D.P.,  Jr..  A.E.
1968.   The  carclnogenlcUy
heterocycllc nltro or amino
Cancer Res.   28(5):924-933.
 Casey.  E.K.  Welsburger  and  J.H.   Welsburger.
of multiple  Intragastrlc doses  of aromatic  and
derivatives In young female  Sprague-Dawley  rats.
U.S.  EPA.    1987.   Health  and  Environmental  Effects  Profile  for  3,3'-D1-
methylbenzldlne.  Prepared by  the Office  of  Health and Environmental Assess-
ment,  Environmental  Criteria and Assessment  Office. Cincinnati,  OH for  the
Office of Solid Waste and Emergency Response, Washington. DC.

1.1-D1methylhydraz1ne
Toth,  B.   1972.  Comparative  studies  with hydrazlne  derivatives.  Carclno-
genlclty  of  1,1-dlmethylhydrazlne,   unsymmetrlcal  (1,1-DMH)   In  the  blood
vessels,  lung,  kidneys  and  liver of  Swiss mice.   Proc. Am.  Assoc.  Cancer
Res.  13:34.

Toth,  B.   1973.    1,1-Dlmethylhydrazlne   (unsymmetrlcal)  carclnogenesls  In
mice.   Light microscopic  and  ultrastructural  studies  on  neoplastlc  blood
vessels.  J. Natl. Cancer Inst.  50(1):181-194.

U.S. EPA.   1984.  Health and  Environmental  Effects Profile for 1,1-Dlmethyl-
hydrazlne.   Prepared  by the  Office  of Health and  Environmental Assessment,
Environmental Criteria  and  Assessment  Office. Cincinnati. OH  for  the Office
of Solid Waste,  Washington.  DC.

1,2-Dlmethylhydrazlne
Toth.  B.  and  R.B.  Wilson.   1971.   Blood  vessel  tumorlgenes Is  by 1,2-dl-
methylhydrazlne dlhydrochlorlde (symmetrical).  Am. J.  Pathol.   64: 585.

U.S. EPA.   1984.  Health and  Environmental -Effects Profile for 1,2-Dlmethyl-
hydrazlne.   Prepared  by the  Office  of Health and  Environmental Assessment,
Environmental Criteria  and  Assessment  Office, Cincinnati. OH  for  the Office
of Solid Waste.  Washington,  DC.

Dimethyl sulfate
U.S.  EPA.    1985.   Health  and  Environmental  Effects  Profile  for  Dimethyl
sulfate.  Prepared  by  the  Office  of  Health  and  Environmental  Assessment,
Environmental Criteria  and  Assessment  Office, Cincinnati, OH  for  the Office
of Solid Waste,  Washington.  DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.
2.4-D1n1trotoluene
Ellis, H.V., S.H.  Hageusen,  J.R. Jodgson  et  al
of Munition  Compounds.   Phase III.  Effects of
2,4-Dlnltrotoluene.  NTIS AD-A077692.   281  p.
                    ,   1979.
                    Lifetime
Mammalian
Exposure.
Toxlclty
 Part  I.
U.S.  EPA.    1987.    Health  Effects  Assessment  for  2,4-  and  2,6-Dlnltro-
toluenes.  Prepared  by the  Office of  Health  and  Environmental  Assessment,
Environmental Criteria and  Assessment  Office,  Cincinnati, OH  for  the Office
of Emergency  and Remedial  Response, Washington,  DC.
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U.S.  EPA.  1990.   Carcinogen  Risk Assessment  Verification  Endeavor  (CRAVE)
Work  Group.   Verified,  pending concurrence  on  final  coversheet  and  Input
onto IRIS.

2.6-Dlnltrotoluene
U.S.  EPA.   1987.   Health  Effects   Assessment  for  2,4- and  2,6-D1n1tro-
toluenes.  Prepared  by  the  Office of  Health  and  Environmental  Assessment,
Environmental Criteria  and Assessment Office,  Cincinnati,  OH  for  the Office
of Emergency and Remedial Response, Washington. DC.

U.S.  EPA.  1990.   Carcinogen  Risk Assessment  Verification  Endeavor  (CRAVE)
Work  Group.   Verified,  pending concurrence  on  final  coversheet  and  Input
onto IRIS.

1,4-D1oxane
NCI   (National  Cancer   Institute).    1978.    Bloassay   of  1,4-dloxane  for
possible carclnogenldty.   NCI  Cardnogenesls  Tech. Rep.  Ser.  No.  80.   DHEW
Publication No.   (NIH) PB-285-711.

U.S.  EPA.   1990.   Integrated  Risk   Information  System  (IRIS).   Online.
Office  of  Health  and  Environmental   Assessment,  Environmental Criteria  and
Assessment Oflce, Cincinnati,  OH.

1.2-Dlphenylhvdrazlne
NCI  (National   Cancer   Institute).   1978.   Bloassay of   hydrazobenzene  for
possible carclnogenldty.   NCI  Cardnogenesls  Tech. Rep.  Ser.  No.  92.   DHEW
Publ. No. (NIH)  78-1342.

U.S.  EPA.  1980.   Ambient  Water Quality Criteria  Document for 1,2-D1phenyl-
hydrazlne.   Prepared  by the Office of Health  and  Environmental  Assessment,
Environmental Criteria  and Assessment Office,  Cincinnati,  OH  for  the Office
of Water Regulations and Standards, Washington,  DC.  EPA-440/5-80-062.   NTIS
PB 81-117731.

U.S.  EPA.   1987.   Health  Effects   Assessment  for  1,2-Dlphenylhydrazlne.
Prepared by  the Office  of  Health and  Environmental  Assessment. Environmental
Criteria and Assessment Office, Cincinnati, OH  for the Office of  Emergency
and Remedial  Response,  Washington,  DC.

U.S.  EPA.    1988.   Health   and  Environmental  Effects  Document for  1,2-DI-
phenylhydrazlne.  Prepared  by the Office of Health  and  Environmental  Assess-
ment, Environmental  Criteria  and Assessment Office, Cincinnati,  OH  for  the
Office of Solid  Waste and Emergency Response, Washington,  DC.

U.S.  EPA.    1990.   Integrated   Risk   Information  System  (IRIS).    Online.
Office  of  Health  and  Environmental  Assessment,  Environmental Criteria  and
Assessment Office, Cincinnati,  OH.

Direct Black  38
NCI (National Cancer Institute).  1978.  13-Week  subchronlc toxldty  studies
of direct blue  6, direct  black 38, and  direct brown 95 dyes.  NCI Cardno-
genesls. Tech.  Rep. Ser. No.  108.   p.  127.
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U.S.  EPA.   1987.   Health and Environmental Effects  Profile for Direct Black
38.    Prepared  by   the   Office   of  Health  and  Environmental  Assessment,
Environmental Criteria  and Assessment Office, Cincinnati,  OH  for  the Office
of Solid Waste and Emergency Response. Washington, DC.

Direct Blue 6'
NCI  (National Cancer  Institute).   1978.   13-Week subchronlc toxldty studies
of direct  blue  6, direct  black  38, and direct  brown  95  dyes.   NCI Carclno-
genesls. Tech. Rep. Ser. No. 108.  p. 127.

U.S.  EPA.   1987.   Health  and  Environmental  Effects Profile for  Direct Blue
6.    Prepared  by  the  Office  of   Health   and  Environmental  Assessment,
Environmental Criteria  and Assessment Office, Cincinnati,  OH  for  the Office
of Solid Waste and Emergency Response, Washington, DC.

Direct Brown 95
NCI  (National Cancer  Institute).   1978.   13-Week subchronlc toxldty studies
of direct  blue  6, direct  black  38, and direct  brown  95  dyes.   NCI Carclno-
genesls. Tech. Rep. Ser. No. 108.  p. 127.

U.S.  EPA.   1987.   Health and Environmental Effects  Profile for Direct Brown
95.    Prepared  by   the   Office   of  Health  and  Environmental  Assessment,
Environmental Criteria  and Assessment Office. Cincinnati.  OH  for  the Office
of Solid Waste and Emergency Response, Washington. DC.

Direct Sky Blue 6B
U.S.  EPA.   1987.   Health  and  Environmental  Effects  Profile for  Direct  Sky
Blue  68.   Prepared  by  the  Office  of  Health and  Environmental  Assessment,
Environmental Criteria  and Assessment Office, Cincinnati.  OH  for  the Office
of Solid Waste.  Washington. DC.

Eplchlorohydrln
Kom1sh1,  T.,  A.  Kawabata,  A.  Denda,   et al.   1980.   Forestomach  tumors
Induced by  orally administered eplchlorohydrln  In  male  Wlstar  rats.   Gann.
71: 922-923.

Laskln, S,  A.R. Sellakumar.  M.  Kuschner. et  al.  1980.   Inhalation carclno-
genlclty  of  eplchlorohydrln  In  nonlnbred  Sprague-Dawley  rats.   J.  Natl.
Cancer Inst.  65(4):  751-757.

U.S.   EPA.   1984.  Health  Assessment  Document  for Eplchlorohydrln.   Office of
Health and  Environmental  Assessment, Environmental  Criteria and  Assessment
Office, Research Triangle Park, NC.   EPA 600/8-83-032F.  NTIS PB85-132363.

U.S.   EPA.   1985.   Health  and  Environmental  Effects Profile  for  Eplchloro-
hydrln.   Prepared by  the  Office   of  Health  and Environmental  Assessment,
Environmental  Criteria and Assessment Office, Cincinnati,  OH  for  the Office
of Solid Waste.  Washington, DC.

U.S.   EPA.    1990.   Integrated  Risk Information  System  (IRIS).   Online.
Office of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati,  OH.
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Ethyl acrylate
NCI  (National  Toxicology Program).   1986.   Carclnogenesls  studies  of ethyl
acrylate In F344/N rats and B6C3F1 mice (gavage studies).

U.S.  EPA.   1987.   Health  and  Environmental  Effects  Profile  for  Ethyl
Acrylate.   Prepared  by  the  Office of  Health and  Environmental  Assessment,
Environmental Criteria  and  Assessment Office, Cincinnati,  OH  for  the Office
of Solid Waste and Emergency Response, Washington, DC.

Ethylene oxide
Shelllngs, W.M., C.S. Well and  R.R. Horonpot.   1981.   Final Report,  Ethylene
Oxide,  Two  Year   Inhalation  Study.   Submitted  to  the U.S.  Environmental
Protection Agency  by  Bushey  Run Research Center, Pittsburgh,  PA.   (CHed In
U.S. EPA, 1985)

U.S. EPA.   1985.   Health Assessment Document for Ethylene  Oxide.   Office of
Health  and  Environmental Assessment.  Environmental Criteria  and  Assessment
Office, Research Triangle Park, NC.  EPA 600/8-84-009F.  NTIS PB86-102597.

Ethylene thlourea
U.S.  EPA.    1984.   Health  and  Environmental  Effects  Profile for  Ethylene
Thlourea.   Prepared  by  the  Office of  Health and  Environmental  Assessment,
Environmental Criteria  and  Assessment Office, Cincinnati,  OH  for  the Office
of Solid Waste, Washington.  DC.

Folpet
Chevron  Chemical   Company.    1982.    Chevron  study:   Lifetime  oncogenlclty
feeding  study  of  pholton technical  (SX-946; folpet)  In CD-I  (ICR  derived)
mice.  Cited In U.S.  EPA. 1987.

U.S.  EPA.    1984.   Health  and  Environmental  Effects  Profile for  Folpet.
Prepared by  the Office  of Health and  Environmental  Assessment, Environmental
Criteria  and Assessment  Office,  Cincinnati,  OH  for  the  Office  of  Solid
Waste, Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk   Information  System  (IRIS).    Online.
Office  of  Health  and  Environmental  Assessment.  Environmental Criteria  and
Assessment Office, Cincinnati, OH.

Formaldehyde
U.S.  EPA.   1985.  Health  and  Environmental Effects  Profile  for  Formalde-
hyde.   Prepared  by   the Office of  Health  and  Environmental  Assessment,
Environmental Criteria  and  Assessment Office, Cincinnati,  OH  for  the Office
of Solid Waste, Washington.  DC.
U.S. EPA.   1988a.   Review Draft.
Carclnogenlclty of  Formaldehyde.
Addendum  to  Evaluation of  the Potential
U.S. EPA.   1988b.   Carcinogen  Assessment  Group (CAG) Profiles.   Prepared  by
the Carcinogen Assessment Group.   Available through RCRA/Superfund Docket.

U.S.  EPA.   1990.    Integrated  Risk  Information  System  (IRIS).    Online.
Office of  Health and  Environmental  Assessment,  Environmental Criteria  and
Assessment Office,  Cincinnati,  OH.
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Furozolldone
U.S.  DHEW.   1976a.   Furozolldone,  nlhydrazone,  furaltadone,  nltrofurazone.
Withdrawal  of  proposals  and  notice  of  proposed  rule  making.   Federal
Register 41: 34884-34921.

U.S.  DHEW.  1976b.  Furozolldone  (NF-180):  Notice of  Opportunity for hearing
on  proposal  to Withdraw  approval  of certain  new animal  drug  applications.
Federal Register.  41: 19907-19921.

U.S.  EPA.   1987.   Health  and  Environmental  Effects   Document  for  Nltro-
furans.   Prepared  by  the  Office of  Health  and Environmental  Assessment,
Environmental  Criteria and  Assessment Office. Cincinnati, OH for  the Office
of Solid Waste and Emergency Response, Washington, DC.

Furlurn
Cohen,  S.M.,  E.  Erturk  and  G.T.   Bryan.   1970.   Production of  leukemia  and
stomach  neoplasms  In  Swiss,  R.F.,  BALB/c and  C3H  female  mice  by  feeding
N-(4,5-n1tro-2-furyl-2-th1azolyl)acetam1de.  Cancer Res.  30(9): 2320-2325.

U.S.  EPA.   1987.   Health and  Environmental   Effects  Document   for  Selected
Nltrofurans.   Prepared by the Office  of  Health and Environmental Assessment,
Environmental  Criteria and  Assessment Office, Cincinnati. OH for  the Office
of Solid Waste and Emergency Response, Washington, DC.

Glyddaldehyde
U.S.  EPA.   1989.   Health  and  Environmental  Effects  Document for  Glycld-
aldehyde.   Prepared  by  the  Office of  Health and Environmental Assessment.
Environmental  Criteria and  Assessment Office, Cincinnati, OH for  the Office
of Solid Waste and Emergency Response, Washington, DC.

Heptachlor
Davis. K.   1965.   Pathology  report on mice fed  aldrln,  dleldrln,  heptachlor
and heptachlor epoxlde  for  two years.   Internal FDA memorandum to  Dr.  A.J.
Lehman. July 19.

Epstein.  S.S.   1976.   Carclnogenlclty  of  heptachlor  and chlordane.   Scl.
Total  Environ.  6:  103-154.

NCI (National  Cancer  Institute).   1977.   Bloassay of  Heptachlor for  Possible
Carclnogenlclty.   NCI Carclnogenesls  Tech.  Rep.  Ser. No.  9, DHEW No.  (NIH)
77-809.

Reuber,  M.D.   1977.   Hlstopathology  of carcinomas  of  the liver   In  mice
Ingesting heptachlor  or  heptachlor epoxlde.   Exp. Cell.  Blol.  45:  147-157.

U.S.  EPA.   1986.   Carclnogenlclty  Assessment of  Chlordane and Heptachlor/
Heptachlor  Epoxlde.   Prepared  by  the   Office  of  Health  and  Environmental
Assessment,  Carcinogen Assessment  Group,  Washington,  DC.  OHEA-C-204.

U.S. EPA.  1987.   Health Effects Assessment for  Heptachlor.   Prepared by  the
Office  of  Health and  Environmental  Assessment,  Environmental   Criteria  and
Assessment Office, Cincinnati,  OH for the  Office of Emergency  and  Remedial
Response, Washington,  DC.
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U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of Health  and  Environmental  Assessment,  Environmental  Criteria and
Assessment Office, Cincinnati, OH.

Heptachlor epoxlde
Davis,  K.J.   1965,  July  19.  Pathology report  on  mice fed aldrln, dleldrln,
heptachlor and heptachlor epoxlde  for  two  years.   Internal FDA memorandum to
Dr. A.J.  Lehman.

Velslcol  Chemical Corporation.  1973.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of Health  and  Environmental  Assessment,  Environmental  Criteria and
Assessment Office, Cincinnati, OH.

Hexachlorobenzene
Cabral,  J.R.P.,  P.  Shublk,  T. Mollner  et  al.  1977.   Carcinogenic activity
of hexachlorobenzene In hamsters.  Nature.   269: 510-511.

U.S.  EPA.  1984.   Health  Effects  Assessment  for Hexachlorobenzene.  Prepared
by the  Office  of  Health and Environmental  Assessment,  Environmental Criteria
and  Assessment  Office,   Cincinnati,  OH  for  the  Office  of  Emergency  and
Remedial  Response, Washington. DC.

U.S.  EPA.  1985.   Drinking Water  Criteria  Document  for Hexachlorobenzene.
Prepared  by the  Office of Health  and Environmental Assessment, Environmental
Criteria  and  Assessment   Office,  Cincinnati,  OH for  the Office  of Drinking
Water, Washington, DC.   Final Draft (on Public Comment).  EPA-600/X-84-179-1.
NTIS PB86-117777.

Hexachlorobutadlene
Kodba,  R.J.,  D.G.  Keyes,  6.C.  Jersey  et  al.  1977.   Results of a two-year
chronic  toxlclty  study  with  hexachlorobutadlene   In   rats.   Am.  Ind.  Hyg.
Assoc. J.  38: 589-602.

U.S.  EPA.  1980.   Ambient  Water  Quality  Criteria Document  for  Hexachloro-
butadlene.  Prepared by   the  Office  of  Health  and  Environmental  Assessment,
Environmental   Criteria and  Assessment Office, Cincinnati,  OH  for the Office
of Water  Regulations and  Standards,  Washington,  DC.  EPA-440/5-80-053.   NTIS
PB 81-117640.

U.S.  EPA.    1984.   Health  Effects  Assessment   for  Hexachlorobutadlene.
Prepared  by the Office of Health  and Environmental  Assessment, Environmental
Criteria  and  Assessment Office,  Cincinnati,   OH  for the  Office  of Emergency
and Remedial  Response.  Washington. DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of Health and  Environmental Assessment,  Environmental Criteria  and
Assessment Office, Cincinnati. OH.

Hexachlorocyclohexane-alpha
Ito, N.,  H.  Nagasaki.  M.  Aria,  et al.   1973.  Hlstologlcal  and  ultrastruc-
tural studies  on  the hepatocarclnogenlclty of benzene  hexachlorlde In  mice.
J. Natl. Cancer Inst.   51:817-826.
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U.S.  EPA.   1987.  Health  and  Environmental Effects  Profile  for Hexachloro-
cyclohexanes.   Prepared  by  the  Office of  Health and  Environmental  Assess-
ment,  Environmental  Criteria and  Assessment  Office, Cincinnati, OH  for the
Office of Solid Waste and Emergency Response. Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).    Online.
Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria and
Assessment Office, Cincinnati, OH.

Hexachlorocyclohexane-beta
Thorpe,  E.   and  A.I.T.  Walker.    1973.   Toxicology  of  deldrln (HEOD)  II.
Comparative  long-term oral  toxlclty  studies   In mice  with  dleldrln,  DDT,
phenobarbltone, beta-HCH and gamma-HCH.  Food Cosmet. Toxlcol.  11:  433-442.

U.S.  EPA.   1987.  Health  and  Environmental Effects  Profile  for Hexachloro-
cyclohexanes.   Prepared  by  the  Office of  Health and  Environmental  Assess-
ment,  Environmental  Criteria and  Assessment  Office, Cincinnati, OH  for the
Office of Solid Waste and Emergency Response, Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).    Online.
Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria and
Assessment Office, Cincinnati, OH.

Hexachlorocyclohexane-delta
Ito,  N.,  H.  Nagasaki, M.  Aral,  S.  Suglhara  and S.  Maklura.   1973.   Hlsto-
loglc  and  ultrastructural  studies  on the  hepatocarclnogenlclty of  benzene
hexachlorlde 1n mice.  J. Natl. Cancer Inst.  51(3): 817-826.

Ito,  N.,  H.  Nagasaki,  H.  Aoe,  et al.  1975.   Brief communication:  Develop-
ment  of  hepatocellular   carcinomas  In   rats   treated  with  benzene  hexa-
chlorlde.  J. Natl. Cancer Inst.   54: 801-805.

Nagasaki. H.,  S.  Tomll,  T. Mega.  M.  Marugaml and  N.   Ito.   1972.   Hepato-
carclnogenlc  effect  of   a-,  B-,  Y-.  4-lsomers  of  benzene  hexachlorlde
In mice.  Gann.  63(3): 393.

U.S.  EPA.   1987.  Health  and  Environmental Effects  Profile  for Hexachloro-
cyclohexanes.  Prepared  by  the  Office of  Health and  Environmental  Assess-
ment.  Environmental  Criteria and  Assessment Office, Cincinnati, OH  for the
Office of Solid Waste and Emergency Response,  Washington, DC.

U.S.  EPA.    1990.   Integrated  Risk  Information  System  (IRIS).    Online.
Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati,  OH.

Hexachlorocyclohexane.  gamma (Llndane)
Thorpe, E.  and A.I.T. Walker.  1973.   The  toxicology of dleldrln (HEOD). II.
Comparative   long-term  oral  toxlclty  studies   In  mice  with  dleldrln,  DDT,
phenobarbltone, beta-BHC  and gamma-BHC. Food  Cosmet. Toxlcol.  11:  433-442.

U.S.  EPA.   1984.   Health  Effects  Assessment  for  Llndane.   Prepared by the
Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment  Office, Cincinnati,  OH for the  Office of Emergency  and  Remedial
Response, Washington, DC.
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 U.S.  EPA.   1986.   Health and Environmental  Effects Profile  for  Hexachloro-
 cyclohexanes.   Prepared  by  the  Office  of Health  and Environmental  Assess-
 ment,  Environmental Criteria  and Assessment Office.  Cincinnati,  OH  for  the
 Office  of Solid Waste  and Emergency  Response, Washington,  DC.

 U.S.  EPA.    1990.   Integrated   Risk  Information   System  (IRIS).    Online.
 Office  of  Health  and   Environmental  Assessment, Environmental  Criteria  and
 Assessment  Office,  Cincinnati, OH.

 Hexachlorocvclohexane-epsllon
 Goto,  M., M. Hattorl,  T. Mlyagawa and  M.  Enomoto.  1972.  Ecological  chem-
 istry.  II.  Hepatoma formation In mice after  administration of high doses  of
 hexachlorocyclohexane  Isomers.  Chemosphere.  1:  279-282.

 U.S.  EPA.   1987.   Health and Environmental  Effects Profile  for  Hexachloro-
 cyclohexanes.   Prepared  by  the   Office  of Health  and Environmental  Assess-
 ment,  Environmental Criteria  and Assessment Office,  Cincinnati,  OH  for  the
 Office  of Solid Waste  and Emergency Response, Washington,  DC.

 U.S.  EPA.    1990.   Integrated   Risk  Information   System  (IRIS).    Online.
 Office  of  Health  and   Environmental  Assessment, Environmental  Criteria and
 Assessment  Office,  Cincinnati, OH.

 Hexachlorocvclohexane-technlcal
 MonH,  K.M., C.S.  Soman and  V. Samatl.  1983.   Hexachlorocyclohexane-lnduced
 tumorlgenldty  In  mice under  different  experimental conditions.  Tumorlgen-
 Iclty.  69:  383-386.

 U.S.  EPA.   1987.    Health and Environmental Effects  Profile for  Hexachloro-
 cyclohexane.  Prepared by the  Office  of  Health  and  Environmental  Assessment,
 Environmental Criteria and Assessment Office, Cincinnati,  OH  for  the Office
 of Solid  Waste and  Emergency Response, Washington,  DC.

 U.S.  EPA.   1990.   Integrated  Risk  Information   System   (IRIS).    Online.
 Office  of Health  and   Environmental  Assessment, Environmental  Criteria and
 Assessment Office,  Cincinnati, OH.

 Hexachloroethane
 NCI  (National  Cancer  Institute).   1978.   Bloassay of  Hexachloroethane for
 Possible  Carclnogenlclty.   NCI Cardnogenesls Tech. Rep.  Ser. No.  68,  DHEW
 No. (NIH) 78-1318.

 U.S.  EPA.   1980.    Ambient Water  Quality  Criteria   Document  for  Chlorinated
 Ethanes.   Prepared  by  the Office  of Health  and  Environmental  Assessment,
 Environmental Criteria  and Assessment Office, Cincinnati, OH  for  the  Office
 of Water  Regulations and  Standards,  Washington,  DC.  EPA-440/5-80-029.  NTIS
 PB 81-117400.                                                       ,

 U.S. EPA.   1987.   Health  Effects  Assessment  for Hexachloroethane.  Prepared
 by the Office of Health and Environmental  Assessment,  Environmental  Criteria
and  Assessment  Office,  Cincinnati,  OH  for  the  Office  of  Emergency  and
Remedial Response.  Washington,  DC.
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U.S. EPA.   1989.   Health and Environmental Effects  Document  for Hexachloro-
ethane.   Prepared by  the  Office of  Health  and Environmental  Assessment,
Environmental Criteria and  Assessment  Office, Cincinnati,  OH  for  the Office
of Solid Waste and Emergency Response,  Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati. OH.

Hydrazlne/Hydrazlne sulfate
B1anc1f1or1,  C.   1970.   Hepatomas  In  CBA/Cb/Se  mice and  liver  lesions  In
golden  hamsters  Induced  by  hydrazlne  sulfate.   J.  Natl.  Cancer  Inst.   44:
943.

MacEwen,  J.D.,   E.H.   Vernot,  C.C.  Haun,   E.R.   Klnkead  and  A.  Hall.  III.
1981.   Chronic   Inhalation  Toxlclty  of  Hydrazlne:  Oncogenlc   Effects.   Air
Force  Aerospace  Medical  Research  Laboratory,   Wright-Patterson  Air  Force
Base, OH.  NTIS

U.S. EPA.  1984.  Health and  Environmental  Effects  Profile  for Hydrazlne and
Hydrazlne  Sulfate.   Prepared by  the  Office  of Health  and  Environmental
Assessment, Environmental Criteria and Assessment Office, Cincinnati, OH for
the Office of Solid Waste and Emergency Response,  Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of  Health and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

Indenod ,2.3-c.d)pyrene
U.S. EPA.   1990.   Carcinogen  Risk Assessment Verification Endeavor  (CRAVE)
Work Group.   Verified,  pending  concurrence  on  final  coversheet and  Input
onto IRIS.

Isophorone
NTP  (National Toxicology  Program).    1986.   Toxicology  and  carclnogenesls
studies  of  Isophorone  (CAS  No.  78-59-1)  In  F344/N rats  and B6C3F1  mice
(gavage studies).  NTP  Tech. Rep.  Ser.  No.  291, DHHS (NIH) 86-2547.

U.S. EPA.   1986.   Health and  Environmental Effects  Profile for  Isophorone.
Prepared by the Office of Health  and Environmental  Assessment, Environmental
Criteria and Assessment Office, Cincinnati, OH  for  the  Office  of Solid Waste
and Emergency Response, Washington, DC.

U.S. EPA.  1987.  Health Effects Assessment for Isophorone. Prepared by the
Office  of  Health and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH for  the  Office of Emergency  and  Remedial
Response, Washington,  DC.

U.S. EPA.   1989.   Carcinogen  Risk Assessment Verification Endeavor  (CRAVE)
Work Group.   Verified,  pending  concurrence  on  final  coversheet and  Input
onto IRIS.
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Lead
U.S.  EPA.   1984.   Health  Effects  Assessment  for  Lead.   Prepared  by  the
Office  of Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office,  Cincinnati,  OH for  the  Office of  Emergency  and Remedial
Response, Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office. Cincinnati. OH.

Methoxychlor
U.S.  EPA.   1987.   Health  and  Environmental  Effects  Profile  for  Methoxy-
chlor.   Prepared  by  the  Office  of  Health and Environmental  Assessment,
Environmental Criteria  and  Assessment Office, Cincinnati,  OH  for  the Office
of Solid Waste, Washington,  DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

2-Methoxy-5-nltroanllIne
NCI  (National Cancer Institute).   1978.   Bloassay of 5-nltro-o-anlsldlne for
possible  carclnogenlclty.    NCI   Carclnogenesls   Tech.   Rep.   Ser.  No.  127.
123 p.

U.S.  EPA.   1987.   Health and Environmental  Effects  Profile for  2-Methoxy-5-
nltroanlllne.   Prepared  by   the  Office of  Health and  Environmental  Assess-
ment, Environmental  Criteria and  Assessment  Office, Cincinnati,  OH  for  the
Office of Solid Waste and Emergency Response, Washington, DC.

2-Hethylanlllne
Hecht.  S.S.,  A. El-Boyoumy.  A.  Rlvenson and E.  Flala.   1982.   Comparative
carclnogenlclty  of o-toluldlne  hydrochlorlde  and  o-nltrotoluene  In  F-344
rats.  Cancer Lett.  16(1):  103-108.

U.S.  EPA.  1987.   Health  and  Environmental Effects  Profile for  2-Methyl-
anlllne and 2-Methylanlllne  Hydrochlorlde.   Prepared  by the Office of Health
and  Environmental  Assessment,  Environmental Criteria  and  Assessment Office,
Cincinnati,  OH  for  the Office   of  Solid  Waste  and  Emergency  Response,
Washington, DC.

2-Methylan1l1ne hydrochlorlde
Hecht,  S.S.,  A. El-Boyoumy,  A.  Rlvenson and E.  Flala.   1982.   Comparative
carclnogenlclty  of o-toluldlne  hydrochlorlde  and  o-nltrotoluene  In  F-344
rats.  Cancer Lett.  16(1):  103-108.

U.S.  EPA.   1987.   Health  and  Environmental Effects  Profile for  2-Methyl-
anlllne and 2-Methylan1l1ne Hydrochlorlde.   Prepared  by the Office of Health
and  Environmental  Assessment,  Environmental Criteria  and  Assessment Office,
Cincinnati,  OH   for  the Office   of  Solid  Waste  and  Emergency  Response,
Washington, DC.
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4.4-Hethy1eneb1s benzelamlne
NTP   (National   Toxicology   Program).   1983.    Carclnogenesls   studies  of
4,4-methylened1an1l1ne  dlhydrochlorlde  In   F344/N  rats  and  B6C3F1  mice
(drinking water studies).  NTP-81-143 NIH Publ. No. 83-2504.  NTP-TR-248.

U.S.  EPA.   1984.   Health  and  Environmental  Effects  Profile  for  Benzel-
amlne, 4,4-Methylenebls.  Prepared by  the  Office  of Health and Environmental
Assessment. Environmental Criteria and  Assessment Office, Cincinnati. OH for
the Office of Solid Waste, Washington, DC.

4.4'-Methylene-b1s(N.N'-dimethyl)an111ne
NCI  (National  Cancer  Institute).   1979.   Bloassay of 4,4'-methyleneb1s(N,N-
d1methyl)benzenam1ne  for  possible  carclnogenlclty.   NCI  Carcinogen.  Tech.
Rep. Ser. No. 186.  CAS 101-61-1.   NCI-CG-TR-186.

U.S.  EPA.   1985.  Health and  Environmental  Effects  Profile  for  4,4'-Methy-
lene-b1s(N.N'-d1methyl)an111ne.   Prepared  by  the  Office  of   Health  and
Environmental  Assessment,  Environmental  Criteria  and  Assessment  Office,
Cincinnati,  OH  for   the  Office  of  Solid  Waste  and   Emergency  Response,
Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office of Health  and  Environmental   Assessment,  Environmental Criteria and
Assessment Office, Cincinnati,  OH.

Methylene chloride
NCA  (National  Coffee  Association).   1983.   Twenty-four  month  oncogenlclty
study  of methylene  chloride   In  mice.  Prepared by  Hazelton  Laboratories,
America Inc., Vienna,  VA.   Unpublished.

NTP  (National  Toxicology  Program).    1986.    Toxicology  and  carclnogenesis
studies  of  dlchloromethane  (methylene chloride)  (CAS  No.  75-09-2)  In F344/N
rats  and B6C3F1  mice  (Inhalation studies).   NTP  Tech.  Rep.  Ser.  No.  306,
DHHS (NIH) 86-2562.

U.S.  EPA.   1984.    Health  Effects  Assessment  for  Methylene   Chloride.
Prepared by the  Office of Health  and  Environmental Assessment, Environmental
Criteria and Assessment  Office, Cincinnati, OH  for the  Office of  Emergency
and Remedial Response,  Washington, DC.

U.S. EPA.   1985.   Addendum  to  the Health  Assessment  Document for  Dlchloro-
methane  (methylene chloride).   Updated  Carclnogenlclty Assessment.   Prepared
by  the  Carcinogen  Assessment  Group,  Office  of  Health  and  Environmental
Assessment, Washington, DC.   EPA 600/8-82-004FF.  NTIS PB 86-123742.

U.S.  EPA.   1990.    Integrated  Risk  Information  System  (IRIS).    Online.
Office of  Health and  Environmental  Assessment,  Environmental Criteria and
Assessment Office.  Cincinnati.  OH.

Methyl Ethyl Ketone
U.S. EPA.   1985.   Health  and  Environmental Effects Profile for Methyl  Ethyl
Ketone.   Prepared  by  the  Office of  Health  and  Environmental  Assessment,
Environmental  Criteria and  Assessment  Office,  Cincinnati,  OH  for  the Office
of Solid Waste  and Emergency Response, Washington, DC.
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 U.S.   EPA.   1988.   Updated  Health  Effects  Assessment   for  Methyl  Ethyl
 Ketone.   Prepared  by   the  Office  of  Health  and  Environmental  Assessment,
 Environmental  Criteria  and Assessment  Office, Cincinnati,  OH for the Office
 of  Solid Waste and  Emergency Response,  Washington, DC.

 Methylhydrazlne
 Toth,  B.  and  H.  Shlmlzu.  1973.   Methyl  hydrazlne  tumorlgenesls  In Syrian
 golden  hamsters  and the morphology of  malignant  hlstlocytomas.  Cancer Res.
 33: 2744.

 U.S.  EPA.   1984.   Health and Environmental  Effects  Profile for Methylhydra-
 zlne.   Prepared  by  the  Office  of  Health  and  Environmental  Assessment,
 Environmental  Criteria  and Assessment  Office, Cincinnati,  OH for the Office
 of  Solid Waste. Washington. DC.

 2-Methyl-5-nUroan111ne
 NCI  (National  Cancer  Institute).   1978.  Bloassay of 5-nltro-o-toluldlne for
 possible carclnogenlclty.  NCI Carcinogen. Tech. Rep. Ser.  No. 107.  102 p.

 U.S.  EPA.   1987.    Health  and  Environmental Effects  Profile for  2-Methyl-5-
 nltroanlllne.   Prepared by  the  Office  of  Health and  Environmental  Assess-
 ment,  Environmental  Criteria and  Assessment Office. Cincinnati,  OH  for  the
 Office of Solid Waste and Emergency Response, Washington, DC.

 Mlrex
 NTP  (National   Toxicology Program).    1987.   NTP  Technical  Report  on  the
 Toxicology and Carclnogenesls Studies of Mlrex (CAS  No. 2385-85-5) In F344/N
 Rats.  NTP TR 313 (March, 1987 draft), NIH Publ. No. 87-2569.

 U.S.  EPA.   1987.   Health Effects  Assessment  for  Mlrex.   Prepared  by  the
 Office  of  Health and  Environmental  Assessment,  Environmental Criteria  and
 Assessment Office,  Cincinnati,  OH for  the  Office of Emergency  and  Remedial
 Response. Washington. DC.

 Niagara Blue 48
 U.S. EPA.  1987.  Health and Environmental   Effects  Profile for  Niagara Blue
 48.   Prepared  by   the   Office   of   Health  and   Environmental  Assessment,
 Environmental Criteria  and  Assessment Office, Cincinnati.  OH  for  the Office
 of Solid Waste and Emergency Response, Washington, DC.

 Nickel
 Chovll, A., R.B. Sutherland and M.  Halllday.  1981.   Respiratory  cancer In a
 cohort of sinter plant  workers.   Br. J.  Ind. Med.   38: 327-333.

 Enterllne,  P.E. and  G.M.  Marsh.   1982.   Mortality among  workers  In  a nickel
 refinery and  alloy  manufacturing  plant In  West  Virginia.  J.  Nat.  Cancer
 Inst.  68:  925-933.

Magnus, K.,  A. Andersen and  A.   Hogetvelt.  1982.  Cancer of  respiratory
organs among workers  at  a  nickel  refinery  1n  Norway.   Int. 0.  Cancer.  30:
681-685.
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Peto, J., H. Cuckle, R. Doll, et  al.   1984.   Respiratory cancer mortality of
Welsh  nickel  refinery  workers.    In:  Nickel  1n  the  Human  Environment:
Proceedings  of  a Joint Symposium,  March, 1983.   IARC Scientific  Publ.  No.
53.  IARC, Lyon, France,  p. 36-46.

U.S.  EPA.   1984.   Health  Effects Assessment  for Nickel.   Prepared  by  the
Office  of  Health and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office,  Cincinnati,  OH for  the  Office of  Emergency  and Remedial
Response, Washington, DC.

U.S.  EPA.   1986.    Health  Assessment  Document   for   Nickel   and  Nickel
Compounds.   Office   of  Health  and  Environmental  Assessment.  Environmental
Criteria and Assessment Office,  Research Triangle  Park,  NC.   EPA-600/8-83-
012F. NTIS PB 86-232212.

U.S.  EPA.   1990.   Integrated   Risk   Information  System  (IRIS).   Online.
Office  of  Health and  Environmental  Assessment.  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

Nltrofurazone
Erturk,   E.,  J.E.  Morris,  S.M.   Cohen,  et  al.    1970.   Transplantable  rat
mammary  tumors  Induced  by 5-n1tro-2-furaldehyde  semlcarbazone  and by formic
acid  2-[4-(5-n1tro-2-furyl)-2-th1azolyl]hydraz1de.    Cancer   Res.    30(5):
1409-1412.

U.S.  EPA.   1987.   Health and  Environmental  Effects  Document  for  Selected
Nltrofurans.   Prepared by the Office of  Health and Environmental Assessment,
Environmental Criteria  and  Assessment  Office,  Cincinnati, OH  for  the Office
of Solid Waste  and Emergency Response.  Washington. DC.

2-N1tropropane
Lewis,  T.R., C.E.   Ulrlch  and  W.M.   Busey.  1979.   Subchronlc  Inhalation
toxlclty of  nltromethane  and 2-nltropropane.   J. Environ.  Pathol.  Toxlcol.
2(5)-.233-249.

U.S.  EPA.   1985.  Health and Environmental  Effects Profile  for 2-NHropro-
pane.   Prepared  by  the  Office  of   Health  and  Environmental  Assessment,
Environmental Criteria  and  Assessment  Office,  Cincinnati, OH  for  the Office
of Solid Waste  and Emergency Response,  Washington, DC.

U.S.  EPA.   1986.  Carcinogen Assessment  Group (CAG)  Profiles.   Prepared by
the Carcinogen  Assessment  Group.   Available through RCRA/Superfund Docket.

N-Nltrosodl-n-butylamlne
Bertram, J.S. and A.W. Craig.   1970.   Induction  of bladder  tumors  In  mice
with d1butyln1trosam1nes.   Br. J.  Cancer.   24:  352-359.

U.S.  EPA.    1986.    Health  and  Environmental   Effects  Profile  for  Nltros-
amlnes.    Prepared by  the  Office of  Health  and Environmental  Assessment,
Environmental Criteria  and  Assessment  Office,  Cincinnati, OH  for  the Office
of Solid Waste  and Emergency Response,  Washington, DC.

U.S.  EPA.    1990.   Integrated   Risk   Information  System  (IRIS).   Online.
Office  of  Health and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.


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N-Nltrosodlethanolamlne
LlJInsky, Wt  and  R.M>  Kovatch.   1985.  Induction of  liver  tumors  In rats by
nUrosodlethanolamlne at low doses.  Carclnogenesls.  6: 1679-1681

U.S.  EPA.   1986.    Health  and  Environmental  Effects   Profile  for  Nltros-
amlnes.   Prepared  by  the  Office of  Health  and  Environmental  Assessment,
Environmental  Criteria  and  Assessment Office, Cincinnati,  OH  for  the Office
of Solid Waste and Emergency Response, Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of Health  and  Environmental   Assessment,  Environmental Criteria  and
Assessment Office, Cincinnati, OH.

N-Nltrosodlethylamlne
Peto,  R.,  R.  Gray,  P.  Brantom and  P.  Grasso.   1984.   NHrosamlne  carclno-
genesls  In  5120 rodents: Chronic  administration of  16  different  concentra-
tions  of  NDEA, NONA. NPYR  and  NPIP  In the  water of 4440  Inbred  rats,  with
parallel  studies on  NDEA alone  of the effect of  age  of  starting  (3,  6 or 20
weeks)  and  of species  (rats, mice or  hamsters).   IARC   Scl.  Publ.   57:
627-665.

U.S.  EPA.   1986.    Health  and  Environmental  Effects   Profile  for  NHros-
amlnes.   Prepared   by  the  Office of  Health  and  Environmental  Assessment,
Environmental  Criteria  and  Assessment Office, Cincinnati,  OH  for  the Office
of Solid Waste and Emergency Response, Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of Health  and  Environmental  Assessment,  Environmental Criteria  and
Assessment Office, Cincinnati, OH.

N-Nltrosodlmethylamlne
Peto.  R.,  R.  Gray,  P.  Brantom and  P.  Grasso.   1984.   NHrosamlne  carclno-
genesls  In  5120 rodents: Chronic  administration of  16  different  concentra-
tions  of  NDEA, NDMA. NPYR  and  NPIP  1n the  water of 4440  Inbred  rats,  with
parallel  studies on  NDEA alone  of the effect of  age  of  starting (3,  6 or 20
weeks)  and  of species  (rats,  mice or  hamsters).   IARC   Scl.  Publ.   57:
627-665.

U.S.  EPA.   1986.    Health  and  Environmental  Effects   Profile  for  Nltros-
amlnes.   Prepared  by  the  Office of  Health  and  Environmental  Assessment,
Environmental  Criteria and  Assessment  Office, Cincinnati,  OH  for  the Office
of Solid Waste and Emergency Response, Washington, DC.

U.S.  EPA.   1990.    Integrated   Risk  Information  System  (IRIS).    Online.
Office  of  Health   and  Environmental  Assessment,  Environmental Criteria  and
Assessment Office,  Cincinnati, OH.

N-Nltrosodlphenylamlne
NCI  (National  Cancer  Institute).   1979.   Bloassay  of N-nHrosodlphenylamlne
(CAS  No.  86-30-6)   for  possible carclnogenlclty.   NCI   Carclnogenesls  Tech.
Rep. Ser. No. 164,  NIH 79-1720.   NTIS PB298-275.
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Peto,  R.,  R.  Gray, P.  Brantom and P. Grasso.   1984.   Nltrosoamlne carclno-
genesls  In 5120 rodents:  Chronic  administration of 16  different concentra-
tions  of  NDEA,  NDMA.  NPYR  and NPIP in  the  water of  4440  Inbred rats, with
parallel  studies on NDEA alone of  the effect  of age of starting  3,  6 or 20
weeks)  and of species  (rats,  mice or  hamsters).  IARC  Scl.  Publ.  57: 627-
665.

U.S.  EPA.   1980.   Ambient Water Quality Criteria Document  for NHrosamlnes.
Prepared  by the Office  of Health  and  Environmental Assessment, Environmental
Criteria  and  Assessment  Office,  Cincinnati,   OH for  the  Office of  Water
Regulations  and  Standards,  Washington.  DC.    EPA-440/5-80-064.   NTIS  PB
81-117756.

U.S.  EPA.  1986a.   Health  and  Environmental   Effects  Profile  for  NHros-
amlnes.   Prepared  by   the  Office  of  Health  and Environmental  Assessment,
Environmental  Criteria  and Assessment  Office,  Cincinnati.  OH  for  the Office
of Solid Waste and Emergency Response,  Washington, DC.

U.S.  EPA.   1986b.   Integrated  Risk Information  System  (IRIS).  Carclnogen-
Iclty  Assessment  for  Lifetime Exposure  to  N-NHrosodlmethylamlne.   Online.
(Verification  date  10/29/86.)  Office  of  Health and Environmental  Assess-
ment, Environmental Criteria and Assessment Office, Cincinnati, OH.

U.S.  EPA.   1987.   Health  Effects Assessment   for  N-NHrosodlphenylamlne.
Prepared  by the Office  of Health  and  Environmental Assessment, Environmental
Criteria  and  Assessment Office, Cincinnati, OH  for  the Office of Emergency
and Remedial Response. Washington, DC.

U.S.  EPA.   1990.    Integrated  Risk   Information  System  (IRIS).   Online.
Office  of Health and  Environmental Assessment.  Environmental  Criteria  and
Assessment Office,  Cincinnati, OH.

N-Nltrosodl-n-propylamlne
Druckrey,  H.    1967.    Quantitative  aspects  In  chemical   carcinogens.   In:
Potential  Carcinogenic   Hazards  from  Drugs.    UICC  Monograph,  Series  7.
Sprlnger-Verlag, Berlin,  p. 60-78.

Druckrey,  H.,  R.  Puressman,  S. Ivankovlc  and  D.  Schmahl.   1967.   Organo-
troplc  carcinogenic effect  of 65  different  N-n1troso  compounds on BD rats.
Z. Krebsforsch.   69:  103-201.

U.S.  EPA.  1986.   Health  and  Environmental   Effects  Profile for  Nltros-
amlnes.   Prepared  by  the  Office   of  Health  and Environmental  Assessment,
Environmental  Criteria  and  Assessment  Office,  Cincinnati,  OH  for  the Office
of Solid Waste and  Emergency Response,  Washington, DC.

U.S.  EPA.   1990.    Integrated  Risk   Information  System  (IRIS).   Online.
Office  of  Health  and  Environmental Assessment,  Environmental Criteria  and
Assessment Office,  Cincinnati, OH.

N-N1trosomethy1ethylam1ne
Druckrey,  H.  1967.   Quantitative  aspects  In  chemical  carclnogenesls.   In:
Potential  Carcinogenic   Hazards  from  Drugs.    UICC  Monograph,   Series  7.
Sprlnger-Verlag, Berlin,  p. 60-78.
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Druckrey, H.,  R.  Puressman,  S.  Ivankovlc  and D.  Schmahl.  1967.   Organo-
troplc carcinogenic effect  of 65 different  N-nHroso  compounds on  BO  rats.
Z. Krebsforsch.  69:  103-201.

U.S.  EPA.    1986.   Health  and  Environmental   Effects   Profile  for  Nltros-
amlnes.   Prepared  by  the  Office  of  Health  and  Environmental  Assessment,
Environmental Criteria and  Assessment  Office,  Cincinnati,  OH for  the Office
of Solid Waste and  Emergency Response,  Washington,  DC.

U.S.  EPA.   1990.    Integrated  Risk  Information   System  (IRIS).   Online.
Office of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office,  Cincinnati, OH.

N-N1trosomethylv1nylam1ne
U.S.  EPA.    1986.   Health  and  Environmental   Effects   Profile  for  Nltros-
amlnes.   Prepared  by  the  Office  of  Health  and  Environmental  Assessment.
Environmental Criteria and  Assessment  Office,  Cincinnati,  OH for  the Office
of Solid Waste and  Emergency Response.  Washington,  DC.
N-Nltrosopyrroll dine
Preussmann,  R.,  D.  Schmahl  and  G.
N-n1trosopyrroll dine:  Dose-response
161-166.
  Elsenbrand.   1977.
  study  In rats.   Z.
Carclnogenlclty of
 Krebsforsch.   90:
U.S.  EPA.   1990.    Integrated  Risk  Information  System  (IRIS).    Online.
Office of  Health and  Environmental  Assessment,  Environmental Criteria  and
Assessment Office,  Cincinnati,  OH.

Parathlon
U.S. EPA.  1987.  Health  Effects  Assessment for Parathlon.   Prepared  by  the
Office of  Health and  Environmental  Assessment,  Environmental Criteria  and
Assessment Office. Cincinnati,  OH  for the  Office  of Emergency and  Remedial
Response, Washington, DC.

U.S.  EPA.   1990.    Integrated  Risk  Information  System  (IRIS).    Online.
Office of  Health and  Environmental  Assessment,  Environmental Criteria  and
Assessment Office.  Cincinnati,  OH.

1.2.3.4.5-Pentabromo-6-ch1orocyclohexane
Blair, E.H.   1981.   TSCA sec  8(e)  submission 8EHg-0381-0393;  88-8100295  by
Dow Chemical  Co.  Office of  Toxic  Substances,  U.S.  EPA,  Washington,  DC.

U.S.  EPA.   1985.  Health  and  Environmental  Effects Profile  for  1.2,3,4,5-
Pentabromo-6-chlorocyclohexane.   Prepared  by   the   Office   of  Health  and
Environmental  Assessment.  Environmental   Criteria  and  Assessment   Office.
Cincinnati.  OH  for   the  Office  of  Solid  Waste  and  Emergency  Response,
Washington. DC.

Pentachloronltrobenzene
Innes, J.R.H.,  B.M.  Ulland,  M.G.  Valeria, et al.  1969.   Bloassay  of  pesti-
cides  and  Industrial  chemicals  for  tumorIgenlclty   In  mice:  A  preliminary
note.  J. Natl. Cancer Inst.  41:  1101-1114.
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U.S.  EPA.   1986.   Health and Environmental Effects  Profile for Pentachloro-
nltrobenzene.   Prepared  by  the  Office of  Health and  Environmental  Assess-
ment,  Environmental  Criteria and  Assessment  Office. Cincinnati,  OH  for  the
Office of Solid Waste and Emergency Response,  Washington, DC.

o-Phenylened1am1ne
U.S.  EPA.   1985.   Health and Environmental Effects  Profile for o-Phenylene-
dlamlne.   Prepared by  the  Office  of Health  and Environmental  Assessment,
Environmental Criteria and Assessment Office, Cincinnati,  OH  for  the Office
of Solid Waste and Emergency Response, Washington. DC.

Welsburger, E.K., A.B. Russfleld and  F. Homburger, et al.  1978.  Testing of
twenty-one  environmental  aromatic   amines   of   derivatives  for  long-term
toxldty or carclnogenldty.  J.  Environ.  Pathol. Toxlcol.  2(2): 325-256.
2-Phenylphenol
Hlraga K.  and T.
1n  F344   rats  by
Cosmet. Toxlcol.
FuJII.  1981.   Induction  of tumours of  the  urinary system
 dietary administration  of  sodium o-phenylphenate.   Food
19(3): 303-310.
U.S.  EPA.   1984.   Health and  Environmental Effects  Profile  for  2-Phenyl-
phenol.   Prepared  by  the  Office of  Health and Environmental  Assessment,
Environmental Criteria and  Assessment  Office, Cincinnati.  OH  for  the Office
of Solid Waste. Washington.  DC.

Polybromlnated blphenyls  (PBBs)
NTP  (National  Toxicology Program).  1983.   Cardnogenesls  studies  of  poly-
bromlnated blphenyl mixture In F344/N rats and  B6C3F1  mice (gavage studies).
Flremaster FF-1.  Case No. 67774-32-7.   NTP,  Research Triangle Park, NC.

U.S.  EPA.   1989.   Health and  Environmental  Effects Document  for  Polybroml-
nated Blphenyls (PBBs).   Prepared by the Office  of  Health and Environmental
Assessment, Environmental Criteria and Assessment Office,  Cincinnati, OH for
the Office of Solid Waste and  Emergency  Response, Washington, DC.
Polychlorlnated blphenyls (PCBs)
Nor back, D.H.  and R.H.  Weltman.
of  hepatocellular carcinoma  In
Perspect.  60: 97-105.
                 1985.   Polychlorlnated  blphenyl  Induction
                the  Sprague-Dawley rat.   Environ.  Health
U.S.  EPA.   1984.   Health  Effects  Assessment  for  PCBs.   Prepared  by  the
Office  of  Health and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati,  OH for the  Office  of Emergency  and  Remedial
Response, Washington,  DC.

U.S.  EPA.    1987.   Drinking  Water  Criteria  Document   for  Polychlorlnated
Blphenyls  (PCBs).   Prepared  by  the  Office  of  Health  and  Environmental
Assessment, Environmental  Criteria and Assessment  Office, Cincinnati,  OH for
the Office of Drinking Water.  Washington,  DC.   Final  Document.

U.S.  EPA.    1990.    Integrated   Risk   Information   System  (IRIS).   Online.
Office  of  Health and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office,  Cincinnati, OH.
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Propylene oxide
Dunkelberg,  H.   1982.   Carclnogenlclty  of  ethylene oxide  and 1,2-propylene
oxide upon Intragastrlc administration to rats.  Br. J. Cancer.  46: 924-933.

NTP  (National  Toxicology  Program).   1985.    Toxicology  and  cardnogenesls
studies of propylene oxide (CAS No.  75-56-9).  In F344/N rats and B6C3F1 mice
(Inhalation  studies).  NTP Tech.  Rep.  Ser.  No.  267.   NTP,  Research Triangle
Park. NC.  NIH Pub. No. 85-2527.

Renne, R.A.,  W.E.  Glddens,  G.A.   Boorman, R.  Kovatch,  J.E.  Haseman and W.O.
Clarke.   1986.   Nasal  cavity  neoplasla 1n  F344/N rats  and (C57BL/6XC3H)F1
mice  Inhaling propylene  oxide for  up to two  years.   J.  Natl.  Cancer  Inst.
77: 573-582.

U.S.  EPA.    1985.   Health  and  Environmental   Effects  Profile  for  Propylene
Oxide.   Prepared  by   the  Office  of  Health   and   Environmental  Assessment,
Environmental Criteria and Assessment  Office.  Cincinnati,  OH  for  the Office
of Solid Waste and Emergency  Response,  Washington,  DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office of  Health  and  Environmental Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati,  OH.

Qulnollne
Hlrao, K.,  Y. Shlnohara.  H.  Tsuda,  et al.   1976.  Carcinogenic  activity of
qulnlolne on rat liver.  Cancer Res.  36: 329-335.

U.S.  EPA.   1985.   Health  and  Environmental Effects  Profile  for  Qulnollne.
Prepared by  the  Office of Health  and Environmental Assessment, Environmental
Criteria and Assessment Office, Cincinnati,  OH  for the Office of Solid Waste
and Emergency Response. Washington,  DC.

RDX (CvclonUe)
L1sh,  P.M.,  B.S.  Levlne,  E.M.  Fured!,  E.M.  Sagartz   and  V.S. Rac.   1984.
Determination of  the chronic mammalian toxlcologlcal  effect  of  RDX:  Twenty-
four  month  chronic  tox1c1ty/carc1nogen1c1ty  study of  hexahydra-1.3,5-tr1-
n1tro-l,3,5-tr1az1ne (RDX) In  the  B6C3F1 hybrid  mouse.   Phase VI.  Vol.  1.
ITT  Research  Institute.   Chicago.   IL.   U.S.  Army   Medical  Research  and
Development Command, Contract No.  DAMD 17-79-C-9161.

U.S.  EPA.  1988.   Carcinogen Risk  Assessment  Verification  Endeavor  (CRAVE)
Work  Group.   Verified, pending  concurrence on final  coversheet  and  Input
onto IRIS.

U.S.  EPA.   1989.    Health  and   Environmental  Effects  Document   for  RDX
(Cyclonlte).  Prepared  by the Office of  Health  and Environmental  Assessment,
Environmental Criteria  and Assessment  Office,  Cincinnati,  OH  for  the Office
of Solid Waste and Emergency Response,  Washington.  DC.

Selenium sulflde
NCI/NTP  (National   Cancer  Institute/National   Toxicology  Program).    1980.
Bloassay  of   selenium  sulflde  (gavage)  for  possible  carclnogenlclty.   NCI
Technical Report Series No. 194.   NTP No. 80-17.
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U.S. EPA.  1989.  Health and  Environmental  Effects  Document for Selenium and
Compounds.   Prepared  by the  Office  of Health and  Environmental Assessment,
Environmental Criteria  and Assessment Office, Cincinnati,  OH  for  the Office
of Solid Waste and Emergency Response. Washington, DC.

Slmazlne
U.S.  EPA.    1984.   Health   and  Environmental  Effects  Profile  for  Slmazlne.
Prepared by  the  Office  of  Health  and Environmental  Assessment, Environmental
Criteria and Assessment Office, Cincinnati, OH for the Office of Solid Waste,
Washington, DC.

U.S. EPA.   1989.  Carcinogen  Risk  Assessment Verification Endeavor  (CRAVE)
Work  Group.   Verified,  pending  concurrence  on  final  coversheet  and  Input
onto IRIS.

Sodium dlethyldUhlocarbamate
BRL  (Blonetlcs  Research Laboratories).   1968.  Evaluation  of carcinogenic,
teratogenlc  and  mutagenlc   activities  of  selected  pesticides  on  Industrial
chemicals.   Vol.  I. Carcinogenic  study.   Prepared  for  National Cancer Insti-
tute.   U.S.  Dept. Commerce,  Nat.  Tech.  Info.  Serv.,  Washington,  DC.   NTIS
PB223159.

U.S.  EPA.    1988.  Health  and  Environmental  Effects   Document for  Sodium
dlethyldUhlocarbamate.  Prepared by the Office of  Health  and Environmental
Assessment,  Environmental  Criteria and  Assessment Office,  Cincinnati, OH for
the Office of Solid Waste and Emergency Response, Washington. DC.

Styrene
Jeney,  G., M.  Balner. J.  Quast.  et  al.  1978.  Two-year  chronic  Inhalation
toxlclty  and  carclnogenlclty  study  on  monomer1c  styrene   In  rats.   Dow
Chemical Study for Manufacturing Chemists Association.   December 6.

NCI (National Cancer  Institute).  1979.   National Cancer Institute  Technical
Report  Series,  No.  185:   Bloassay of Styrene for  Possible Carclnogenlclty.
Litton Blonetlcs, Inc., Kensington, MD.

U.S. EPA.   1989.  Health  Effects  Assessment  for Styrene.   Prepared by  the
Office  of  Health and  Environmental   Assessment.  Environmental  Criteria  and
Assessment Office, Cincinnati,  OH for  the  Office  of Emergency  and Remedial
Response. Washington,  DC.

U.S. EPA.   1989.  Carcinogen Risk Assessment Verification  Endeavor  (CRAVE)
Work Group.   Verified,  pending concurrence  on  final  coversheet   and  Input
onto IRIS.

2.3.7.8-TCDD
Koclba,  R.J.,  D.G.  Keyes,   J.E.  Bower et al.  1978.   Results of a two-year
chronic  toxlclty  and  oncogenldty  study  of  2,3,7,8-tetrachlorodlbenzo-p-
dloxln In rats.   Toxlcol Appl. Pharmacol.   46(2): 279-303.

U.S. EPA.   1984.  Health  Effects Assessment  for 2,3,7,8-TCDD.  Prepared  by
the Office  of Health  and   Environmental  Assessment,  Environmental  Criteria
and  Assessment   Office,  Cincinnati,   OH  for   the  Office   of  Emergency  and
Remedial Response, Washington. DC.
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U.S. EPA.  1985a.  Drinking Water  Criteria  Document for 2,3,7,8-Tetrachloro-
d1benzo-p-d1ox1n.   Prepared  by  the  Office  of  Health  and  Environmental
Assessment, Environmental Criteria and Assessment  Office.  Cincinnati.  OH for
the Office of  Drinking  Water.  Washington.  DC.   EPA  600/X-84-194-I.   NTIS PB
86-117983.

U.S. EPA.  1985b.  Health Assessment  Document for  Polychlorlnated Dlbenzo-p-
dloxln.   Office  of  Health   and   Environmental  Assessment.  Environmental
Criteria  and  Assessment Office.  Cincinnati. OH.   EPA  600/8-84-014F.   NTIS
PB86-122546.

1.1.1,2-Tetrachloroethane
NTP  (National   Toxicology   Program).   1983.   Carclnogenesls   studies  of
1.1.1.2-tetrachloroethane (CAS  No.  630-20-6) In F344/N  rats  and  B6C3F1  mice
(gavage  studies).   NTP-81-53;   NIH  Publ.  No.  83-1793;  NTP  Technical  Report
Seroes No. 237.  NTIS. Springfield. VA.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of Health and  Environmental   Assessment.  Environmental Criteria  and
Assessment Office. Cincinnati,  OH.

1.1.2.2-Tetrachloroethane
NCI  (National  Cancer  Institute).   1978.   Bloassay of  1,1,2,2-tetrachloro-
ethane  for possible carclnogenldty.  NCI Carclnogenesls  Tech. Rep.  Ser. No.
27. DHEW No.  (NIH) 78-827.

U.S. EPA.   1980.  Ambient  Water Quality Criteria Document  for  Chlorinated
Ethanes.   Prepared  by  the  Office  of Health and  Environmental  Assessment,
Environmental  Criteria  and  Assessment Office, Cincinnati.  OH  for  the  Office
of Water  Regulations and Standards. Washington,  DC.  EPA-440/5-80-029.   NTIS
PB 81-117400.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).   Online.
Office  of Health and  Environmental   Assessment,  Environmental Criteria  and
Assessment Office, Cincinnati,  OH.

Tetrachloroethylene (Perchloroethylene)
NCI  (National  Cancer  Institute).    1977.    Bloassay  of  tetrachloroethylene
(CAS No.  127-18-4)  for  possible  carclnogenldty.   NCI  Carclnogenesls  Tech.
Rep. Ser. No.  13, DHEW No.  (NIH) 78-813.

NTP (National  Toxicology Program).  1986.   Carclnogenesls  bloassay of  tetra-
chloroethylene  (perchloroethylene)   (CAS  No.  127-18-4)   In   F344  rats  and
B6C3F1  mice (Inhalation  study).  NTP Tech. Report.  Ser.  No. 311.

U.S. EPA.  1985.   Drinking  Water Criteria  Document  for  Tetrachloroethylene.
Prepared by the Office  of Health and  Environmental Assessment, Environmental
Criteria  and  Assessment Office, Cincinnati,  OH for  the Office  of  Drinking
Water,  Washington, DC.   Final  Document.   NTIS PB 86-118114.

U.S. EPA.   1986.  Addendum to  the  Health  Assessment  Document   for  Tetra-
chloroethylene   (Perchloroethylene):   Updated   Carclnogenldty   Assessment.
Office  of  Health  and  Environmental Assessment,  Carcinogen  Assessment  Group,
Washington, DC.  EPA/600/8-82/005FA.   External Review Draft.
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U.S.  EPA.   1988.   Updated  Health  Effects  Assessment  for  Tetrachloroethy-
lene.   Prepared  by  the  Office  of   Health  and  Environmental  Assessment,
Environmental  Criteria  and Assessment Office, Cincinnati,  OH  for the Office
of Emergency and Remedial Response,  Washington, DC.  ECAO-CIN-H009a.

p.g.a.a-Tetrachlorotoluene
Fukada,  K.S.,  Hatsashlta  and  K.   Takemotol.   1979.   Carclnogenldty  of
p-chlorobenzotrlchlorlde.  Proc of Japan Assoc. of Ind. Health,   p. 330-331.

U.S.  EPA.   1987.   Health and  Environmental  Effects  Document  for  Selected
Chlorinated  Toluenes.   Prepared  by  the Office  of Health  and Environmental
Assessment,  Environmental  Criteria and Assessment  Office, Cincinnati, OH for
the Office of Solid Waste and Emergency Response. Washington, DC.

Tetrachlorovlnphos (Stlrofos)
NCI  (National  Cancer  Institute).  1978.   Bloassay of  Tetrachlorvlnphos for
Possible  Carclnogenldty.   NCI  Carcinogen.   Tech.  Rep.  Ser.  No.  33.   NTIS
PB278650.

U.S.  EPA.   1984.   Health and  Environmental  Effects  Profile  for  Stlrofos.
Prepared  by  the Office  of  Health  and  Environmental Assessment, Environmental
Criteria  and  Assessment  Office, Cincinnati, OH  for  the  Office  of  Solid
Waste, Washington, DC.

Thallium and Compounds
U.S.  EPA.   1989.   Carcinogen  Risk  Assessment Verification  Endeavor  (CRAVE)
Work  Group.   Verified,  pending  concurrence  on final  coversheet and  Input
onto IRIS.

2.4-Toluened1am1ne
NCI  (National  Cancer  Institute).   1979.  Bloassay of  2,4-dlamlnotoluene for
possible Carclnogenldty.  NCI Carcinogen.  Tech.  Rep.  Ser. No.  162.

U.S.  EPA.   1986.   Health and Environmental Effects Profile  for 2,4-Toluene-
dlamlne.   Prepared  by  the Office  of Health  and  Environmental  Assessment,
Environmental Criteria  and  Assessment  Office, Cincinnati, OH  for the Office
of Solid Waste and Emergency Response,  Washington,  DC.

o-Toluldlne
Hecht,  S.S.,  K.  El-Bayouml,  A.  Rlvenson  and E. Flnala.   1982.  A Study  of
chemical  Carclnogenldty  of  o-tolu1d1ne  hydrochlorlde and  o-nltrosotoluene
In rats.  Cancer  Lett.  16: 103-108.

U.S.  EPA.   1984.   Health and  Environmental  Effects  Profile for  Toluldlnes.
Prepared by  the Office  of  Health  and  Environmental Assessment, Environmental
Criteria  and Assessment  Office,  Cincinnati,  OH  for   the  Office  of  Solid
Waste, Washington, DC.

p-Toluldlne
U.S.  EPA.   1984.   Health and  Environmental  Effects  Profile for  Toluldlnes.
Prepared by  the Office  of Health  and  Environmental Assessment, Environmental
Criteria  and Assessment  Office,  Cincinnati,  OH  for   the  Office  of  Solid
Waste, Washington, DC.
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Welsburger, E.K., A.B. Russfield and F.  Homburger,  et  al.   1978.  Testing of
twenty-one  environmental  aromatic  amines   of   derivatives  for  long-term
toxlclty or carclnogenlclty.   0.  Environ. Pathol. Toxlcol.   2(2): 325-256.
Toxaphene
LHton B1onet1cs,  Inc.   1978.
Prepared  by  Litton  Blonetlcs,
Wilmington, DE.
Carcinogenic  evaluation  In mice:  Toxaphene.
 Inc.,  Kensington,  MO  for  Hercules,   Inc.,
U.S.  EPA.   1980.   Ambient  Water  Quality Criteria  Document  for  Toxaphene.
Prepared by the Office of Health  and  Environmental  Assessment, Environmental
Criteria  and  Assessment  Office,   Cincinnati.  OH  for  the  Office  of  Water
Regulations  and  Standards.   Washington,  DC.    EPA-440/5-80-076.   NTIS  PB
81-117863.

U.S. EPA.  1987.   Health  Effects  Assessment  for Toxaphene.   Prepared  by the
Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office,  Cincinnati,  OH for the Office  of Emergency  and Remedial
Response, Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk   Information   System  (IRIS).    Online.
Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

2.4.6-Trlchloroanlllne and 2.4.6-tr1chloroan1l1ne hydrochlorlde
Welsburger, E.L., A.B. Russfleld, R. Homburger.  et  al.   1978.  Testing of 21
environmental   aromatic  acmlnes  or  derivatives  for long-term   toxlclty  or
carclnogenlclty.  J. Environ.  Pathol.  Toxlcol.   2:  235-258.

U.S. EPA.   1987.   Health and  Environmental  Effects Document  for Trlchloro-
anlllnes.  Prepared  by the  Office of Health  and  Environmental  Assessment,
Environmental  Criteria and Assessment  Office.  Cincinnati, OH  for  the  Office
of Solid Waste and Emergency  Response,  Washington,  DC.
1.1,2-TrIchloroethane
NCI  (National  Cancer Institute).   1978.   Bloassay
for  possible  carclnogenlclty.   NCI  Carclnogenesls
DHEW No. NIH 78-1324.
                    of  1,1,2-trlchloroethane
                    Tech. Rep.  Ser.  No. 74,
U.S.  EPA.   1980.  Ambient  Water  Quality  Criteria Document  for  Chlorinated
Ethanes.   Prepared  by  the  Office  of Health  and Environmental  Assessment,
Environmental Criteria  and  Assessment Office,  Cincinnati, OH  for  the Office
of Water Regulations and Standards, Washington,  DC.   EPA-440/5-80-029.   NTIS
PB 81-117400.

U.S.  EPA.    1984.    Health   Effects  Assessment  for  1,1,2-Trlchloroethane.
Prepared by  the  Office  of Health and  Environmental Assessment. Environmental
Criteria and  Assessment Office,  Cincinnati, OH  for  the  Office of  Emergency
and Remedial Response,  Washington,  DC.

U.S.  EPA.    1990.    Integrated  Risk   Information  System  (IRIS).    Online.
Office  of  Health and  Environmental  Assessment,  Environmental Criteria  and
Assessment  Office,  Cincinnati,  OH.
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Trlchloroethylene
Fukuda, K.,  K.  Takemoto, H.  Tsuruta.   1983.  Inhalation  carclnogenlcUy of
trlchloroethylene In mice and rats.  Ind.  Health 21:  243-254.

Maltonl,  C.,  G.  Lefemlne,  G.  Cottl.    1986.    Experimental  Research  on
Trlchloroethylene  Carclnogenesls.    Archlv.  Res.  Industrial  Carclnogenesls
Series.   Maltonl,  C..  Mehlman, M.A.,  Eds., Vol.  V.   Princeton  Scientific
Publishing Co.,  Inc., Princeton, NJ, p. 393.

NCI   (National   Cancer   Institute).    1976.   Carclnogenesls   bloassay  of
trlchloroethylene.   NCI  Carclnogenesls  Tech. Rep.  Ser.  No. 2,  DHEM  No. NIH
76-802.

NTP   (National  Toxicology   Program).   1983.    Carclnogenesls  bloassay  of
trlchloroethylene.   NTP Tech Rep. Ser.  No. 243,  NIH 83-1799.

U.S.  EPA.   1985.   Health Assessment Document for  Trlchloroethylene.   Office
of  Health  and Environmental  Assessment,  Environmental  Criteria  and  Assess-
ment  Office,  Cincinnati,  OH Research Triangle Park.  NC.  EPA 600/8-82-006F.
NTIS PB 85-249696.

U.S.  EPA.   1987.   Addendum  to the Health Assessment  Document  for  Trlchloro-
ethylene.   Office of  Health  and Environmental Assessment,  Carcinogen  Assess-
ment Group, Washington, DC.   EPA 600/8-82-006FA.   External  Review Draft.

U.S.  EPA.   1988.   Updated  Health  Effects Assessment  for  Trlchloroethylene.
Prepared by  the Office of Health and Environmental  Assessment, Environmental
Criteria and  Assessment  Office, Cincinnati,  OH  for the Office  of  Emergency
and Remedial Response, Washington, DC.

2.4.6-Tr1ch1orophenol
NCI  (National  Cancer  Institute).   1979.   Bloassay of  2,4,6-trlchlorophenol
for  possible  carclnogenlcUy.  NCI  Carclnogenesls  Tech. Rep. Ser. No.  155,
DHEW No. NIH 79-1711.

U.S.  EPA.   1980.  Ambient  Water Quality  Criteria  Document  for  Chlorinated
Phenols.   Prepared  by  the  Office  of  Health and  Environmental  Assessment,
Environmental Criteria and  Assessment  Office.  Cincinnati.   OH  for  the Office
of Water Regulations  and  Standards,  Washington.  DC.   EPA-440/5-80-032.   NTIS
PB 81-117434.

U.S.  EPA.   1984.    Health   Effects Assessment   for   2.4,6-Trlchlorophenol.
Prepared by  the Office of Health and Environmental  Assessment, Environmental
Criteria and  Assessment  Office, Cincinnati,  OH  for  the Office  of  Emergency
and Remedial Response, Washington, DC.

U.S.  EPA.   1987.   Health and Environmental  Effects Document  for Chlorinated
Phenols.   Prepared  by  the  Office  of  Health and Environmental  Assessment,
Environmental Criteria and  Assessment  Office,  Cincinnati.   OH  for  the Office
of Solid Waste and  Emergency Response,  Washington,  DC.

U.S.  EPA.    1990.    Integrated  Risk  Information  System   (IRIS).    Online.
Office  of  Health and  Environmental Assessment.  Environmental  Criteria  and
Assessment Office,  Cincinnati, OH.
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Trlfluralln
Emmerson,  J.L.,  E.G.  Pierce,  J.P.  McGrath,  et  al.    1980.   The  Chronic
Toxldty of Compound 36352  (Trlfluralln) Given  as a Compounds of the Diet to
the  Fischer  344  Rats  for  Two Years.   Studies  R-87  and  R-97  (unpublished
study  received  September  18,  1980  under  1471-35;   submitted  by  Elanco
Products Co., Division of Ell Lilly and Co., Indianapolis, IN).

U.S. EPA.   1984.   Health and Environmental Effects  Profile for  Trlfluralln.
Prepared by the Office of  Health  and  Environmental Assessment, Environmental
Criteria  and  Assessment  Office,   Cincinnati,  OH for  the  Office  of  Solid
Waste,  Washington, DC.

U.S.  EPA.   1990.   Integrated  Risk  Information  System  (IRIS).    Online.
Office  of  Health  and  Environmental Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati. OH.
Trlmethyl phosphate
NCI  (National  Cancer  Institute).   1978.  Bloassay  of
possible carclnogenldty.  NCI Carcinogen.  Tech. Rep..
                   trlmethylphosphate
                   Ser. No. 81.
     for
U.S.  EPA.   1985.   Health and  Environmental Effects  Profile  for  Trlmethyl
Phosphate.  Prepared  by the Office  of  Health and  Environmental  Assessment,
Environmental  Criteria  and  Assessment  Office, Cincinnati, OH  for  the Office
of Solid Waste and Emergency Response,  Washington, DC.

Vinyl chloride
ATSDR  (Agency for  Toxic  Substances  and  Disease  Registry).   1988.   First
Post-Comment Draft.  Revised Toxlcologlcal Profile  for  Vinyl  Chloride.   U.S.
Public Health  Service.   Public  Comment  Draft.

Feron,  V.J.,  C.F.M.  Hendrlksen,  A.J.  Speek et  al.   1981.    Llfespan  oral
toxlclty  study  of  vinyl  chloride In  rats.   Food  Cosmet.  Toxlcol.   19(3):
317-333.

Maltonl.  C.,   G.   Lefemlne.  A.  Clllbertl   et  al.   1980.    Vinyl  chloride
carclnogenldty bloassays  (BT  project)  as  an  experimental  model  for  risk
Identification and assessment  In environmental  and  occupational  carclno-
genesls.   Ep1dem1ol.  An1m.  Epldemlol.  Hum:  Cas  Chlorure  Vlnyle  Monomere,
(Reun Club Cancerog Chlm), 20th, Meeting Date 1979,  p.  11-112.   Publ Essent,
Paris, France.

Maltonl,  C.,   G.   Lefemlne,  A.  Clllbertl   et  al.   1981.    Carclnogenldty
bloassays  of   vinyl  chloride  monomer:  A  model  of  risk assessment  on  an
experimental basis.  Environ.  Health  Perspect.  41:  329.

U.S. EPA.  1984.   Health Effects Assessment  for Vinyl Chloride.  Prepared  by
the  Office  of Health  and Environmental  Assessment, Environmental  Criteria
and  Assessment  Office,  Cincinnati.   OH  for the Office  of  Emergency and
Remedial Response, Washington,  DC.
U.S.  EPA.   1985a.   Drinking Water  Criteria  Document
Office of Drinking Water,  Washington,  DC.   Final  Draft.
                     for Vinyl  Chloride.
                     NTIS PB86-118320.
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U.S.   EPA.   1985D.   Health and  Environmental  Effects  Profile for  Chloro-
ethene.   Prepared  by  the  Office  of  Health  and  Environmental  Assessment.
Environmental  Criteria and  Assessment  Office.  Cincinnati. OH  for  the Office
of Solid Waste and Emergency Response.  Washington,  DC.
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