United States        OSWER (OS-230)      OERR 9200.6-303-(89-4)
             Environmental Protection    ORD (RD-689)       October 1989
             Agency
&EPA       Health Effects Assessment
             Summary Tables

             Fourth Quarter
             FY1989

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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                                11                              10/10/89

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                               TABLE  OF  CONTENTS


                                                                        Page
INTRODUCTION 	    1

WHAT'S NEW IN THE FOURTH QUARTER HEAST 	    3

USER'S GUIDE: CHEMICAL TOXICITY	   12

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-7

REFERENCES FOR TABLES A	  D-l

REFERENCES FOR TABLES B.	D-83
 0618h                                 111                             12/29/89

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                                 INTRODUCTION

    This document  contains the  "Fourth  Quarter FY89"  update of  the  Health
Effects Asessment  Summary  Tables (HEAST) prepared  for  Superfund use  by  the
Environmental Criteria  and Assessment Office  (ECAO-CIn)  In  EPA's  Office  of
Health  and  Environmental  Assessment.   Chemicals  considered  are   those  for
which  Health  Effects  Assessment Documents, Health  and  Environmental  Effects
Profiles,  Health  and  Environmental   Effects   Documents,  Health  Assessment
documents  or Air  Quality  Criteria  Documents  have been  prepared by  ECAO.
Rad1onucl1des considered are  those  believed to be  most  commonly encountered
at  Superfund  sites.    This   report   1s  an  excellent  "pointer"  system  to
Identify  current  literature  or  changes  1n  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   toxldty  criteria  are   based.    Original  assessment
documents  must  be consulted  by risk  assessors In order  for them to  fully
appreciate the  strengths and  limitations of a  specific data  base.   Original
source  documents  will   allow  for   the  most   complete  characterization  of
potential  toxlclty associated with  the  range  of exposure  pathways  generally
evaluated at  Superfund  sites.   The  HEAST 1s  structured  to point the  user  to
these sources.
    We 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 toxldty for  Superfund sites:
0618h                               -1-                              12/29/89

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

    2. ECAO  Health   Effects   Assessment   Summary  Tables  and   dted
       references  (updated  quarterly).  Limited  copies available  from
       the  Superfund   Docket  (202/382-6940).   To  update  mailing  list
       Information,  call   Superfund's   Toxics   Integration   Branch  at
       202/475-9486.

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

    4. Do  not  consult either the  tox1c1ty  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).

    Should  there  be  any  questions  regarding  the above  Information,  please
call Superfund's Toxics Integration Branch at 202/475-9486.
0618h                               -2-                              01/11/90

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                      WHAT'S NEW IN FOURTH QUARTER HEAST

GENERIC ISSUES:

    This  update  of  the  HEAST Includes  new  tables and  a  user's  guide  that
contain  quantitative  Information  useful  In  evaluating  carcinogenic  risks
from exposures to radlonuclldes (see page C-l).

    A  significant  change In  format  has  been  made In  HEAST  Tables A and  B
since  the  last  version;  Individual  chemicals  formerly  listed  under  a
chemical class are now listed Individually In alphabetical  order.

    The fourth quarter 1989 update of  the HEAST has  been expanded to Include
entries for  chemicals that were  subjects of  Final  Documents of  Health  and
Environmental  Effects Profiles  (HEEPs)  and  that had  not  been  entered  as
subjects of  previous  HEAs,  HADs,  AQCDs,  or HEEDs.  Acceptable  Dally Intakes
(ADI)  and  slope  factors  (q*)  derived  In  HEEPs have  been  entered  Into
Tables  A  and  B,  respectively.   ADIs  presented  in HEEPS  are  Identical  to
RfDs,  which  1s  the  currently accepted  term  for  these  values.   Appropriate
footnotes  Indicate  the  current  status  of  these  values.    If  the  HEEP
estimated that  the Information available was  Inadequate or  Insufficient  for
deriving an  ADI, a statement  was  entered In Table A  Indicating so.  Chemi-
cals  from HEEPs added  to  Table  B   Include  those assigned  to  a  U.S.  EPA
carclnogenlclty  group,   even  If  no  quantitative  estimate for  carcinogenic
potential was made In the HEEP.

    Please  be  advised  that   Inhalation  RfDs  for  acroleln,  bromomethane,
cumene,    p-dlchlorobenzene,     eplchlorohydrin,    methylene     chloride,
nitrobenzene,  toluene  and  mixed  xylenes  have  been   verified   by  the  RfD
Workgroup.   However,  these  values should be considered as  Interim, pending
Workgroup  concurrence   on  the   final   cover   sheets   and   input  on  IRIS.
Inhalation RfDs  for   the  other  34 chemicals  have been excerpted  from final
EPA  documents  prepared  prior  to  the development  and   Implementation  of  the
Interim Methodology  for  Inhalation  RfDs (U.S. EPA, 1989).   Interim Methods
for   Development  of   Inhalation  Methods   for   Development   of  Inhalation
Reference Doses.  EPA/600/8-88/066F).   Inhalation  RfDs for  these chemicals
will be submitted to the RfD Workgroup for review on a priority basis.

    A  new footnote (bb)  has been  added  to indicate RfD values that have  been
calculated based on developmental effects.

    For  chemicals  with  verified RfD   values  or  slope  factors   that   are
currently under  review,  1t was  agreed  by the  Superfund Office  and ECAO to
retain the verified  values  in the Tables  unless  there  have  been fundamental
errors or oversight  In  the  development  of the  verified values.   Appropriate
footnotes explain the current status  of these values.

    RfD and  CRAVE  Workgroup status  reports dated  10/31/89 were  used in  this
update of the Tables.
0622h                                -3-                            01/11/90

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CHEMICAL-SPECIFIC CHANGES TO TABLE A; OTHER THAN CARCIN06ENICITY

The Following Chemicals Are New Entries To Table A From Final HEEPs:

       Acephate
       Acroleln
       Acrylamlde
       Alachlor
       Allldochlor
       Ally! Alcohol
       Allyl Chloride
       Ametryn
       l-Amlno-2-Naphtol
       l-Amlno-2-Naphtol Hydrochlorlde
       o-, m-, p-Amlnophenols
       Anthracene
       Atrazlne
       Benefln
       Benzal Chloride
       Benzaldehyde
       l,l'-B1phenyl
       Bromlnated 01benzo-p-01ox1ns
       Bromlnated Dlbenzofurans
       Bromoacetone
       Bromochloroethanes
       Bromodlchloromethane
       4-Bromo Phenyl Ether
       Bromophos
       Bromoxynll
       Bromoxyn'n Octanoate
       Busan 77
       Busan 90
       Butylate
       t-Butylchlorlde
       Butyrolactone, gamma
       Captafol
       Captan
       Carbaryl
       Carbofuran
       m-Chloron1trobenzene
       Chlorotoluenes
       Chlorpyrlfos
       Chlorpyrlfos-methyl
       Chlorthalonll
       Chlorthlophos
       Chrysene
       Cyanazlne
       Cycloate
       Cyclohexanol
       Dacthal
       Dalapon
       2.4-DB
       Decabromodlphenyl Oxide
       Dlazlnon
       1,4-Dlbromobenzene


0622h                                 -4-                            01/11/90

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      Dlchloroprop
      Dlchloropropanes
      1,3-D1chloropropene
      N,N-D1ethylan1line
      Dlethylformamlde
      1,2-Dlethylhydrazlne
      Dlmethoate
      N,N-D1methylan1l1ne
      N.N-Dlmethylformamide
      2,3-, 2,4-, 2,5-, 3,6-D1methylphenols
      Dimethyl Terephthalate
      N,N-D1methylurea
      Dinltrobenzenes
      2,6-D1n1tro-p-Cresol
      4,6-ClnHro-o-Cresol
      Dlnltrophenols
      Dlnltrotoluenes
      Dlnoseb
      N,N-Dlphenylam1ne
      Direct Llghtfast Blue
      EPIC
      Ethoprop
      2-Ethoxyethanol Esters
      Ethyl Acetate
      N-Ethylanlllne
      Ethylene Thlourea
      Ethyl Methacrylate
      Flurldone
      Folpet
      Hexabromobenzene
      Hexachlorophene
      Hexaraethylenedlamlne
      Isobutyl Alcohol
      Isopropalln
      Lead  Alkyls
      Llnuron
      Malathlon
      Malelc Anhydride
      MalononHrlle
      Hancozeb
      Maneb
      MCPA
      MCPB
      MCPP
      Mephosfolan
      Merphos
      Merphos Oxide
      Methoxychlor
      2-Methoxyethanol Acetate
      Methyl Acetate
      Methyl Acrylate
      Methyl Bromide
      Methyl Chloride
      Methylcyclohexane
      Methylene  Bromide


0622h                                -5-                           01/11/90

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      4,4'-Methy1ened1phenyl Isocyanate
      Methyl Ethyl Benzenes
      Methyl Isocyanate
      Methyl Methacrylate
      Methyl Parathlon
      a-Methyl Styrene
      Mollnate
      1,4-Naphtoqulnone
      o-t ro-, p-NHroanlllnes
      Nltromethane
      p-NHrosod1phenylam1ne
      o-, ro-, p-NHrotoluenes
      Octabromodlphenyl Ether
      Paraldehyde
      Pebulate
      Pendlmethalln
      Pentabromodlphenyl Ether
      Pentachloronltrobenzene
      1,1,2.3,3-Pentachloropropene
      o-, m-, p-Phenylened1am1nes
      Phosgene
      o-, m-, p-Phthallc Acids
      Phthallc Anhydride
      Profluralln
      Propachlor
      PropazAne
      2-Propenolc Acid
      Proplonltrlle
      Pyrldlne
      Ronnel
      Slmazlne
      Stlrofos
      Styrene
      Temephos
      Terbufos
      Terephthallc  Acid
      Tetrachloroazobenzene
      Tetrachloroazoxybenzene
      Tetrachlorohydrazobenzene
      1,1,2,3-Tetrachloropropene
      2-(Th1ocyanoraethylth1o)-benzoth1azole
      2,3-;  3,4-Toluened1am1ne
      Toluene-2,5-01am1ne
      Toluene-2,6-01am1ne
      m-Toluldlne
      Trlallate
      1,2,4-Trlbromobenzene
      1,2,3-Trlchloropropene
      Trlfluralln
      Trlnltrophenols
      Vernolate
      4-V1nyl-l-cyclohexene
      Z1neb
0622H                                -6-                            01/11/90

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The Following  Chemicals  are New Entries  to  Table A from HEEDs Finalized  In
the 3rd and 4th Quarters  of FY89:

       AramHe
       Benzyl Alcohol
       1-Butanol
       Cacodyllc Add
       2-Chloro-l,3-butad1ene
       Dlethyl-p-nltrophenyl phosphate
            (paraoxon)
       Endothall
       Fluoride
       Glycldaldehyde
       Heptane
       n-Hexane
       2-Hexanone
       Malelc hydrazlde
       Methyl chlorocarbonate
       Monochlorobutanes
       Nitrite
       Octamethylpyrophosphoramide
       Pentachlorobenzene
       Polybromlnated Blphenyls
       RDX (Cyclonlte)
       Thlofanox
       Thlram
       Trlnltrobenzene
AcetonUrlle
    A  footnote  has  been added to  Indicate  that  the  oral  RfO Is being recon-
sidered.

Acroleln
    A  footnote  has been added to Indicate that an Inhalation RfD Is verified.

Arsenic
    A  footnote  has  been added to  Indicate  that  the  oral  RfO 1s under review
by  the Work Group.

Barium
    A  footnote  has  been added to  indicate  that  the  oral  RfD 1s being recon-
sidered by  the  Work Group.

Bromomethane
    A  footnote  has been added to Indicate that an Inhalation RfD Is verified.

Butyl  Benzyl  Phthalate
    The footnote  now  Indicates that  the oral RfD 1s available on IRIS.

Cadmium
    A  footnote  has   been  added  to  Indicate  that  the oral  RfD  values  are
available on  IRIS.
 0622h                                -7-                            01/11/90

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Chlorobenzene
    The footnote  now Indicates  that  the verified  oral  RfD Is available  on
IRIS.

Chromium
    Hexavalent and trlvalent Chromium are now  listed  under  Chromium (VI)  and
(III), respectively.

m-. o-. p-Cresol
    A  reference  to a HEEP  was added to  the Reference column and  Reference
list.

1,l-D1ch1oroethylene
    The footnote  now Indicates  that  the oral  RfD  Is being reconsidered  by
the Work Group.

1,2-D1chlorobenzene
    The footnote  now Indicates  that  the verified  oral  RfD Is available  on
IRIS.

1,3-Dlchloropropene
    Information for  the  Inhalation route has  been  updated based on  a  final
HEED (1989).

EpIchTorohydrln
    A  footnote has been added to Indicate that an Inhalation RfD Is  verified.

Ethyl  Benzene
    A  reference  to  a HEEP (1986)  was  added  to  the  Reference column  and
Reference list.

Isophorone
    The footnote now  Indicates that the oral RfD  Is available on IRIS.

Nitrobenzene
    The footnote  now Indicates  that the oral  RfD, while still on  IRIS,  1s
being  reconsidered by the Work Group.   A new footnote has also been added to
Indicate that an Inhalation RfD 1s verified.

Phenol
    The footnote  now Indicates  that the  verified  oral RfD Is  available on
IRIS.

Selenium
    Information for  the  Inhalation route  has  been updated based on  a  final
HEED  (1989).  Subchronlc oral RfD value has also  been revised.

Thallium SelenUe
    The footnote  now Indicates  that the oral  RfD Is  being  reconsidered by
the Work Group.

Toluene
    The footnote  now Indicates  that the  oral  RfD Is  being  reconsidered by
the Work Group.
 0622h                                -8-                            01/11/90

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1.2.4-Trlchlorobenzene
    The footnote  now Indicates that  the  oral  RfD Is being withdrawn  by  the
Work Group.

1.1.2-Tr1ch1oro-1.2.2-tr1f1uoroethane
    The footnote  now Indicates  that  the oral  RfD 1s being  reconsidered  by
the Work Group.

Vanadium
    A footnote has been added to Indicate that the oral  RfD Is under review.
CHEMICAL-SPECIFIC CHANGES TO TABLE B: CARCINOGENICITY

The Following Chemicals Are New Entries To Table B From Final HEEPs:

       Acephate
       Acrylamlde
       Aniline
       Azobenzene
       Benzo(k)fluoranthene
       BenzotrlchloMde
       Benzyl Chloride
       Bromoethene
       Captafol
       Carbazole
       Chloranll
       4-Chloro-2-Methylan111ne
       4-Chloro-2-Hethylan111ne HC1
       o-, p-Chloronltrobenzenes
       Chlorthalonll
       Decabromodlphenyl Ether
       Decabromodlphenyl Oxide
       Dlallate
       1,2-D1bromoethane
       l,3-D1chloropropene
       3,3'-D1methoxybenz1d1ne
       2,4-D1methylan1l1ne
       2,4-D1methylan1l1ne Hydrochlorlde
       3,3'-D1methy1benz1d1ne
       1,l-D1methylhydraz1ne
       1,2-D1methylhydraz1ne
       Dimethyl Sulfate
       Direct Black  38
       Direct Blue 6
       Direct Brown  95
       Direct Sky Blue 68
       Ethyl Acrylate
       Ethylene Thlourea
       Folpet
       Formaldehyde
       Hexachlorocyclohexane
       Hydrazlne
       Hydrazlne  Sulfate
 0622h                                -9-                            01/11/90

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       2-Methoxy-5-N1troan1l1ne
       2-MethylanlHne
       2-Methylanlllne  Hydrochlorlde
       4,4'-Methyleneb1sbenzened1am1ne
       4,4'-MethylenebU(N,N'-dimethyl) Aniline
       Methylhydrazlne
       2-Methyl-5-N1troannine
       Niagara Blue  48
       2-NHropropane
       N-N1trosod1-n-butylam1ne
       N-N1trosod1ethanolam1ne
       N-N1trosod1ethylam1ne
       N-N1trosodlmethylaralne
       N-NUrosodlphenylamlne
       N-N1trosodl-n-propylamlne
       N-NHrosomethylethylamlne
       N-N1trosomethylv1nylam1ne
       l,2,3,4,5-Pentabromo-6-Chlorocyclohexane
       Pentachloronltrobenzene
       o-Phenylenedlamlne
       2-Phenylphenol
       Propylene Oxide
       Qulnollne
       Stlrofos
       2,4-Toluened1am1ne
       o-, p-Tolu1d1ne
       Trlfluralln
       TMmethyl Phosphate

The Following  Chemicals  Are New Entries To  Table A From HEEDs Finalized In
The 3rd and 4th Quarters of FY89:
       Aramlte
       Dlbromochloromethane
       Glycldaldehyde
       Polybromlnated blphenyls
       RDX (Cyclonlte)

Benzotr1chlor1de
    A  footnote  has  been added  to Indicate that  the  slope factors for  oral
and Inhalation routes are being reviewed by the CRAVE  Workgroup.

Bromoform
    Information for  the carclnogenldty has  been updated based  on  a  final
HEED (1989).

Chromium
    Hexavalent Chromium Is  now listed under Chromium (VI).

Decabromodlphenyl  Oxide
    A  footnote  had  been added  to  Indicate that the  carcinogenic  welght-of-
evldence has been verified.
0622h                                -10-                           01/11/90

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1.3-Dlchloropropene
    Information for  the  Inhalation route has  been  updated based on  a  final
HEED  (1989).    The  oral  quantitative  risk  estimate  for  the  carcinogenic
assessment has been withdrawn from IRIS.

Dimethyl Sulfate
    Footnote changed to Indicate availability on IRIS.


Formaldehyde
    The footnote now Indicates  that  the Inhalation  slope factor 1s  available
on IRIS.

Methyl Ethyl Ketone
    The footnote  now Indicates  that  the  carcinogenic we1ght-of-ev1dence has
been verified.

Hethylene Chloride
    The  footnote  now  Indicates  that the oral  slope factor  Is being recon-
 sidered by CRAVE.

Trlchloroethylene
    The  footnote  now  Indicates  that the oral  and  Inhalation  slope factors
 have been withdrawn  from IRIS.

 2.4.6-Tr1ch1oropheno1
    The footnote  now Indicates  that  the oral slope factor 1s being withdrawn
 by CRAVE.
 0622h                                -11-                           01/11/90

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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  carclno-
genlclty 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  1s presented  1n  Chapter  7  of  Risk
Assessment  Guidance  for  Superfund:  Human Health  Evaluation Manual Part  A.
The chemicals  Included  1n 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 A1r  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  Refer-
ences  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                                -12-                              12/07/89

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Table A: Subchronlc and Chronic ToxIcUy (other than Carc1nogen1c1ty)
    The RfD  Is an  estimate  (with uncertainty  spanning perhaps an  order  of
magnitude) of  the dally exposure  to  the human population  (Including  sensi-
tive subgroups) that  Is  likely to be without  an  appreciable  risk  of delete-
rious effects  during  a portion of the  lifetime,  In  the case  of a  subchronlc
RfO  (designated  "RfD " In Table  A and  formerly  called AIS),  or  during  the
lifetime,   1n  the  case of a  chronic RfO  (designated  "RfO"  In Table A  and
formerly  called  AIC).  The RfD values  are listed  1n  Table A  In  the  column
under "Reference  Dose."   The  RfD  1s derived by dividing the  NOAEL (or LOAEL
1f a suitable  NOAEL Is 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 1s  listed
under "Exposure."  When a NOAEL  or LOAEL  1s  reported  1n  terms of  exposure
concentration and  schedule, the calculated  mg/kg/day  dose  Is  given In  paren-
theses.    The  species  1n  which the  NOAEL  or  LOAEL  was determined and  the
effect  of concern  are also  described,  and the  reference  for   the  study  Is
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  1n  calculating  the  RfD reflects  scientific
judgment  regarding the various types  of  data  used to  estimate RfO values.
An  uncertainty factor  of  10   Is  usually used  to account   for  variations  In
human  sensitivity  when  extrapolating   from  valid  human   studies  Involving

0618h                               -13-                             12/07/89

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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
RfO.   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
uncertainty factor  or  modifying  factor  ranging  from greater  than  0  to less
than or equal  to  10 1s  applied.   The default value for this modifying factor
Is 1.
    A  subchronlc  RfO Is  usually  derived,  If  not  previously derived In health
effects  documents  that  originally addressed the chemical,  for chemicals  for
which  a  chronic  RfD 1s  presented 1n Table A.  The subchronlc  RfD 1s  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.
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  Inhalation  RfD
for bromomethane  reflects  an  uncertainty  factor  of  100  and   a  modifying
factor of 1.

0618h                               -14-                             12/07/89

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    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 Is 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  taken  Into  the determination of  the  effective dose  delivered  to  the
target  organ.    Additional  Information  concerning this  methodology   can  be
found  1n  "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  1n  air
(mg/m3),  although  It   may  be  converted  to  a corresponding   Inhaled  dose
(mg/kg/day)  by   dividing   by  70  kg  (an  assumed  human  body weight)  and
multiplying  by 20 mVday (an  Inhalation  rate).
     RfD  values reported  In 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
                                             o
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).
 0618H                               -15-                             01/11/90

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    RfD values  for  oral  exposure  are reported as  mg/kg/  day.   An oral  RfD
value can  be  converted to a  corresponding concentration In drinking  water,
assuming human  body weight of  70 kg  and water consumption  of 2  t/day,  as
follows:
               mg/8. In water = oral RfD (In mg/kg/day) x 70  kg
                                          2 i/day

    The RfD  Is  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  lUt  cancer and  will refer  to
Table B If additional  Information  concerning  carclnogenlclty  Is available 1n
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
0618h                               -16-                             01/11/90

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the following groups, according  to  the weight of evidence  from  epldemlolog-
1cal studies and animal  studies:

    Group A -  Human Carcinogen  (sufficient evidence  of  cardnogenlclty
               In humans)
    Group B -  Probable  Human  Carcinogen  (Bl  -  limited  evidence  of
               cardnogenlclty  In  humans;  82  -  sufficient evidence  of
               cardnogenlclty  In  animals  with  Inadequate  or  lack  of
               evidence  In humans)
    Group C -  Possible  Human  Carcinogen  (limited  evidence of cardno-
               genlclty  1n animals  and Inadequate or  lack of human  data)
    Group D -  Not Classifiable as  to Human Cardnogenlclty (Inadequate
               or no evidence)
    Group E -  Evidence  of  Noncardnogenlclty for  Humans  (no evidence
               of cardnogenlclty In 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%
confidence  limit) at  low extrapolated  doses that  1s  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 1n fact may be  lower.
    Quantitative  carcinogenic   estimates   listed  In  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
0618h                               -17-                             01/11/90

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Unit risk  estimates for  Inhalation  and oral  exposure can be  calculated  by
dividing the appropriate  slope  factor  by 70  kg and multiplying by the 1nhal-
                  3
atlon  rate (20  m /day)  or  the  water  consumption rate  {2 I/day),  respec-
tively, for risk associated with unit concentration In air or  water.  Hence,
    risk per yg/m3 (air) =
    slope factor (risk per mg/kg/day) x —J— x 20 m3/day x 10~3 (mg/yg)
                                        70 kg
    risk per yg/l (water) =
    slope factor (risk per mg/kg/day) x —!— x 2 J,/day x 10-3 (mg/yg)
                                        • V "a
Quantitative  estimates  of  carcinogenic  risk  are listed under  "slope  factor
or Unit  Risk" 1n Table  B.   Information on the  study and data  set  used for
estimation of  the slope  factor  Is given 1n the other columns of Table B.  In
the  "Exposure" and  "Reference"  columns.  Information  for the  Inhalation route
1s 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  1n Table
B  to Indicate those Instances  1n  which  the  values for Inhalation  or  oral
exposure are based on extrapolation  from another route  of exposure.
    To estimate  risk-specific  concentrations  In air  from  the  unit  risk  In
air  as presented 1n Table  B, the specified level of  risk Is  divided  by the
                                                             3
unit  risk  for air.   Hence  the air  concentration  (1n yg/m ) corresponding
to an upper-bound  Increased lifetime  cancer  risk  of  1x10"   1s  calculated
as follows:
               yg/m3 1n air = 	1x1°"	—-
                              unit risk 1n (yg/m3)~'
0618h                               -18-                             01/11/90

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    To estimate risk-specific concentrations  1n  drinking  water  from the oral
slope  factor  values presented  In Table  B,  the specified  level  of  risk  1s
multiplied  by 70   kg  and  divided  by  the   slope  factor  and  by  2  it/day.
Hence,  the  water  concentration  corresponding  to  an upper-bound  Increased
                            _5
lifetime cancer risk of 1x10   Is calculated as follows:
               mg/i in water = 	IxlO"5 x 70 kg	
                               slope factor In {mg/kg/day)"1 x 2 a/day
 0618h                               -19-                              01/11/90

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                           HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE A: SUBCHRONIC AND CHRONIC TOXICITY (OTHER THAN CARCINOGENICITY)
                                                                   Update:  September. 1989
Compound
Acenaphthene
Acenaphtnylene
Acephate
subchronlc (RfOg)
chronic (RfO)
Acetone
subchronlc (RfOg)
chronic (RfO)
Acetone cyanohydrln
subchronlc (RfOs)
Exposure
Inhalation; Oral


NA; 2 ppm In the diet
for 13 weeks (0.135
mg/kg/day)
NA; 2 ppm 1n the diet
for 13 weeks (0.13S
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/m3)
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/«3 (mg/kg/day)] (mg/kg/day)
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
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 1E-13 NA 1000
liver and kidney
weight, nephro-
toxlclty
rat rat CNS signs; body 1E-1 (4E-2) 7E-2n 100 500
weight, thyroid and
CNS effects
Reference
Inhalation/Oral
U.S. EPA, 1987
U.S. EPA, 1987
U.S. EPA. 1989/
Chevron Chem.
Co.. 1989;
U.S. EPA, 1984;
U.S. EPA. 1989
U.S. EPA. 1987/
Chevron Chem.
Co., 1989;
U.S. EPA, 1984;
U.S. EPA, 1989
U.S. EPA, 1988/
U.S. EPA,
1986a,b, 1988
U.S. EPA, 1988/
U.S. EPA,
1986a,b. 1988
Blank and Thake.
1984; U.S. EPA,
1988/Howard and
Hanzal, 1955;
U.S. EPA,
1985a,b, 1988
0059h
                                                                             A-l
01/11/90

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                          HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE A: SUBCHRONIC AND CHRONIC TOXICITY (OTHER THAN CARCINOGENICITY)
                                                                  Update:  September, 1989
Exposure
Compound
Inhalation
; Oral
Species
Inhalation Oral
Effect of
Inhalation
Concern
; Oral

Reference
Inhalation
[mg/m3 (nig/kg/day)]
Dose
Oral
(mg/kg/day)
Uncertainty
Inhalation
Factor
Oral
Reference
Inhalation/Oral
  chronic  (RfO)
10.1 ppm (35.2 mg/m3)
6 hours/day, 5 days/week
for 14 weeks (4.0 mg/kgX
day); 10.8 mg CN/kg/day
for 104 weeks from diet
treated with HCN
rat        rat      CNS signs;  body
                    weight,  thyroid and
                    CNS effects
U-l (4E-2)
7E-2n        100       500    Blank and Thake,
                              1984; U.S. EPA.
                              1988/Howard and
                              Hanzal, 1955;
                              U.S. EPA,
                              1985a,b, 1988
Acetonltrlle
  subchronlc (RfD$)
Acetophenone
  subchronlc (RfD$)
100 ppm (168 mg/m3)
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)
  chronic (RfD)
                        hours/day, 65/92 days
                        (19.3 mg/kg/day)
0.007 mg/m3 contin-
uously  for 70 days
(0.0045 mg/kg/day);
10,000  ppm diet  (84SO
ppm, correcting  for
volatilization)  for  17
weeks  (423 mg/kg/day)

0.007  mg/m3 contin-
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)
mouse      mouse    elevated relative
                    liver weight;
                    elevated relative
                    liver weight
  chronic (RfO)         100 ppm (168 mg/m3)        mouse
                        6 hours/day, 65/92 days
                        (39.0 mg/kg/day);  100
                        ppm (168 mg/m3) 6
                                     mouse    decreased RBC
                                              counts and hemato-
                                              crH and hepatic
                                              lesions; decreased
                                              RBC counts and
                                              hematocrlt and
                                              hepatic lesions
rat        rat      congestion of
                    cardiac vessels
                    and liver dys-
                    trophy, reduced
                    albumin/globulin
                    ratio; none
                    observed

rat        rat      congestion of
                    cardiac vessels
                    and liver dys-
                    trophy, reduced
                    albumin/globulin
                    ratio; none
                    observed
5E-1 (1E-1)
                                                             6E-2
                               300       300
                                           5E-2 (1E-2)
                                                                                       6E-3°>Z      3000       3000
2E-4(5E-5)
 1E+0
                                                                          100       300
                                                                                             2E-5(5£-6)
                  lE-la       1000      3000
                              Coate, 1983;
                              U.S. EPA, 1987a/
                              Coate, 1983;
                              U.S. EPA, 1987a
                                                Coate,  1983;
                                                U.S.  EPA,  1987a/
                                                Coate,  1983;
                                                U.S.  EPA,
                                                19873,b
Imasheva, 1966;
U.S. EPA, 1987a/
Hagan et al.,
1967; U.S. EPA,
1987b
                               Imasheva. 1966;
                               U.S. EPA, 1987a/
                               Hagan et al.,
                               1967; U.S. EPA.
                               1987b
 0059h
                                                                             A-2
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                           HEALTH tmclS ASSESSMENTS SUMMARY TABLE  A:  SUBCHRONIC AND CHRONIC TOXICITY (OTHER  THAN CARCINOGENICITY)
                                                                  Update:   September,  1989
Compound
Acroleln
subchronlc (RfOs)
chronic (RfO)
Acrylamlde
subchronlc (RfDj)
chronic (RfD)
Acrylic acid
subchronlc (RfDg)
chronic (RfD)
Adlponltrlle
Exposure
Inhalation; Oral
0.4 ppm, 6 hours/day,
5 days/week for 62 days;
NA
0.4 ppm, 6 hours/day.
5 days/week for 62 days;
NA
NA; 0.2 mg/kg/day 1n the
drinking water for 90
days
NA; 0.2 mg/kg/day 1n 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

Species Effect of Concern Reference Dose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
[rag/m3 (mg/kg/day)] (mg/kg/day)
rat NA pulmonary function 1E-3 NO 300 NA
and lung composi-
tion; NA
rat NA pulmonary function 1E-4
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                          HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE A: SUBCHRONIC AND CHRONIC TOXICITV (OTHER THAN CARCINOGENICITY)
                                                                  Update:  September. 1989
Compound
Alachlor
subchronlc (RfOs)
chronic (RfO)
Aldrln
subchronlc (RfDj)
chronic (RfO)
Allldochlor
Ally! alcohol
subchronlc (RfD$)
chronic (RfD)
Exoosure
Inhalation; Oral
NA; 1 mg/kg/day by
gavage for 1 year
NA; 1 mg/kg/day by
gavage for 1 year
NA; 0.5 ppn In diet
for 2 years (0.02S
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.B mg/kg/day)
NA; 50 ppm In the
drinking water for 15
weeks (4.8 mg/kg/day)
Species Effect of Concern Reference Dose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/«3 (mg/kg/day)] (mg/kg/day)
NA dog NA; hemolytlc ND 1E-2 NA 100
anemia, heroo-
slderosU
NA dog NA; hemolytlc ND 1E-28 NA 100
anemia, hemo-
slderosls
NA rat NA; liver lesions NO 3E-5 NA 1000
NA rat NA; liver lesions NO 3E-5a NA 1000
(also see Table
B)
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA rat NA; liver and ND SE-2 NA 100
kidney
NA rat NA; liver and ND 5£-3a NA 1000
kidney
Reference
Inhalation/Oral
U.S. EPA, 1986/
Monsanto
Company, 1984;
U.S. EPA, 1984;
U.S. EPA, 1986
U.S. EPA, 1986/
Monsanto
Company, 1984;
U.S. EPA, 1984;
U.S. EPA. 1986
NA/Fltzhugh,
et al.. 1964;
U.S. EPA, 1985,
1987
NA/Fltzhugh
et al.. 1964;
U.S. EPA, 1985,
1987
U.S. EPA, 1984
U.S. EPA, 1985.
1986/ Carpamlnl
et al., 1978;
U.S. EPA. 1985,
1986
U.S. EPA, 1985.
19B6/ Carpamlnl
et al.. 1978;
U.S. EPA. 1985,
1986
0059h
                                                                             A-4
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                           HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE A: SUBCHRONIC AND CHRONIC TOXICITY (OTHER THAN CARCINOGEN1CITY)
                                                                   Update:  September. 1989
Compound
Exposure
Inhalation; Oral
Ally! chloride (3-chloropropene)
subchronlc (RfD$) occupational; NA
chronU (RfD)
Aluminum
Ametryn
subchronlc (RfDg)
chronic (RfD)
occupational; NA

NA; 10 mg/kg/day, 6
days/week for 13 weeks
by gavage
NA; 10 mg/kg/day. 6
days/week for 13 weeks
by gavage
l-Amlno-2-naphtol and
l-Amlno-2-naphtol hydrochloMde
in-Aro1nophenol
subchronlc (RfOg)
chronic (RfD)
o-Amlnophenol
p-Am1nophenol
4-Amlnopyr Idlne
subchronlc (RfD$)
NA; 1300 ppm In the
diet for 13 weeks (65
mg/kg/day)
NA; 1300 ppm 1n the
diet for 13 weeks (65
mg/kg/day)


NA; 3 ppm 1n diet
for 90 days (0.15
mg/kg/day)
Species Effect of Concern Reference Dose
Inhalation Oral Inhalation; Oral Inhalation Oral
[mg/«3 (mg/kg/day)] (mg/kg/day)
human NA liver; NA ND 2E-3&
human NA liver; NA ND 2E-3°
(also see
Table B)
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA rat NA; liver ND 9E-2
NA rat NA; liver NO 9E-3*
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA rat NA; thyroid and ND 7E-1
body weight
NA rat NA; thyroid and ND 7E-2
body weight
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA rat NA; Increased liver ND 2E-4
(males) and brain
weight (females)
Uncertainty Factor Reference
Inhalation Oral Inhalation/Oral
NA 100 U.S. EPA, 1983/
ACGIH, 1980;
U.S. EPA. 1963
NA 100 U.S. EPA. 1963/
ACGIH, 1980;
U.S. EPA. 1983
U.S. EPA. 1987
NA 100 U.S. EPA. 1987/
Clba-Gelgy,
1961; U.S. EPA,
1984. 1987
NA 1000 U.S. EPA, 1987/
C1ba-Ge1gy,
1961; U.S. EPA,
1984. 1987
U.S. EPA, 1986
NA 100 NA/Re et al..
1984; U.S. EPA,
1985
NA 1000 NA/Re et al.,
1984; U.S. EPA.
1985
U.S. EPA, 1985
U.S. EPA. 1985
NA 1000 U.S. EPA, 1989/
Kohn, 1968; U.S.
EPA, 1980, 1989
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                          HEALTH  EFFECTS  ASSESSMENTS  SUMMARY  lABLt A: SUBCHKON1C  AND  CHRONIC  fOXICITY  (OTHER  THAN  CARC1NOGEN1CITY)
                                                                 Update:   September,  1989
Compound
chronic (RfD)


Ammonia
subchronU (RfO$)




thr«nk (MO)




Anthracene
AntlMony
subchronU (RfOS)




chronic (RfO)




Antimony pentoxlde
subchronU (RfO$)





Cxoosure
Inhalation; Oral
NA; 3 ppm In diet
for 90 days (0.1S
mg/kg/day)

0.36 mg/m3 continuous;
9934 mg/l 1n drinking
water



0.3fc mg/m3 continuous;
34 my/t 1n drinking
water





NA; S ppii Sb fro*
antimony potassium
tartrate In drinking
water, lifetime
(0.35 mg Sb/kg/day)
NA; S ppm Sb from
antimony potassium
tartrate In drinking
water, lifetime
(0.35 mg Sb/kg/day)

NA; S ppm Sb from
antimony potassium
tartrate In drinking
water, lifetime
(0.35 mg Bs/kg/day.
0.46 mg Sb205 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 rat NA; Increased liver ND 2E-5« NA 10.000
(males) and brain
weight (females)

human human odor threshold; 0.36C 34 mg/1 none none
taste threshold In drinking
waterd



human human odor threshold; 0.36C>9 34 mg/t none none
taste threshold In drinking
water*1



DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT

NA rat cancer; reduced N0« 4E-4 NA 1000
llfespan. altered
blood chemistries


NA rat cancer; reduced NO* 4E-4a NA 1000
llfespan. altered
blood chemistries



HA rat cancer; reduced NDe 5E-4f NA 1000
llfespan, altered
blood chemistries



Reference
Inhalation/Oral
U.S. EPA, 1989/
Kohn. 1968; 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/Caapbell
et at.. 1958.
U.S. EPA. 1981.
1987; MHO. 1986
U.S. EPA. 1987

U.S. EPA. 1987/
Schroeder
et al., 1970;
U.S. EPA. 19856

U.S. EPA. 1987/
Schroeder
et al.. 1970;
U.S. EPA.
188Sa,b. 1987

U.S. EPA. 1987/
Schroeder
et al.. 1970;
U.S. LPA. 1985b


0059h
A-6
                                                                                                                                                  09/25/89

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                          HEALTH EFFECTS ASSESSMENTS SWMMARV 1ABIC A:  SUBCHRONIC AND CHROMIC TOXICITV (OTHER THAN CARCINOGENICITY)
                                                                  Update:   September.  1989
Compound
chronic (RfO)





Antimony potassium
tartrate
subchrontc (RfOs)






chronic (RfD)






Antimony tetroxlde
subchronlc (RfDs)




chronic (RfO)




Exposure Soedes
Inhalation; Oral Inhalation Oral
MA; 5 ppm Sb from NA rat
antimony potassium
tartrate 1n drinking
water, lifetime
(0.35 mg Sb/kg/day,
0.46 mg Sb205 kg/day)


NA; 5 ppn Sb from MA rat
antimony potassium
tartrate 1n drinking
water, lifetime
(0.35 mg Sb/kg/day.
0.93 mg SbK tartrate/
kg/day)
NA; 5 ppm Sb from NA rat
antimony potassium
tartrate In drinking
water, lifetime
(0.3S mg Sb/kg/day.
0.93 mg SbK tartrate/
kg/day)

MA; 5 ppm Sb from antl- NA rat
mony potassium tartrate
1n drinking water, life-
time (0.35 mg Sb/kg/day.
0.44 mg Sb204/kg/day)
HA; S ppm Sb from antl NA rat
mony potassium tartrate
In drinking water, life-
time (0.35 mg Sb/kg/day.
0.44 mg Sb204/kg/day)
Effect of Concern Reference Dose Uncertainty Factor
Inhalation; Oral Inhalation Oral Inhalation Oral
[rng/iti3 (mg/kg/day)] (mg/kg/day)
cancer; reduced M0e 5E-4f NA 1000
llfespan, altered
blood chemistries





cancer; reduced N0e 9E-4f NA 1000
llfespan. altered
blood chemistries




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





cancer; reduced N0e 4E-4f NA 1000
llfespan. altered
blood chemistries


cancer; reduced NO* 4E-4f NA 1000
llfespan, altered
blood chemistries


Reference
Inhalation/Oral
U.S. EPA. 1987/
Schroeder
et al.. 1970;
U.S. EPA.
1985a.b. 1987



U.S. EPA, 1987/
Schroeder
et al.. 1970;
U.S. EPA. 1985b,



U.S. EPA. 1987/
Schroeder
et al.. 1970;
U.S. EPA. 1985b.
1987



U.S. EPA, 1987/
Schroeder
et al.. 1970;
U.S. EPA.
1985b
U.S. EPA, 1987/
Schroeder
et al., 1970;
U.S. EPA.
1985a,b. 1987
OOS9h
                                                                             A  7
                                                                                                                                                 09/25/89

-------
                           llfAl III mKIS ASStSSMtNIS SUMMARY TABLE A: SUBCHRONIC AND CHRONIC TOXICITY  (OTHER THAN CARCINOGENICITY)
                                                                   Update:  September, 1969
Compound
Antimony trloxlde
subchronlc (RfOg)
chronic (RfD)
Araffllte
subchronlc (RfDj)
chronic (RfO)
Arsenic
subchronlc (RfD$)
chronic (RfD)
Atrazlne
subchronlc (RfO$)
chronic (RfD)
Exposure
Inhalation; Oral
NA; 5 ppm Sb from
antimony potassium
tartrate In drinking
water, lifetime
(0.35 mg Sb/kg/day,
0.42 mg Sb203/kg/day)
NA; 5 ppm Sb from
antimony potassium
tartrate In drinking
water, lifetime
(0.35 mg Sb/kg/day,
0.42 mg Sb203/kg/day)
NA; 500 ppm In diet
for 52 weeks (12.5
mg/kg/day)
NA; 100 ppm In
diet for 104 weeks
(5 mg/kg/day)
NA; 1 ng/kg/day
NA; 1 yg/kg/day
NA; 15 ppm 1n the diet
for 52 weeks (0.5
mg/kg/day)
NA; 15 ppm In the diet
for 52 weeks (0.5
mg/kg/day)
Species Effect of Concern
Inhalation Oral Inhalation; Oral
NA rat cancer; reduced
llfespan, altered
blood chemistries
NA rat cancer; reduced
Ufespan, altered
blood chemistries
NA dog NA; degenerative
liver effect
NA rat NA; Increased
liver weight
(also see Table B)
NA human NA; keratosls and
hyper pigmentation
NA human cancer; keratosls
and hyperplgmenta-
tlon (also see
Table 8)
NA dog NA; cardiac
effects
NA dog NA; cardiac
effects
Reference Dose Uncertainty Factor
Inhalation Oral Inhalation Oral
[rog/m3 (mg/kg/day)] (mg/kg/day)
NDe 4E-4f NA 1000
NDC 4E-4* NA 1000
NO 1E-1 NA 100
NO SE-2 NA 100
NO 1E-3 NA 1
NO IE -39 NA 1
NO 5E-3 NA 100
ND 5E-3a NA 100
Reference
Inhalation/Oral
U.S. EPA, 1987/
Schroeder
et a!.. 1910;
U.S. EPA, 1985b
U.S. EPA, 1987/
Schroeder
et al.. 1970;
U.S. EPA,
1985a,b, 1987
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, 1988/
C1ba-Ge1gy.
1987; U.S. EPA,
1984, 1988
U.S. EPA, 1988/
C1ba-Ge1gy,
1987; U.S. EPA,
1984. 1988
0059h
A-8
11/24/89

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                            HEALTH  EFFECTS  ASSESSMENTS  SUMMARY  TABLE  A:  SUBCHRONIC  AND  CHRONIC  TOXICITY  (OTHER THAN  CARCINOGENICITY)
                                                                   Update:  September,  1989
Compound
Barium
subchronlc (RfOs)






chronic (RfD)






Benefln
subchronlc (RfOs)



chronic (RfD)



Ben/al chloride
Benzaldehyde
subchronlc (RfD$)



Exposure
Inhalation; Oral
1.15 mg BaC03/n>3
(0.80 mg Ba/m3) 4
hours/day for 4 months
(0.14 mg Ba/kg/day);
100 ppm Ba from BaClj
(5.1 mg Ba/kg/day) tn
drinking water for 4
<16 months
1.15 mg BaC03/m3
(0.80 mg/Ba/m3} 4
hours/day for 4 months
(0.14 mg Ba/kg/day);
100 ppm Ba from BaCl?
(5.1 rag Ba/kg/day) In
drinking water for
<16 months

NA; 25 mg/kg/day 1n the
diet for 1 year


NA; 25 mg/kg/day In the
diet for 1 year




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

Species Effect of Concern Reference Dose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
tmg/m3 (rag/kg/day)] (nig/kg/day)
rat rat fetotoxklty; 5E-3 (1E-3)D|> 5E-2 100 TOO
Increased blood
pressure





rat rat fetotoxUUy; 5E-4 (1E-4)Db 5E-2* 1000 100
Increased blood
pressure






NA dog NA; hematologkal NO 3E-1 NA 100
effects


NA dog NA; hematologkal ND 3E-la NA 100
effects


DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT

NA rat NA; kidney, ND 1E+0 NA 100
forestomach


Reference
Inhalation/Oral
Tarasenko et
al., 1977;
U.S. EPA, 1984/
Perry et al.,
1983; U.S. EPA,
1985b


Tarasenko et
al., 1977;
U.S. EPA, 1984/
Perry et al.,
1983; U.S. EPA.
1984, 1985a,b



U.S. EPA. 1985/
E11 Lilly Co..
1972; U.S. EPA,
1984. 1985
U.S. EPA, 1985/
Ell Lilly Co..
1972; U.S. EPA,
1984, 1985
U.S. EPA, 1985

U.S. EPA, 1987/
Kluwe et al .,
1983; U.S. EPA,
1985. 1987
0059h
                                                                             A-9
11/24/89

-------
                          HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE A: SUBCHRONIC AND CHRONIC TOXICITY (OTHER THAN CARCINQGEN1CITY)
                                                                  Update:  September, 19B9
Compound
chronic (RfD)



BenzaTdehyde cyanohydrln
Benzldlne
subchronlc (RfOs)




chronic (RfO)




Benzole acid
subchronlc (RfDj)



chronic (RfD)



Benzyl Alcohol
subchronlc (RfO$)



chronic (RfD)



Beryllium
subchronlc (RfD$)



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

Species Effect of Concern Reference
Inhalation Oral Inhalation; Oral Inhalation
[mg/m3 (mg/kg/day )]
NA rat NA; kidney, NO
forestomach


Dose Uncertainty Factor
Oral Inhalation Oral
(mg/kg/day)
1E-13 NA 1000



DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT

NA; 160 ppm benzldlne
dlhydrochlorlde 1n
drinking water for
33 months
(27.2 mg/kg/day)
NA; 160 ppm benzldlne
dlhydrochlorlde 1n
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)

NA; 5 ppm 1n drinking
water for lifetime
(0.54 mg/kg/day)


NA mouse NA; brain cell NO
and liver cell
changes


NA mouse NA; brain cell NO
and liver cell
changes (also
see Table B)


NA human NA; Irritation, NO
malaise


NA human NA; Irritation, NO
malaise



NA rat NA; decrease In NO
body weight


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


NA rat NA; none observed ND




3E-3 NA 1000




3E-3a NA 1000





4E»0 NA 1



4E+Oa NA 1




1EfO NA 1000



3E-1 NA 1000




5E-3 NA 100



Reference
Inhalation/Oral
U.S. EPA, 1987/
Kluwe et al.,
1983; U.S. EPA,
1985, 1987
U.S. EPA, 1988

U.S. EPA, 1987a/
LUtlefleld
et al., 1983;
U.S. EPA, 1987b

U.S. EPA, 1987a/
Llttlefleld
et al., 1983;
U.S. EPA, 1987b


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

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

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

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


U.S. EPA, 1987/
Schroeder and
MHchener, 1975;
U.S. EPA, 1985
0059h
A-10
11/24/89

-------
                            HEALTH EFFECTS  ASSESSMENTS  SUMMARY TABLE A: SUBCHRONIC AND CHRONIC TOXICITY  (OTHER THAN CARCINOGENICITY)
                                                                   Update:  September, T9B9





1








Compound
chronic (RfO)



J'-Blphenyl
subchronlc (RfDg)



chronic (RfD)



Exposure
Inhalation; Oral
NA; 5 ppm 1n drinking
water for lifetime
(O.S4 mg/kg/day)


NA; 0.1X 1n the diet
for 700 days (50 mg/kg/
day)

NA; 0.1X 1n the diet
for 700 days (50 mg/kg/
day)

Species
Inhalation Oral
NA rat




NA rat



NA rat



Effect of Concern
Inhalation; Oral
NA; none observed
(also see Table B)



NA; kidney
damage


NA; kidney
damage


Reference Dose
Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
NO 5E-3a




NO 5E-2



ND 5E-2a



Uncertainty Factor
Inhalation Oral
NA 100




NA 1000



NA 1000



Reference
Inhalation/Oral
U.S. EPA, 1987/
Schroeder and
MHchener, 1975;
U.S. EPA, 1985

NA/Ambrose
et al., 1960;
U.S. EPA, 1984,
1985
NA/Ambrose
et al., 1960;
U.S. EPA. 1984.
1985
B1s(2-ethylhexyl) phthalate








subchronlc (RfDg)



chronic (RfD)



NA; 0.04X of diet for
1 year (19 mg/kg/day)


NA; 0.04X of diet for
1 year (19 mg/kg/day)


NA guinea
pig


NA guinea
pig


NA; Increased
relative liver
weight

NA; Increased
relative liver
weight (also see
Table B)
ND 2E-2



ND 2E-2a



NA 1000



NA 1000



U.S. EPA. 1987/
Carpenter
et al., 1953;
U.S. fPA, 1986
U.S. EPA. 1987/
Carpenter
et al.. 1953;
U.S. EPA, 1986
Blsphenol A








subchronlc (RfOg)



chronk (RfO)



NA; 0-1000 ppm for
18 weeks. 2 generations
(NOAEL 750 ppm =
62 mg/kg/day)
NA; 0. 1,000, 2,000 ppm
(1000 ppm = 50 mg/kg/day)


NA rat



NA rat



NA; reduced body
weight


NA; reduced body
weight


ND 6E-1



ND 5E-2a



NA 100



NA 1,000



U.S. EPA. 1988a/
U.S. EPA. 1984c.
1988a

U.S. EPA. 1988a/
NTP. 1982;
U.S. EPA,
1988
Boron




subchronlc (RfD$)



NA; 350 ppm In diet
(8.75 mg/kg/day) for
2 years

NA dog



NA; tesMcular
lesions


ND 9E-2



NA 100



U.S. EPA. 1987/
Heir and
Fisher. 1972;
U.S. EPA. 1987
0059h
                                                                             A-ll
11/24/89

-------
                           HIAITH  UKC1S ASSESSMIN1S SUMMARY TABLE A: SUBCHRON1C AND CHRONIC TOX1C11Y (OTHER 1HAN CARClNOGtNlCHY)
                                                                  Update:  September. 1989
Compound
chronic (RfD)
Exposure
Inhalation; Oral
NA; 350 ppm In diet
(8.75 mg/kg/day) for
2 years
Bromlnated d1benzo-p-d1ox1ns
and dlbenzofurans
Bromoacetone
Bromochloroethane


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; testlcular NO 9E-2J NA 100
lesions
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
(also see Table B)
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
Reference
Inhalation/Oral
U.S. EPA, 19B7/
Heir and
Fisher, 1972;
U.S. EPA, 1987
U.S. EPA,
19B5a,b, 1986
U.S. EPA, 1986
U.S. EPA, 1985
Bromodlchloromethane
  subchronlc (RfD$)
  chronic (RfO)
Bromoform
  subchronlc (RfDs)
  chronic (RfD)
NA; 25 mg/day by gavage   NA
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
NA; 25 mg/kg by gavage    NA
5 days/week for 13 weeks
(17.9 mg/kg/day)
NA; 25 mg/kg by gavage    NA
5 days/week for 13 weeks
(17.9 mg/kg/day)
           mouse    NA;  renal  cytomegaly   NO
                                                            mouse
           rat
                                     rat
NA, renal cytomegaly   NO
(also see Table B)
NA; liver effects
                                                                     NO
                    NA; liver effects      NO
                    (also see Table B)
2E-2          NA      1000    U.S.  EPA,  1987a/
                              NTP,  1986/
                              U.S.  EPA,  1987b

2E-2*         NA      1000    U.S.  EPA,  1987a/
                              NTP,  1986;
                              U.S.  EPA,  1987b
2E-1          NA       100    U.S.  EPA,  1987a/
                              NTP.  1988;
                              U.S.  EPA,  1987b.
                              1989

2E-2a         NA      1000    U.S.  EPA,  1987a/
                              NTP.  1988;
                              U.S.  EPA.  19B7b.
                              1989
subchronlc (RfD$)
26.6 ppm (103 mg/m3) rabbit rat
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)
neurotocxlclty; 6E-2
hyperplasla
of forestomach
epithelium
1E-2 300 100 Russo et al.,
1984/Danse et
al., 1984;
U.S. EPA, 1987
 0059h
                                                                             A-12
                                                                                                                                                  12/01/89

-------
                           HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE  A:  SUBCHRONIC  AND  CHRONIC  TOXICITY  (OTHER  THAN  CARC1NOGENICITY)
                                                                  Update:   September.  1989
Compound
chronic (RfD)
4 Bromophenyl phenyl
Bromophos
subchrontc (RfOg)
chronic (RfD)
Bromoxynll
subchronk (RfOs)
chronic (RfD)
Bromoxynll octanoate
subchronk (RfDs)
chronic (RfO)
Exposure
Inhalation; Oral
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 1n 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)
NA; 100 ppm In the diet
for 2 years (5 mg/kg/
day)
NA; 100 ppm 1n the diet
for 2 years (5 mg/kg/
day)
Species
Inhalation Oral
rabbit rat
DATA
NA rat
NA rat
NA rat
NA rat
NA rat
NA rat
Effect of Concern Reference Dose Uncertainty factor
Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/ffl3 (mg/kg/day)] (mg/kg/day)
neurotoxlclty; 6E-2J lE-3a 3000 1000
hyperplasla of
forestomach
epithelium
INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA; depression NO 5E-2 NA 100
of plasma and
liver cholln-
esterase
NA; depression ND 5E-3 NA 1000
of plasma and
liver cholln-
esterase (also see
Table B)
NA; no adverse ND 2E-2 NA 300
effects
NA; no adverse NO 2E-2a NA 300
effects
NA; no adverse ND 2E-2 NA 300
effects
NA; no adverse ND 2E-2a NA 300
effects
Reference
Inhalation/Oral
Russo et al..
1984/Danse
et al., 1984;
U.S. EPA, 1986a.
1987, 1988
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. 1987/
Union Carbide.
1982; U.S. EPA,
1984. 1987
U.S. EPA. 1987/
Union Carbide,
1982; U.S. EPA.
1984, 1987
U.S. EPA. 1987/
Union Carbide.
1982; U.S. EPA,
1984, 1987
U.S. EPA, 1987/
Union Carbide,
1982; U.S. EPA,
1984. 1987
0059h
A-13
                                                                     12/01/89

-------
                          HtALTH EFFECTS ASSESSMENTS SUMMARY TABLE A: SUBCHRONIC AND CHRONIC TOX1C1TY (OTHER THAN CARCINOGfNIC1TY)
                                                                  Update:  September. 1989
Compound
Busan 7?
Busan 90
1-Butanol
Subchronlc (RfDg)
chronic (RfD)
Butylate
subchronlc (RfDj)
chronic (RfD)
Butyl benzyl phthalate
subchronlc (RfD$)
chronic (RfD)
t-Butylchlorlde
Butyrolactone, gamma
Cacodyllc acid
subchronlc (RfOs)
Exposure
Inhalation; Oral


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; 0.28X of diet
for 26 weeks (159
mg/kg/day)
NA; 0.26* of diet
for 26 weeks (159
mg/kg/day)


NA; 184 mg/kg cacodyllc
acid In diet for 90 days
(9.2 mg/kg/day)
Species
Inhalation Oral
DATA
DATA
NA rat
NA rat
NA dog
NA dog
NA rat
NA rat
DATA
DATA
NA rat
Effect of Concern Reference Dose Uncertainty Factor
Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA; effects NO 1E*0 NO 100
on erythrocyte
NA; effects NO 1E-1 ND 1000
on erythrocyte
NA; liver ND 5E-2 NA 100
effects
NA; liver ND 5E-2* NA 100
effects
NA; effects on body ND 2E*0 NA 100
weight gain, testes.
IWer, kidney
NA; effects on body NO 2E-la NA 1000
weight gain, testes,
liver, kidney
(also see Table B)u
INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA; none NA 3E-2 NA 300
Reference
Inhalation/Oral
U.S. EPA, 1984
U.S. EPA, 1984
U.S. EPA. 1989/
U.S. EPA. 1986.
1989
U.S. EPA, 19B9/
U.S. EPA. 1986.
1989
U.S. EPA. 1984/
Stauffer Chem.
Co.. 1987; U.S.
EPA, 1984, 1989
U.S. EPA, 1984/
Stauffer Chem.
Co.. 1987; U.S.
EPA. 1984. 1989
U.S. EPA, 1987
1989/NTP, 1985;
U.S. EPA. 1986,
1987, 1989
U.S. EPA. 1987
1989/NTP, 1985;
U.S. EPA, 1986,
1987. 1989
U.S. EPA, 1988/
U.S. EPA. 1988
U.S. EPA, 1984
U.S. EPA. 1989/
Nees, 1968;
U.S. EPA, 1989
i9/m /no
0059h

-------
                            HEALTH  EFFECTS  ASSESSMENTS  SUMMARY TABLE A: SUBCHRONIC AND CHRONIC TOXICITY  (OTHER THAN CARCINOGENICITY)
                                                                   Update:  September,  1989
Compound
chronic (RfD)


Cadmium
subchronlc (RfOj)

chronic (RfD)

Caprolactara
subchronlc (RfD$)



chronic (RfD)



Captafol
subchronlc (RfDg)




chronic (RfD)




Captan
subchronlc (RfD$)






Exposure Species
Inhalation; Oral Inhalation Oral
NA; 1B4 mg/kg cacodyllc NA rat
acid In diet for 90 days
(9.2 ing/kg/day)

NA; NA NA NA

NA; NA NA human


NA; 0.1X diet 90 days NA rat
(50 mg/kg/day)


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 1n NA rats
the diet (multi-
generation)




Effect of Concern Reference Dose Uncertainty Factor
Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
NA; none NA 3E-3 NA 3000



cancer; NA NO NDn NA NA

cancer (see Table B); ND 1E-3 (food)a>^NA 10
renal damage 5E-4 (water)

NA; renal effects ND 5E-1 NA 100



NA; reduced body ND 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





Reference
Inhalation/Oral
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

U.S. EPA, 1988a/
Powers et al.,
1984; U.S. EPA.
1988a
U.S. EPA, 1988a/
Serota et al..
1984; U.S. EPA,
1988a.b

U.S. EPA. 1987/
Ortho-Chevron
Chemical Co.,
1985; U.S. EPA.
1984, 1987
U.S. EPA, 19B7/
Ortho-Chevron
Chemical Co.,
1985; U.S. EPA,
1984. 1987

U.S. EPA, 1989/
Stauffer Chem.
Co.. 1982;
Chevron Chem.
Co., 1982;
U.S. EPA, 1984,
1989
0059h
                                                                             A-15
11/24/89

-------
                          HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE A: SUBCHRONIC AND CHRONIC TOXICITY (OTHER THAN CARCINOGENICITY)
                                                                  Update:  September, 1989
Compound
chronic (RfD)
Carbaryl
subchronlc (RfD;)
chronic (RfD)
Carbofuran
subchronlc (RfOj)
chronic (RfD)
Carbon tetrachloHde
subchronlc (RfOg)
chronic (RfO)
Exposure Species
Inhalation; Oral Inhalation Oral
NA; 12.5 mg/kg/day In NA rats
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)
NA; 0.5 mg/kg/day In NA dog
the diet for 1 year
NA; 0.5 mg/kg/day In NA dog
the diet for 1 year
NA; 1 mg/day, 5 days/ NA rat
week for 12 weeks
(0.71 mg/kg/day)
NA; 1 mg/day, 5 days/ NA rat
week for 12 weeks
(0.71 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; decreased ND 1E-13 NA 100
body weight
NA; kidney and ND 1E-1 NA 100
and liver
toxlclty
NA; kidney and ND 1E-1» NA 100
and liver
toxlclty
NA; hematolog- ND 5E-3 NA 100
leal, testlcular
and uterine
effects
NA; hematolog- ND 5E-3a NA 100
leal, testlcular
and uterine
effects
NA; liver lesions ND 7E-3 NA 100
NA; liver lesions NO 7E 4* NA 1000
(also see Table B)
Reference
Inhalation/Oral
U.S. EPA, 1989/
Stauffer Chem.
Co., 1982;
Chevron Chem.
Co., 1982;
U.S. EPA. 1984,
1989
U.S. EPA, 1985/
Carpenter
et al., 1961;
U.S. EPA, 1984,
1985
U.S. EPA, 1985/
Carpenter
et al.. 1961;
U.S. EPA, 1984,
1985
U.S. EPA, 1987/
FMC Corp., 1983;
U.S. EPA. 1984,
1987
U.S. EPA, 1987/
FMC Corp., 1983;
U.S. EPA. 1984,
1987
U.S. EPA, 1984/
Bruckner
et al. 1986;
U.S. EPA, 1985
U.S. EPA, 1984/
Bruckner
et al.. 1986;
U.S. EPA, 1985
0059h
                                                                             A-16
                                                                                                                                                  11/24/89

-------
                           HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE A: SUBCHRONIC AND CHRONIC TOXICITY (OTHER THAN CARCINOGEN1CITY)
                                                                   Update:  September, 1989
Compound
Chloral
subchronlc (RfOs)
chronic (RfO)
Chlordane
subchronlc (RfO$)
chronic (RfO)
Chloroacetaldehyde
Chloroacetlc add
subchrontc (RfOg)
chronic (RfO)
2-Chloroanlllne
3-Chloroan1l1ne
4-Chloroan1l1ne
(p-ChloroanWne)
subchronlc (RfOg)
Exposure
Inhalation; Oral
NA; 15.7 mg/kg/day
from drinking water
NA; 15.7 mg/kg/day
from drinking water
NA; 1 ppm In diet for
130 weeks (0.045
mg/kg/day)
NA; 1 ppm In diet for
130 weeks (0.045
mg/kg/day)

NA; 30 mg/kg, 5 days/
week for 13 weeks
(21.4 mg/kg/day)
NA; 30 mg/kg. 5 days/
week for 13 weeks
(21.4 mg/kg/day)


NA; 250 ppm 1n diet
for 78 weeks (12.5
mg/kg/day)
Soeclef Effect of Concern Reference Dose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/ffl3 (mg/kg/day)] (mg/kg/day)
NA mouse NA; hepatotoxlclty ND 2E-2 NA 1000
NA mouse NA; hepatotoxlclty ND 2E-3a NA 10,000
(also see Table B)
NA rat NA; liver necrosis ND 6E-5 NA 1000
NA rat NA; liver necrosis NO 6E-5a NA 1000
(also see Table B)
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA rat NA; myocarditis ND 2E-2 NA 1000
NA rat NA; myocarditis ND 2E-3 NA 10,000
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT (SEE TABLE B)
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT (SEE TABLE B)
NA rat NA; prollferatlve ND 4E-3 ' NA 3000
lesions of the
spleen
Reference
Inhalation/Oral
U.S. EPA, 1988a/
Sanders
et al., 1982;
U.S. EPA, 1988a
U.S. EPA. 1988a/
Sanders et al .,
1982; U.S. EPA.
1988a, b
U.S. EPA, 1988/
Velslcol
Chemical Corp..
1983; U.S. EPA,
19B9
U.S. EPA, 1988/
Velslcol
Chemical Corp.,
1983; U.S. EPA,
1989
U.S. EPA, 1988
U.S. EPA, 1988/
IRDC, 1982a;
U.S. EPA, 1988
U.S. EPA, 1988/
IRDC, 1982a;
U.S. EPA, 1988
U.S. EPA, 1987
U.S. EPA. 1987
U.S. EPA, 1987a/
NCI, 1979;
U.S. EPA, 1987b
0059h
                                                                             A-17
                                                                                                                                                  11/24/89

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                          HEALTH  EFFECTS ASSESSMENTS  SUMMARY  TABLE  A:  SUBCHRONIC AND  CHRONIC  TOXICITY  (OTHER  THAN CARCINOGENICITY)
                                                                  Update:   September,  1989
Compound
chronic (RfO)
Chlorobenzene
subchronlc (RfOg)
chronic (RfO)
p-Chlorobeniolc acid
subchronlc (RfDj)
chronU (RfD)
Exposure
Inhalation; Oral
NA; 250 ppm 1n diet
for 78 weeks (12.5
mg/kg/day )
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
75 ppm (345 mg/m*)
7 hours/day, 5 days/
week for 120 days
(53 mg/kg/day);
27.3 mg/kg/day by
capsule for 90 days
NA; 0.2X 1n diet for
5 months (173.3
mg/kg/day)
NA; 0.2% In diet for
5 months (173.3
mg/kg/day )
4-Chlorobenzotrlf luorlde
subchronlc (RfOs) NA; 15 mg/kg/day by
gavage dally for 90
days
chronic (RfD)
NA; 15 mg/kg/day by
gavage dally 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; proliferate NO 4E-3« NA 3000
lesions of the
spleen (also
see Table B)
rat dog liver and kidney 2E-1 (5E-2) 2E-1 1000 100
effects; liver and
kidney effects
rat dog liver and kidney 2E-2 (5E-3) 2E-2a 10,000 1000
effects; liver and
kidney effects
(also see Table B)
NA rat NA; none observed ND 2E+0 NA 100
NA rat NA; none observed NO 2E-1 NA 1000
NA rat NA; renal tubular ND 2E-1 NA 100
degeneration
NA rat NA; renal tubular NO 2E-2 NA 1000
degeneration
Reference
Inhalation/Oral
U.S. EPA, 1987a/
NCI, 1979;
U.S. EPA, 1987b
Dllley, 1977;
U.S. EPA, 1984/
Monsanto, 1967;
U.S. EPA, 1985.
1989
Dllley, 1977;
U.S. EPA, 1984/
Monsanto, 1967;
U.S. EPA, 1985,
1989
U.S. EPA, 19B7/
Kleckebusch
et al.. 1960;
U.S. EPA, 1987
U.S. EPA, 19B7/
Kleckebusch
et al.. 1960;
U.S. EPA, 1987
U.S. EPA, 1988/
Hooker Chemical
Co., 1981;
U.S. EPA, 1988
U.S. EPA. 1988/
Hooker Chemical
Co.. 1981;
U.S. EPA. 1988
0059h
                                                                             A-18
                                                                                                                                                  11/24/89

-------
                           HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE  A:  SUBCHRONIC  AND  CHRONIC  TOXICITY  (OTHER  THAN CARCINOGENICITY)
                                                                  Update:   September.  19B9
Compound
2-Chloro-l ,3-butadlene
(Chloroprene)
subchronlc (RfD$)
chronk (RfO)
1-Chlorobutane
subchronlc (RfD)s
chronic (RfO)
2-Chlorobutane
Chlorocyclopentadlene
Chi or odlbromome thane
subchronlc (RfDj)
chronic (RfO)
p-Chloro-m-cresol
subchronlc (RfOj)
chronic (RfD)
Exposure
Inhalation; Oral
10 ppm, 6 hours/day,
5 days/week for 2 years
(36 mg/m3); NA
10 ppm, 6 hours/day,
5 days/week for 2 years
(36 rog/m3); NA
NA; 120 mg/kg. 5 days/
week for 13 weeks by
gavage (86 mg/kg/day)
NA; 60 mg/kg. 5 days/
week for 103 weeks by
gavage (43 mg/kg/day)


NA; 30 mg/kg 5 days/week
for 13 weeks (21.4
mg/kg/day)
NA; 30 mg/kg 5 days/week
for 13 weeks (21.4
mg/kg/day)
NA; 200 mg/kg/day for
28 days
NA; 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)
rat NA alopecia, retarded 1E-1J4E-2) 2E-2M 100 NA
growth; NA
rat NA alopecia, retarded lE-1(4E-2) 2E-2b><> 100 NA
growth; NA
NA rat NA; CNS and ND 9E-1 NA 100
hematopoletk
effects
NA rat NA; mortality. ND 4E-1 NA 100
CNS and hemato-
logk effects
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA NA NA; liver lesions ND 2E-1 NA 100
NA rat NA; liver lesions NO 2E-2« NA 1000
(also see Table B)
NA rat NA; decrease In ND 2E+0 NA 100
weight gain
NA NA NA; NA ND ND NA NA
Reference
Inhalation/Oral
Du Pont, 1985;
U.S. EPA,
1989a,b/ U.S.
EPA, 1989a,b
Du Pont. 1985;
U.S. EPA,
1989a.b/U.S.
EPA. 1989a.b
U.S. EPA, 1988/
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, 1987a/
NTP, 1985;
U.S. EPA. 1987b
U.S. EPA, 1987a/
NTP. 1985;
U.S. EPA, 1987b
U.S. EPA, 1988/
Madsen et al. ,
1986; U.S. EPA,
1988
U.S. EPA, 1988/
U.S. EPA, 1988
0059h
                                                                            A-19
71/24/89

-------
                          HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE A: SUBCHRONIC AND CHRONIC TOXICITY (OTHER THAN CARCINOQENICITY)
                                                                  Update:  September, 1989
Compound
Chloroform
subchronlc (RfOg)
chronic (RfO)
m-Chloronltrobenzene
Chlorophenol, 3- and
2-Chlorophenol
subchronlc (RfD$)
chronic (RfD)
2-Chloropropane
subchronlc (RfDj)
chronic (RfO)
Exposure
Inhalation; Oral
NA; 15 mg/kg, 6 days/
week for 7.5 years
(12.9 mg/kg/day)
HA; 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
Utter (5 mg/kg/day)
NA; 50 ppm In drinking
water from weaning
through birth of first
litter (5 mg/kg/day)
250 ppm (803 mg/fl>3),
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
Species Effect of Concern Reference Oose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
NA dog NA; liver lesions ND 1E-2 NA 1000
NA dog NA; liver lesions NO lE-2a NA 1000
(also see Table B)
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA rat NA; reproductive NO 5E-3 NA 1000
effects
NA rat NA; reproductive NO 5E-3* NA 1000
effects
rat NA liver effects; NA 3E+0 (9E-1) ND 100 NA
rat NA liver effects; NA 3E-1 (9E-2) ND 1000 NA
Reference
Inhalation/Oral
U.S. EPA, 1988/
Hey wood et al.,
1979; U.S. EPA,
1985
U.S. EPA, 1988/
Hey wood et al.,
1979; U.S. EPA,
1985
U.S. EPA, 1985
U.S. EPA, 1987
U.S. EPA.
1987a,b/Exon and
Koeller, 1982;
U.S. EPA,
1987a,b
U.S. EPA,
1987a,b/Exon and
Koeller. 1982;
U.S. EPA,
1987a,b. 1988
Gage, 1970;
U.S. EPA, 1987/
U.S. EPA, 1987
Gage, 1970;
U.S. EPA, 1987/
U.S. EPA. 1987
0059h
                                                                             A-20
                                                                                                                                                  11/24/89

-------
                           HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE A: SUBCHRONIC AND CHRONIC TOXICITY (OTHER THAN CARCINOGENICITY)
                                                                   Update:  September. 1989
Compound
3-Chloropropene (see
Chlorotoluenes
ChlorpyMfos
subchronlc (RfDj)
chronic (RfD)
Chlorpyrlfos-methyl
subchronlc (RfD$)
chronic (RfO)
Chlorthalonll
subchronlc (RfOj)
chronic (RfO)
Chlorthlophos
subchronlc (RfDs)
Exposure
Inhalation; Oral
Allyl chloride)

NA; 0.03 nig/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
1n dogs
NA; 3-generatlon study
In rats, 2-year study
In dogs
NA; 60 ppm In the diet
for 2 years (1.5 mg/kg/
day)
NA; 60 ppm 1n the diet
for 2 years (1.5 mg/kg/
day)
NA; 1.6 ppm 1n the diet
for 2 years (0.08 mg/
kg/day)
Species
Inhalation Oral

DATA
NA human
NA human
NA rats,
dogs
NA rats,
dogs
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)

INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA; decreased ND 3E-3 NA 10
plasma cholln-
esterase
NA; decreased NO 3E-3a NA 10
plasma cholln-
esterase
NA; reduced NO 1E-2 NA 100
fertility In
rats, liver
effects In dogs
NA; reduced ND IE -29 NA 100
fertility In
rats, liver
effects In dogs
NA; kidney ND l.SE-2 NA 100
lesions
NA; kidney ND 1.5E-2* NA 100
lesions
(also see Table B)
NA; no effect ND BE-4 NA 100
on erthrocyte
chollnesterase
Reference
Inhalation/Oral

U.S. EPA, 1985
U.S. EPA, 1986/
Dow Chemical
Co., 1972; U.S.
EPA. 19B4, 19B6
U.S. EPA, 1986/
Dow Chemical
Co., 1972; U.S.
EPA, 1984, 1986
U.S. EPA, 1984/
U.S. EPA, 1984
U.S. EPA, 1984/
U.S. EPA, 1984
U.S. EPA, 1986/
Diamond Shamrock
Chem. Co., 1970;
U.S. EPA, 1986
U.S. EPA, 1986/
Diamond Shamrock
Chem. Co., 1970;
U.S. EPA. 1986
U.S. EPA. 19B6/
Worthing and
Walker, 1983;
U.S. EPA. 1986
0059h
                                                                             A-21
11/24/89

-------
                          HEALTH  EFFECTS ASSESSMENTS  SUMMARY TABLE A: SURCHRONIC AND CHRONIC  TOX1CITY  (OTHER THAN CARCINOGENICITY)
                                                                 Update:   September.  1989
Compound
chronic (RfO)



Chromium (III)
subchronlc (RfDs)


chronic (RfO)



Chromium (VI)
subchronlc (RfO$)


chronic (RfO)

Chrysene
Copper
subthronU (RfD$)
chronic (RfO)

Exposure
Inhalation; Oral
NA; 1.6 ppm In the diet
for 2 years (0.08 mg/
kg/day)


NA; 5* Cr203 In diet
5 days/week for 90 days
(MOO mg Cr/kg/day)

NA; 5* Cr203 In diet
5 days/week for 600
feedings (1468 mg
Cr/kg/day)


NA; 25 ppm Cr VI In
drinking water for 1
year (2.4 mg/kg/day)
NA; 25 ppm Cr VI In
drinking water for 1
year (2.4 mg/kg/day)



NA; 5.3 mg. single
dose
MA; NA

Species Effect of Concern Reference Oose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
(mg/m3 (mg/kg/day)] (mg/kg/day)
NA rat NA; no effect ND 8E-4 NA 100
on erthrocyte
chollnesterase


NA rat NA; hepatotoxklty ND 1E+1 NA TOO


NA rat NA; hepatotoxlclty NO U+Oa NA 1000




HA rat cancer; not defined NO 2E-2 NA 100


NA rat cancer (see NO 5E-3« NA 500
Table B); not
defined

DATA INADEQUATE fOR QUANTITATIVE RISK ASSESSMENT

NA human NA; local Gl ND 1.3mg/lk NA MA
Irritation
NA human NA; local Gl HO 1.3mg/tk HA MA
Irritation"
Reference
Inhalation/Oral
U.S. EPA. 1986/
Worthing and
Walker. 1983;
U.S. EPA. 1986

U.S. EPA. 19B4/
Ivankovlc and
Preussman. 1975;
U.S. IPA. 1984
U.S. EPA. 1984/
IvankovU and
Preussman. 1975;
U.S. EPA, 1984.
1985

U.S. EPA, 1984/
NacKenzle
et al., 1958;
U.S. EPA. 1984
U.S. EPA, 1984/
MacKenzle
et al.. 1958;
U.S. EPA. 1984,
1986
U.S. EPA. 1984

U.S. EPA. 1984/
U.S. tPA. 1987
U.S. EPA. 1*84/
U.S. EPA. W7
0059h
                                                                             A ??
                                                                                                                                                  09/25/89

-------
                          HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE A:  SUBCHKONIC AND CHHONIC TOXICITY (OTHER THAN CARCINOGENICITY)
                                                                  Update:  September, 1909
Exoosure
Compound Inhalation; Oral
m-Cresol
subchronk (RfDs) NA; 50 mg/kg/day
for 90 days






chronic (RfO) HA; SO rog/kg/day
for 90 days






o-Cresol
subchronlc (RfOs) NA; SO Mg/kg/day
for 90 days






chronic (RfO) NA; SO n»y/kg/day
for 90 days






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

NA rat NA; reduced body NO SE-1 NA 100
weight gain, neuro-
toxklty





NA rat NA; reduced body NO SE-2* NA 1000
weight gain, neuro-
toxklty






NA rat NA; reduced body NO SE-1 NA 100
weight gain, neuro-
XoxkHy





NA rat NA; reduced body NO 5E-2a NA 1000
weight gain, ni.-uro-
toxklty





Reference
Inhalation/Oral

U.S. EPA. 1984,
1985/Mkro-
biological
Associates,
1986; ToxkHy
Research Labora-
tories. 1987;
U.S. EPA. 1987
U.S. EPA. 1984,
1985/Mkro-
blologkal
Associates.
1986; Toxklty
Research Labora-
tories. 1987;
U.S. EPA, 1987

U.S. EPA. 1984.
1985/HUro-
bloloqkal
Associates.
1986; Toxicity
Research Labora-
tories. 1987;
U.S. EPA. 1987
U.S. EPA. 1984.
1985/Hkro-
blologkal
Associates,
1986; loxklty
Research Labora-
tories. 1987;
U.S. EPA. 1987
OOS9h
                                                                             A-23
09/25/89

-------
                           HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE  A:  SUBCHRONIC  AND CHROMIC  TOX1C1TV  (OTHER THAN  CARCINOGENICW)
                                                                  Update:   September.  19B9
Compound
p-Cresol
subchronlc (RfDj)







chronic (RfD)







Exposure
Inhalation; Oral

NA; 50 mg/kg/day
for 90 days






NA; SO mg/kg/day
for 90 days






Species Effect of Concern Reference Dose Uncertainty factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
lmg/m3 (mg/kg/day)) (mg/kg/day)

NA rat NA; reduced body ND SE-1 NA 100
weight gain, neuro-
toxUUy





NA rat NA; reduced body NO 5E-2a NA 1000
weight gain, neuro-
toxlclty





Reference
Inhalation/Oral

U.S. EPA. 1984,
1985/Mlcro-
blologlcal
Associates.
1986; Toxlclty
Research Labora-
tories, T9B7;
U.S. EPA. 1967
U.S. EPA. 1984,
1985/Mlcro-
blologlcal
Associates,
1986; Toxlclty
Research Labora-
tories. 1987;
U.S. EPA, 1987
Cumcne
  subchronlc (RfD$)
  chronic (RfD)
105.1 ppra (517 mg/m3)     rat        rat
for 6 hrs/day. 5
days/wk for 4 weeks;
110 mg/kg/day for
194 days

105.1 ppm (517 mg/m3)     rat        rat
for 6 hrs/day, 5
days/wk for 4 weeks;
110 ing/kg for 194 days
CNS Involvement.       9E-2
nasal Irritation;
renal
CNS Involvement.       9E-3)
nasal Irritation;
renal
4E-1
1000       300
4E-2a      10000      3000
Monsanto Company
1986; U.S. EPA,
1987b/Wolfe.
1956; U.S. EPA,
19876

Monsanto Company
1986; U.S. EPA.
19B7b/Nolf
et al.. 1956;
U.S. EPA, 19B7b
subchronlc (RfDj)
NA; 25 ppm In the diet NA
for 1 year (0.625 g/kg/
day)
dog NA; body weight NO
loss, hemato-
loglc and clin-
ical chemistry
parameters
2E-3 NA 300 U.S. EPA, 1988/
Shell Chem. Co..
1986; U.S. EPA,
19B4. 1968
0059h
                                                     A-24
                                                                                                                                                  10/10/89

-------
                          HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE A:  SUBCHRONIC AND CHRONIC TOX1CITY (OTHER THAN CARCINOGENICITY)
                                                                  Update:   September. 1989
Compound
chronic (RfD)
Cyanide
subchronU (RfOj)
chronic (RfO)
Cycloate
Cyc lohexanol
Cyclohexylamlne
subchronlc (RfD$)
chronic
Cyc 1 open tad lene
subchronU (RfDs)
Exposure
Inhalation; Oral
NA; 25 ppm In the diet
for 1 year (0.625 g/kg/
day)
NA; 10.8 mg/CN/kg/day
for 104 weeks from
diet treated with HCN
NA; 10. B mg CN/kg/day
for 104 weeks from
diet treated with HCN


NA; 600 pp» cyclohexy-
lam1ne*HCl 1n diet
for 90 days (30 mg/kg/
day) cyclohexylamlne)
NA; 600 ppm cyclohexy-
lawlne-HCl \n diet for
2 years (18 mg/kg/day)
cyclohexylamlne
250 ppm (676 mg/ra3)
for 135, 7-hour expo-
sures 1n 194 days
(87.3 mg/kg/day); 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 dog NA; body weight NO 2E-3a NA 300
loss, hemato-
loglc and din
1ca1 chemistry
parameters
NA rat NA; weight loss, NO 2E-2 NA 500
thyroid effects and
myelln degeneration
NA rat NA; weight loss, NO 2E-2* NA 500
thyroid effects and
myelln degeneration1
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
HA rat NA; reduced body HD 3E-1 MA 100
weight
NA rat NA; testlcular NO 2E-la NA 100
effects
rat NA liver and kidney 3E+0 (9E-1) NO 100 NA
lesions; NA
Reference
Inhalation/Oral
U.S. EPA. 1988/
Shell Chen. Co..
1986; U.S. EPA.
1984. 1988
U.S. EPA. 1984/
Howard and
Hanzal. 195S;
U.S. EPA. 1984.
1985
U.S. EPA, 1984/
Howard and
Hanzal, 1955;
U.S. EPA. 1984.
1985
U.S. EPA. 1984
U.S. EPA, 1985
U.S. EPA. 1987a/
Gaunt et al..
1974; U.S. EPA.
1987a
U.S. EPA. 1987a/
Gaunt et al..
1976; U.S. EPA.
1987a.b
Dow. 1987;
U.S. EPA, 19B7/
U.S. EPA. 1987
0059h
A-25
                                                                                                                                                  09/25/89

-------
                          HEALTH EJECTS ASSLSSMtNIS SUHHAKY TABU  A:  MJBCHRONIC AND CHRONIC 10X1CITY (OIHCR THAN CARCINOGEN1CITY)
                                                                  Update:   September. 1989
Compound
Cyclopentadlene
chronic (RfO)

Dacthal (DCPA)
subchronlc (RfOj)




chronk (RfO)



Da Upon (sodium salt)
subthrontc (RfDs)



chronic (RfO)



2. 4 OB
subchronlc (RfDs)



chronic (RfO)



txoosure Species
Inhalation; Oral Inhalation Oral

NA; NA NA NA


NA; 1000 ppm 1n the NA rat
In the diet for 2
years (SO mg/kg/day)


NA. 1000 ppm In the NA rat
In the diet for 2
years (SO mg/kg/day)


NA; IS ng/kg/day In the NA rat
diet for 2 years


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



NA; 6 mg/kg/day In the NA doy
diet for 90 days


NA; 6 mg/kg/day In the NA dog
diet for 90 days


Effect of Concern
Inhalation; Oral

NA; NA


NA; kidney and
adrenal weights



NA; kidney and
adrenal weights



NA; Increased
relative kidney
weight

NA; Increased
relative MUney
weight


NA; Internal
hemorrhage.
mortal Ity

NA; Internal
hemorrhage,
mortality

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

NO NO NA NA U.S. EPA, 1987/
U.S. EPA. 1987

NO 51-1 NA 100 U.S. EPA, 1987/
Diamond Shamrock
Co.. 1963;
U.S. tPA, 1984,
1987
NO 5E-la NA 100 U.S. EPA. 1987/
Diamond Shanrotk
Co.. 1963; U.S.
EPA. 1984. 1987

NO 3E-2 NA 300 U.S. EPA. 1988/
Paynter et al..
1960; U.S. EPA.
1984. 1988
NO 3E-2a NA 300 U.S. EPA. 1988/
Paynter et al. .
1960; U.S. EPA,
1984, 1988

NO 8E-2 NA 100 U.S. EPA. 1985/
Rhodla Inc.,
1969; U.S. EPA.
1984. 1985
NO 8E 3a NA 1000 U.S. EPA. 198S/
Rhodla Inc..
1969; U.S. EPA.
1984. 1985
OOS9h
A-26
09/25/89

-------
                           HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE  A:  SUBCHRONIC AND CHRONIC TOXICITY (OTHER THAN CARCINOGENICITY)
                                                                   Update:   September.  1989
Compound
DOT
subchronlc (RfOj)


chronic (RfD)



Oecabromodlphenyl ether
subchronlc (RfDg)


chronic (RfD)


Decabroraodlphenyl oxide
subchronlc (RfDj)





chronic (RfD)






Exposure Species
Inhalation; Oral Inhalation Oral

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


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


NA; 1.0 mg/kg/day 1n NA rat
the diet for 2 years


NA; 1.0 mg/kg/day 1n NA rat
the diet for 2 years


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





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

NA; liver lesions ND 5E-4 NA 100


NA; liver lesions ND 5E-4a NA 100
(also see Table B)


NA; liver ND 1E-2 NA 100


NA; liver (also see ND lE-2a NA 100
Table B)


NA; liver ND 1E-2 NA 100
enlargement





NA; liver NO lE-2a NA 100
enlargement (also
see Table B)




Reference
Inhalation/Oral

U.S. EPA, 1984/
Laug et al.,
1950; U.S. EPA.
1985
U.S. EPA, 19B4/
Laug et al..
1950; U.S. EPA.
1985. 1988
U.S. EPA. 1985/
Kodba et al..
1975; U.S. EPA.
1983. 1985
U.S. EPA. 1985/
Kodba et al..
1975; U.S. EPA.
1983, 1985
U.S. EPA, 1987/
Kodba et al. ,
1975; Norrls
et al., 1973,
1975; U.S. EPA.
1987; U.S. EPA.
1985
U.S. EPA. 1987/
Kodba et al.,
1975; Norrls
et al., 1973,
1975; U.S. EPA.
1987; U.S. EPA,
1985
0059h
A-27
                                                                     11/24/89

-------
                          HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE A: SUBCHRONIC AND CHRONIC TOXICITY (OTHER THAN CARCINOGENICITY)
                                                                  Update:  September, 1969
Compound
Olazlnon
subchronlc (RfDs)



chronic (RfO)




Olbenzofuran
1,4-Olbromobenzene
subchronlc (RfOj)




chronic (RfO)



Dlbromochloromethane
subchronlc (RfOs)
chronic (RfD)
Exposure Soedes
Inhalation; Oral Inhalation Oral

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

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


DATA

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


NA; 10 mg/kg/day by NA rat
gavage for 45 or 90
days
™* "

NA; 30 mg/kg/day by NA rat
gavage, 5 days/week for
13 weeks (21 mg/kg/day)
NA; 30 mg/kg/day by NA rat
gavage, 5 days/week for
13 weeks (21 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; Inhibition NO 9E-4 NA 100
of plasma chol-
Inesterase
activity
NA; Inhibition NO 9E-4H NA 100
of plasma chol-
Inesterase
activity

INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT

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



NA; liver weight ND 1E-2* NA 1000
and liver enzymes



NA; liver NO 2E-1 NA 100
lesions
NA; liver NO 2E-2a NA 1000
lesions
(also see Table B)
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, 19B7

U.S. EPA, 1986/
Carlson and
Tardlff. 1977;
U.S. EPA, 1984,
1986
U.S. EPA, 1986/
Carlson and
Tardlff, 1977;
U.S. EPA. 1984.
1986
U.S. EPA, 1987/
NTP, 1985;
U.S. EPA, 1985,
1987, 1989
U.S. EPA, 1987/
NTP, 1985;
U.S. EPA, 1985.
1987, 1989
0059h
                                                                             A-28
                                                                                                                                                  11/24/89

-------
                           HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE A: SUBCHRONIC AND CHRONIC TOXICI1Y (OTHER THAN CARCINOGENICITY)
                                                                   Update:  September, 1989
Compound
Dl-n-butyl phthalate
subchronlc (RfD$)


chronic (RfD)



1 ,2-Olchlorobenzene
subchronlc (RfOj)





chronic (RfD)





1 ,3-D1chlorobenzene
1 ,4-D1ch1oroberuene
(p-dlchlorobenzene)
subchronlc (RfDj)



chronic (RfD)



Exposure
Inhalation; Oral
NA; 0.25X of diet
for 52 weeks
(125 mg/kg/day)
NA; 0.25* of diet
for 52 weeks
(125 mg/kg/day)


290 mg/m3 7 hours /day.
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)
290 mg/m3 7 hours/day.
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)
5 hours /day, 5 days/week
for 76 weeks; NA

75 ppra (454.6 mg/ra3)
5 hours/day, 5 days/week
for 76 weeks; 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; mortality NO 1E*0 NA 100


NA rat NA; mortality1 NO lE-la NA 1000




rat rat decreased body 2E*0 (4E-1) 9E-1 100 100
weight gain; liver
effects (also see
Table B)


rat rat decreased body 2E-1 (4E-2) 9E-2a 1000 1000
weight gain;
liver effects
(also see
Table B)

DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT (also see Table B)


rat NA liver and kidney 7E-1 NO 100 NA
effects; NA


rat NA liver and kidney 7E-lJ ND 100 NA
effects (also see
Table B)

Reference
Inhalation/Oral
U.S. EPA, 1987/
Smith. 1953;
U.S. EPA, 1967
U.S. EPA, 1987/
Smith, 1953;
U.S. EPA, 1986
1987

Holllngsworth
et al., 1958;
U.S. EPA, 1987/
NTP. 1985; U.S.
EPA. 1987

Holllngsworth
et al., 1958;
U.S. EPA. 1987/
NTP, 1985; U.S.
EPA. 1987

U.S. EPA, 1987


Rlley et al..
1980; U.S. EPA,
1988/U.S. EPA,
1987
Rlley et al.,
1980; U.S. EPA,
1988/U.S. EPA,
1987
0059h
                                                                             A-29
11/24/89

-------
                          HEALTH  EFFECTS ASSESSMENTS  SUMMARY TABLE A: SUBCHRONIC AND CHRONIC TOXICITY  (OTHER THAN CARCINOGENICITY)
                                                                  Update:  September.  1989
Compound
Dkhlorobutenes
Dkhlorodlf luoromethane
subchronk (RfDj)




chronk (RfD)





1,1-Okhloroethane
subchronk (RfDj)






chronic (RfO)






1.1-Dkhloroethylene
subchronk (RfOg)



Exposure Species
Inhalation; Oral Inhalation Oral
DATA
(f-1*) ,
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


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
(115 mg/kg/day)
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
( mg/kg/day)

NA; 50 ppm In drinking NA rat
water for 2 years
(9 mg/kg/day)

Effect of Concern Reference Dose Uncertainty Factor
Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT (CANCER: SEE TABLE B)

lung and liver 2E*0(5£-1) 9E-1 1000 100
lesions; none



lung and liver 2E-1 (5£-2) 2E-la 10,000 100
lesions; depressed
body weight gain




kidney damage; none 5E*0 (1£»0) 1E+0 100 100






kidney damage; none 5E-1 (1E-1) 1E-19 1000 1000
(also see Table 8)






NA; liver lesions NO 9E-3 NA 1000



Reference
Inhalation/Oral
U.S. EPA, 1967

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,
1985, 1987

Hofmann et al. ,
1971; U.S. EPA,
1984/Hofmann
et al., 1971;
U.S. EPA, 1983,
1984

Hofmann et al..
1971; U.S. EPA,
1984/Hofmann
et al., 1971;
U.S. EPA, 1983,
1984


U.S. EPA, 1984/
Quast et al.,
1983; U.S. EPA,
1985, 1988
0059H
A-30
                                                                                                                                                 11/24/89

-------
                           HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE A: SUBCHRONIC AND CHRONIC TOXICITY (OTHER THAN CARCINOGENICITY)
                                                                   Update:  September, 1989
Compound
chronic (RfD)



1 ,2-c-Dlchloroethylene
1.2-t-Dkhloroethylene
subchrontc (RfOg)



chronic (RfO)



2.4-D1chloropheno1
subchronlc (RfOs)




chronic (RfD)




Dlchlorophenol. 2.3-. 2
2,6-, 3,4- and 3.5-
Dlchloroprop
Olchloropropanes (1.1-,
Exposure
Inhalation; Oral
NA; 50 ppm In drinking
water for 2 years
(9 mg/kg/day)



NA; 0.1 nig/t 1n
drinking water for 90
days (17 mg/kg/day)

NA; 0.1 mg/t 1n
drinking water for 90
days (17 mg/kg/day)


NA; 3 ppm 1n drinking
water for 2 generations
(0.3 mg/kg/day)


NA; 3 ppm 1n drinking
water for 2 generations
(0.3 mg/kg/day)


.5-.


1.2-. 1,3-. 2.2-)
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 lesions ND 9E-3* NA 1000
(also see Table B)


DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT

NA mouse NA; Increased NO 2E-1 NA 100
serum alkaline
phosphatase

NA mouse NA; Increased ND 2E-2a NA 1000
serum alkaline
phosphatase


NA rat NA; Immune function ND 3E-3 NA 100




NA rat NA; Immune function ND 3E-3a NA 100




DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT

OATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT (also see Table B)
Reference
Inhalation/Oral
U.S. EPA. 1984/
Quasi et al. .
1983; U.S. EPA,
1985, 1988
U.S. EPA, 1984

U.S. EPA. 1984/
Barnes et al. .
1985; U.S. EPA,
1988
U.S. EPA, 1984/
Barnes et al..
1985; U.S. EPA,
1968

U.S. EPA.
1987a.b/Exon and
Koller, 1985;
U.S. EPA.
1987a.b
U.S. EPA,
1987a,b/Exon and
Koller. 1985;
U.S. EPA. 1986
1987a.b
U.S. EPA, 1987

U.S. EPA, 1984
U.S. EPA, 1985
0059h
                                                                             A-31
                                                                                                                                                 11/24/89

-------
                           HEALTH EFFECTS  ASSESSMENTS  SUMMARY  TABLE A: SUBCHRONIC AND CHRONIC TOX1CI1Y (OTHER THAN CARCINOGENICITY)
                                                                  Update:  September, 1989
Exposure Species
Compound Inhalation; Oral Inhalation Oral

1,3-Olchloropropene
subchronlc (RfD$) 10 ppm (45.4 mg/m3) rat rat
6 hours/day, 5 days/week
for 13 weeks; 3 rag/kg/
day 1n the diet for
90 days

chronic (RfD) 10 ppm (45.4 mg/m3); rat rat
b 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/n3 (mg/kg/day)] (mg/kg/day)

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


Stott et al.,
1982; U.S. EPA,
1989/Dow
Chemical Co.,
1973; U.S. EPA
1987. 1989
Stott et al.,
1982; U.S. EPA
1989/Oow
Chemical Co..
1973; U.S. EPA
1987, 1989
Dkyclopentadlene
  subchronlc (RfD$)
  chronic (RfD)
1 ppm (5.4 mg/m3),        rat
6 hours/day, 5 days/
week for 90 days (0.61
mg/kg/day); 690 ppm 1n
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 1n
diet for 3 generations
(32 mg/kg/day for males)
rat      liver dysfunction;      2E-3 (6E-4)
         none
rat      liver dysfunction;      2E-4 (6E-5)
         none
3E-1        1000       100    Dodd et al..
                              1982; U.S.  EPA.
                              1987/LUton
                              Blonetlcs,  1980;
                              U.S. EPA,  1987
3E-2      10,000      1000    Dodd et  al.,
                              19B2;U.S.  EPA.
                              1987/LUton
                              Blonetlcs,  1980;
                              U.S. EPA.  1987
Dleldrln
subchronlc (RfD$)
chronic
(RfD)
NA
2
NA
2
; o.i
years
; 0.1
years
ppm 1n
(0.005
ppm In
(0.005
diet for NA
mg/kg/day)
diet for NA
mg/kg/day)
N,N-D1ethylan1l1ne
rat
rat
DATA
NA; liver
lesions ND 5E-5
NA; liver lesions ND 5E-5a
(Cancer: see
Table B)
INADEQUATE FOR
QUANTITATIVE RISK ASSESSMENT
NA TOO U.S. EPA,
Walker et
1969; U.S
1987b
NA 100 U.S. EPA,
Walker et
1969; U.S
19B7b
U.S. EPA,
1987/
al..
. EPA,
1987/
al.,
. EPA.
1987
0059h
                                                     A-32
                                                                                    12/01/89

-------
                           HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE A:  SUBCHRONIC AND CHRONIC TOXICITY (OTHER THAN CARCINOGENICItY)
                                                                   Update:   September. 1989
Compound
Dlethylene glycol
monoethyl ether
subchronk (RfDs)
chronic (RfO)
Dlethylformamlde
subchronk (RfD$)
chronic (RfO)
Exposure Species
Inhalation; Oral Inhalation Oral
NA; diet provided 500 NA rat
mg/kg/day for 90 days
NA; 0.2X In drinking NA rat
water (200 mg/kg/day)
for 2 years
NA; 546 Pg/day (1.56 NA rats
mg/kg/day) 1n diet x
5 days/week for 73 weeks
NA; 546 Mg/day (1.56 NA rats
mg/kg/day) 1n diet x
5 days/week for 73 weeks
Effect of Concern Reference Dose
Inhalation; Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
NA; Impaired renal NO SE+0
function. Increased
testes weight
NA; kidney hlsto- NO 2E*0
pathology
NA; no effect ND 1.1E-1
NA; no effect ND 1.1E-1
Uncertainty Factor Reference
Inhalation Oral Inhalation/Oral
NA 100 U.S. EPA, 1984/
Hall et al..
1966; U.S. EPA.
1984
NA 100 U.S. EPA, 19B4/
Smyth et al..
1964; U.S. EPA,
1984
NA 100 U.S. EPA. 1986/
Argus et al. .
1965; U.S. EPA,
1966
NA 100 U.S. EPA. 1986/
Argus et al.,
1965; U.S. EPA.
1986
l.2-D1ethylhydraz1ne

D1ethy1-p-n1trophenyl
phosphate
  (paraoxon)

Olethyl phthalate
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
U.S. EPA. 1984
U.S. EPA, 1989
subchronlc (RfD$)
chronic (RfD)
Dlmethoate
subchronk (RfD$)
NA; IX 1n diet for NA
16 weeks
(750 mg/kg/day)
NA; IX 1n diet for NA
16 weeks
(750 mg/kg/day)
NA; 1 ppm (0.05 mg/kg/ NA
day) In diet for 2 years
rat NA; reduced ND
terminal body
weight
rat NA; reduced NO
terminal body
weight
rat NA; brain chol- ND
Inesterase
Inhibition
BEtO NA 100 U.S. EPA. 1987a/
Brown et al. ,
1978; U.S. EPA.
1987a
8E-la NA 1000 U.S. EPA, 1987a/
Brown et al.,
1978; U.S. EPA,
198/a,b
2E-4 NA 300 U.S. EPA. 19B5/
American Cyanlmld
Co.. 1986; U.S.
EPA. 1988
0059h
                                                                             A-33
                                                                                                                                                   1/24/89

-------
                          HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE  A:  SUBCHRONIC AND CHRONIC  TOXICMY  (OTHER  THAN  CARCINOGENICITY)
                                                                 Update:   September,  1989

Compound
chronic (RfO)




N.N-D1methylan1l1ne
subchronU (RfO$)



chronic (RfD)



N,N-01fflethyUormam1de
subchroMc (RfO$)



chronic (RfO)



Olmethylphenols (2 1-

2. 6-01methyl phenol
subchronk (RfOs)




Exposure
Inhalation; Oral
NA; 1 ppm (0.05 mg/kg/
day) In diet for 2 years




NA; 31.25 mg/kg/day by
gavage x 5/7 days for
13 weeks

NA; 31.25 mg/kg/day by
gavage x 5/7 days for
13 weeks


NA; 540 ppm (96 mg/kg/
day) 1n diet for 119
days

NA; 540 ppm (96 mg/kg/
day) In diet for 119
days

2.4-, 2.5-. 3,6-)


NA; 0.6 mg/kg/day for
8 months



Species Effect of Concern Reference Oose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
NA rat NA; brain chol- NO 2E-4a NA 300
Inesterase
Inhibition



NA rat NA; splenomegaly NO 2E-2 NA 1000
and splenic
hemoslderosls

NA rat NA; splenomegaly NO 2E 3a NA 10,000
and splenic
hemoslderosls


NA mouse NA; Increased NO 1E+0 NA 100
liver weight


NA mouse NA; Increased NO 11-1 NA 1000
liver weight


DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
(Cancer: see Table B)

NA rat NA; effects on NO 6E-3 NA 100
blood pressure,
weight gain and
hlstologlcal appear
ance of several organs
Reference
Inhalation/Oral
U.S. EPA, 19B5/
American
Cyanlmld Co. ,
1986; U.S. EPA.
1988

U.S. EPA, 1986/
Abdo et al..
1984; U.S. EPA,
1987
U.S. EPA, 1986/
Abdo et al..
1984; U.S. EPA,
1987

U.S. tPA, 1986/
Becd et al.,
1983; U.S. EPA,
1986
U.S. EPA. 1986/
Becci et al..
1983; U.S. EPA.
1986
U.S. EPA. 1986


U.S. EPA. 1987/
Veldre and
Janes. 1979;
U.S. EPA. 1986.
1987
0059h
A 34
                                                                                                                                                 09/25/89

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                          HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE  A:  SUBCHRONIC  AND CHRONIC  TOXICITY  (OTHER  THAN CAHC1NOGENICITY)
                                                                 Update:   September,  1989
Compound
2. 6 -Dimethyl phenol
chronic (RfO)
3.4-l)lmethylphenol
subchronU (RfOj)
chronic (KfD)
Dimethyl phthalate
Dimethyl terephthalate
subchronlc (RfOs)
chronic (RfO)
N.N-Olmethylurea
m-Dinltrobenzene
subchronlc (RfDs)
Exoosure
Inhaldtlon; Oral
NA; 0.6 mg/kg/day for
8 months
NA; 1.4 mg/kg/day
for 8 months
NA; 1.4 mg/kg/day
for 8 months

NA; 2500 ppra
(12S 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) 1n drinking water
for lb weeks
Species Effect of Concern Reference Dose
Inhalation Oral Inhalation; Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
NA rat NA; effects on NO 6E 4a
blood pressure,
weight (jdln and
hlstologlcal appear-
ance of several orgdns
NA rat NA; reduced growth, ND 1E-2
Internal lesions
NA rat NA; reduced growth. NO It 3d
Internal lesions
DA1A INAUEQUAIE FOR QUANTITATIVE RISK ASSESSMENTS- '
NA rat NA; chronic NO 1E-1
kidney Inflam-
mation
NA rat NA; chronic ND lE-la
kidney Inflam-
mation
OAIA INADEQUATE fOR QUANTITATIVE RISK ASSESSMENT
NA rat NA; increased ND 1E-3
splenic weight
Uncertainty Factor Reference
Inhalation Oral Inhalation/Oral
NA 1000 U.S. EPA, 1987/
Veldre and
Janes. 1979;
U.S. EPA. 1986.
1987
NA 100 U.S. EPA. 1987/
Veldre and
Janes. 1979.
U.S. tPA. 1987.
1988
NA 1000 U.S. EPA. 1987/
Veldre and
Janes. 1979,
U.S. F.PA. 1987.
1988
U.S. EPA. 1987
NA 1000 U.S. EPA. 1984/
NCI. 1979;
U.S. EPA, 1985
NA 1000 U.S. EPA. 1984/
NCI. 1979;
U.S. EPA. 1985
U.S. EPA. 1984
NA 300 U.S. EPA. 1985/
Cody et a!.,
1981; U.S. EPA.
1988
OOS9h
                                                                            A 3i
                                                                                                                                                 09/25/89

-------
                           HEAL1H EFFECTS ASSESSMENTS SUMMARY  TABLE  A:  SUBCHRONIC  AND  CHRONIC  TOXICITY  (OTHER  THAN CARCINOGENICITY)
                                                                  Update:   September,  1969
Compound
chronic (RfO)
Dlnltrobenzenes (o-,
subchronk (RfOg)
chronic (RfO)
2,6-D1n1tro-p-creso1
4,6-Dlnltro-o-cresol
subchronk (RfDs)
chronic (RfD)
OlnltrophenoTs (2,3-;
OlnUrotoluenes (2,3-
DI-n-octyT phthalate
Dlnoseb
subchronk (RfDj)
Exposure
Inhalation; Oral
NA; 3 ppm (0.40 mg/kg/
day) In drinking water
for 16 weeks
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; NA
NA; NA
2.5-; 2,6-; 3.5-)
; 2.4-; 2.5-; 2.6-; 3.4-)

NA; 1 mg/kg/day In diet
for 29 weeks
Species Effect of Concern Reference Dose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
fmg/m3 (mg/kg/day)] (mg/kg/day)
NA rat NA; Increased ND lE-4a NA 3000
splenic weight
NA rat NA; Increased NO 3E-3 NA 100
splenic weight
NA rat NA; Increased NO 3E-4 NA 1000
splenic weight
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA NA NA; NA NO 1E-4& NA 1000
NA NA NA; NA NO 1E-4M NA 1000
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT (Cancer: see Table B)
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA rat NA; decreased NO lE-3bb NA 1000
fetal weight
Reference
Inhalation/Oral
U.S. EPA, 1985/
Cody et al.,
1981; U.S. EPA,
1988
U.S. EPA, 1985/
Cody et al.,
1981; U.S. EPA.
19B5
U.S. EPA, 1985/
Cody et al..
1981; U.S. EPA,
1985
U.S. EPA. 1984
U.S. EPA. 1986/
ACGIH, 1985;
U.S. EPA, 1986
U.S. EPA, 1986/
ACGIH, 1985;
U.S. EPA. 1986
U.S. EPA, 1984
U.S. EPA, 1986
U.S. EPA, 1987
U.S. EPA, 1984/
Dow Chemical
Co.. 1981;
U.S. EPA. 1986
0059h
A-36
11/24/89

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                           HEALTH EFFECTS ASSESSMENTS SUMMARY  TABLE  A:  SUBCHRONIC  AND  CHRONIC  TOXICITY  (OTHER  THAN CARCINOGENICITY)
                                                                  Update:   September,  1989
Compound
chronic (RfD)


N,N-D1phenylam1ne
subchronlc (RfOj)



chronic (RfO)




Direct Llghtfast Blue
Endosulfan
subchronlc (RfDj)

chronic (RfO)


Exposure
Inhalation; Oral
NA; 1 mg/kg/day In diet
for 29 weeks


NA: 0.0170 (2.5 mg/kg/
day) In diet for 2 years



NA: 0.0170 (2.5 mg/kg/
day) 1n diet for 2 years






NA; 3 ppm 1n diet In
2-generatlon reproduc-
tive study
(0.15 mg/kg/day)
NA; 3 ppm In diet In
2-generat1on reproduc-
tive study
(0.15 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 ND lE-3a.1.bb NA 1000
fetal weight


NA dog NA; decreased ND 2.5E-2 NA 100
body weight
gain and
Increased liver
and kidney
weights
NA dog NA; decreased NO 2.5E-23 NA 100
body weight
gain and
Increased liver
and kidney
weights (also see
Table B)
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT (also see Table B)

NA rat NA; mild kidney NO 2E-4 NA 1000
lesions

NA rat NA; mild kidney ND 5E-5* NA 3000
lesions

Reference
Inhalation/Oral
U.S. EPA, 1984/
Dow Chemical
Co., 1981;
U.S. EPA. 1986
U.S. EPA, 1985/
Thomas et al.,
1967; U.S. EPA,
1986


U.S. EPA, 1985/
Thomas et al.,
1967; U.S. EPA.
1986



U.S. EPA, 1987

U.S. EPA, 1987a/
Huntlngton
Research Center,
1984; U.S. EPA,
1987a
U.S. EPA, 19B7a/
Huntlngton
Research Center,
1984; U.S. EPA,
1987b
0059h
                                                                             A-37
                                                                                                                                                  11/24/89

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                          HEALTH EFFECTS ASSESSHEHTS SUMMARY TABLE A:  SUBCHRONIC AND CHROMIC TOXICITY (OTHER  THAN CARCIM06EM1C1TY)
                                                                  Update:   September, 1989
Compound
Endothall
subchronlc (RfDs)

chronic (RfO)

Endrln
subchronlc (RfD$)


chronic (RfO)

Ep1chlorohydr1n
subchronlc (RfOj)




chronic (RfD)


Exposure Species
Inhalation; Oral Inhalation Oral
NA; 100 ppm dlsodlum NA dog
endothall In the diet
for 2 years (2 mg
endothall lon/kg/day)
NA; 100 ppm dlsodlum NA dog
endothall In the diet
for 2 years (2 mg
endothall lon/kg/day)
NA; 1 ppm In diet for NA dog
IB months
(0.045 mg/kg/day)
NA; 1 ppm In diet for NA dog
>2 years
(0.025 mg/kg/day)
5 ppm, 6 hours/day, mouse rat
5 days/week for 87 -88
days (HEU0.25 mg/m3);
10 ppm (37.8 mg/m3),
6 hours/day, 5 days/week
for 136 weeks
5 ppm, 6 hours/day, mouse rat
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
Effect of Concern Reference Dose Uncertainty Factor
Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
NA; stomach effect NO 2E-2 N* 10°

NA; stomach effect NO 2E-2a NA 100

NA; increased NO 5E-4 NA 100
relative organ
weights
NA; convulsions NO 3E-4« NA 100
and liver lesions

nasal turblnate 3E-3 2E-2 100 100
Injury; kidney damage




nasal turblnate 3E-4J 2E-3*,b 1000 1000
Injury; kidney damage
(also see Table 8)


Reference
t_fct*l*lt /\n /ftr al
Inna lat lon/ura i
U.S. EPA, 1989/
Keller, 1965;
Pennwalt Agchem,
„ rf. II C FPA.
n.U, u.vi Lrn,
1986, 1989
U.S. EPA, 1989/
Keller, 1965;
Pennwalt Agchem,
n rl • II S EPA
II i U . , U • «S « Lin,
1986. 1989
U.S. EPA, 1987/
Tronn At fll
1 1 VTUII * i o i • »
1QCC. II C fpft
1 7 J.J t U«<*» Lrn»
1985a, 1987
U.S. EPA, 1987/
CBI; U.S. EPA,
1985a, 1987,
1988
Quasi et al.,
1979/Laskln et
al., 1980; U.S.
EPA. 1984. 1985



Quast et al.,
1979/Laskln et
al., 1980; U.S.
EPA, 1984. 1985


EPTC (see S-Ethyl dipropylthlocarbamate)
Ethoprop
DATA
INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
U.S. EPA. 1984
0059h
                                                                             A-38
                                                                                                                                                  12/07/89

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HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE  A:  SUBCHRONIC AND CHRONIC TOXICITY (OTHER  THAN  CARCINOGENICITY)
                                        Update:   September, 1989
Exposure
Compound Inhalation; Oral
2-Ethoxyethanol
subchronk (RfDs) 10 ppm (37 mg/m3)
6 hours/day on days 6-15
of gestation (6.8 mg/kg/
day); 50 »t (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
subchronk (RfDs) NA; 50 ppm (30.1 mg/kg)
x 6 hours/day on gesta-
tlonal day 6-18
chronk (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
subchronk (RfDs) NA; 900 mg/kg/day by
gavage for 90 days
Ethyl acetate
chronk (RfD) NA; 900 mg/kg/day by
gavage for 90 days
n-Ethylanlllne
0059h
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 fetotoxklty; 2E-1 (7E-2)bb 5£-lbb 100 100
fetotoxklty
rat rat altered hemotology; 2E-1 (5E-2) 4E-1 1000 1000
reduced body weight
(also see Table B)
NA rat NA; decreased NO 3E-lb>bb NA 100
ossification
NA rat NA; decreased NO 3E-lb.bb NA 100
ossification
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA rat NA; mortality. NO 9E+0 NA 100
body weight
loss
NA rat NA; mortality, NO 9E-la NA 1000
body weight loss
(also see Table B)
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
A-39
Reference
Inhalation/Oral
Doe, 1984a;
U.S. EPA, 1984/
Stenger et al.,
1971; U.S. EPA,
1984
Barbee et al.,
1984; U.S. EPA,
1984/Melnkk.
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, 1986a/
U.S. EPA,
1986a.b,c
U.S. EPA. 1986a/
U.S. EPA,
1986a,b,c
U.S. EPA, 1986
11/24/89

-------
                         HEALTH mtCTS ASSESSMfNTS SUMMARY 1ABU A: SUBCHRONIC AMD CHROMIC TOXICIIY (OTHER THAN CARCINOGINICITY)
                                                                 Update:  September, 1989
Compound
f.thylbenzene
subchronk (RfOs)
chronic (RfO)
Ethyl chloride
Exposure
Inhalation; Oral
NA; 136 ing/kg 5
days/week for 18?
days (97.1 mg/kg/day)
NA; 136 mg/kg S
days/week for 182
days (97.1 mg/kg/day)

S -Ethyl dlpropylthlocarbamate
subchronk (RfDj) NA; SO ppn In diet for
2 generations (2.5 mg/
kg/day)
chronic («fO)
Ithylene cyanohydrln
subtttronlc (RfOj)
chronic (RfO)
MA; SO p(M In diet for
2 generations (2.S mg/
kg/day)
NA; 30 *qAg/day tn
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 ora i
[mg/m3 (mg/kg/day)) (mg/kg/day)
NA rat MA; hepatotoxldty NO U+0 NA 100
and nephrotoxlc Ity
NA rat MA; hepatotoxldty MO H-1a NA 1000
and ncphrotoxlclty'
OA1A 1NADF.QUATE fOR QUANT 11 AT I VE RISK ASSESSMENT
NA rat NA; degenerative NO 2.5E-2 NA 100
cardlomyopathy
NA rat MA; degenerative MO 2.5E-2* MA 100
cardlomyopathy
HA rat MA; decreased heart MO 3E-1 HA 100
and brain weights
HA rat NA; decreased heart NO 3E-1 NA 100
and brain weights
Reference
Inhalation/Oral
U.S. EPA, 1984/
Wolf et al. .
1956; U.S. EPA.
1984. 1985. 1986
U.S. EPA. 1984/
Wolf et al..
1956; U.S. f-PA,
1984, 1985, 1986
U.S. EPA, 1987
U.S. EPA, 1984/
PPG Industries,
1986; U.S. EPA.
1984. 1987
U.S. tPA. 1984/
PPG Industries.
1986; U.S. EPA.
1984. 1987
U.S. tPA. m»/
Sauerhoff
et al.. 1976;
U.S. EPA. 1988
U.S. EPA, 1988/
Sauerhoff
et al., 1976;
U.S. EPA, 1988
0059h
                                                                             A 40
                                                                                                                                                  09/?5/89

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                           HEALTH EFFECTS ASSESSMENTS SUMMARY  TABLE  A:  SUBCHRONIC  AND CHRONIC TOXICITY  (OTHER THAN CARCINOGENICITY)
                                                                  Update:   September.  1989

Compound

Ethylenedlamlne
subchronlc (RfDg)







chronic (RfD)


Exposure Species
Inhalation; Oral Inhalation Oral

59 ppm (145 mg/ra3) rat rat
7 hours/day, 5 days/week
for 30 days (25.8 mg/kg/
day); 3-month dietary
study with 50 mg/kg/day
ethylenedlamlne dlhydro-
chlorlde (22.6 mg
ethylenedlamlne/kg/day
NA; 3-month dietary NA rat
study with 50 mg/kg/day
ethylenedlamlne d 1 hydro -
rhlnrlde (27.6 ma
Effect of Concern
Inhalation; Oral

death, kidney
and liver
lesions; liver
and hematologlc
changes



NA; liver and
hematologlc
changes
Reference Dose Uncertainty Factor Reference
Inhalation Oral Inhalation Oral Inhalation/Oral
[mg/ra3 (mg/kg/day)] (mg/kg/day)
lEtO (3E-1) 2E-1 100 100 Pozzanl and
Carpenter, 1954;
U.S. EPA, 1988/
Yang et al.,
1983; U.S. EPA.
1988


ND 2E-2 NA 1000 U.S. EPA, 1988/
Yang et al.,
1983; U.S. EPA,
1988
Ethylene glycol
  subchronk (RfO$)
  chronic (RfD)
Ethylene glycol
monobutyl ether
                        ethylenedlamlne/kg/day
NA; 200 mg/kg/day In      NA         rat
developmental toxlclty
NA; 200 mg/kg/day In      NA         rat
2-year dietary study
NA; fetotoxlclty
ND
NA; mortality,         ND
liver and kidney
effects
2E+Obb        NA       100    U.S.  EPA,  1987a/
                              Maronpot
                              et al.,  1983;
                              U.S.  EPA,
                              1987a.b

2E+0*         NA       100    U.S.  EPA,  1987a/
                              DePass et  al.,
                              1986a; U.S.  EPA.
                              1987a,b
subchronlc (RfD$)


chronic (RfO)



25 ppm (121 mg/m3) rat
6 hours/day, 5 days/
week for 13 weeks
(16 mg/kg/day); NA
25 ppm (121 mg/m3) rat
6 hours/day, 5 days/
week for 13 weeks
(16 mg/kg/day); NA
NA altered hematology; 6E-1 (2E-1) ND
NA


NA altered hematology; 6E-2 (2E-2) ND
NA


100 NA Dodd et al..
1983/U.S. EPA,
1984

1000 NA Dodd et al.,
1983/U.S. EPA,
1984

0059h
                                                     A-41
                                                                                                                                                 11/24/89

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                           HI AllH  llltUS AbblbbMtNIb bUMMAKY IABU A: bUBLHKUNIl ANU CHKUNIl IUAH.ni  (UllllK  IMAN  IAKUNUUINIU 11)
                                                                  Update:  September, 1989
Compound
Ethylene thlourea

Ethyl ether
subchronlc (RfDg)




chronic (RfO)




Ethyl methacrylate
subchronlc (RfOj)





(hronli (RID)





Ethyl toluene (o-, p-,
4-Ethyl-o-xylene
F luorldes
subchronlc (RfDg)



chronic (RfDs)



Exposure
Inhalation; Oral



NA; 500 mg/kg/day for
90 days



NA; SOO mg/kg/day for
90 days




NA; 65 ppm (7.5 mg/kg/
day) methyl methacrylate
« 114.5/100.13 (mo lee
uUr weight ratio) In
dr Ink (09 water for ?
jHI \
M. kS ppa ( / S «g/kg/
04 f ) arthfl arlhacryUtr
• 114 S/IOO 13 |«olrt
u\tr weight ratio) In
dr Ink Ing water for ?
years
m-)


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


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


Species Effect of Concern Reference Dose
Inhalation Oral Inhalation; Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENTS
(also see Table B)

NA rat NA; liver effects NO 5E»0




NA rat NA; liver effects NO 5E-19





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




NA rat NA; Increased NO 9E-?9
kidney weight
(also see lable B)



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

NA human NA: dental fluorosls NO 6E-2
at higher levels


NA human NA: dental fluorosls NO 6E-2a
at higher levels


Uncertainty Factor Reference
Inhalation Oral Inhalation/Oral
U.S. EPA. 1964


NA 100 U.S. EPA. 19B7/
American
fllogenlcs Corp. .
1986; U.S. EPA.
1987
NA 1000 U.S. EPA, 1987/
American
Blogenlcs Corp. ,
1986; U.S. EPA.
1987

NA 100 U.S. EPA, 19B6/
Bor/el leca
et al.. 1964;
U.S. EPA. 1986


NA 100 U.S. EPA. 1986/
Borzelleca
et al., 1964;
U.S. EPA. 1986


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

NA 1 U.S. EPA, 1989/
Hodge, I960;
U.S. EPA. 1986.
1989
NA 1 U.S. EPA. 1989/
Hodge. 1950;
U.S. EPA. 1986.
1989
0059h
A-42
                                                                                                                                                12/29/89

-------
                          HEALTH  EFFECTS ASSESSMENTS SUMMARY TABLE A: SUBCHRONIC AND CHRONIC TOXICITY (OTHER THAN CARCINOGENICUY)
                                                                  Update:  September, 1989
Compound
MuMdone
subchronk (RfDs)



chronic (RfD)




Folpet
subchronlc (RfDs)



chronk (RfD)




Exposure
Inhalation; Oral

NA; 200 ppm 1n the diet
for 2 years (8 mg/kg/
day)


NA; 200 ppm 1n the diet
for 2 years (6 mg/kg/
day)



NA; 10 mg/kg/day 1n
capsules for 1 year



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



Formaldehyde cyanohydrln
Furan
subchronk (RfDs)


chronk (RfO)



furfural
subchronk (RfDs)






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);
11 mg/kg, 5 days/week
for 13 weeks (7.9 rag/
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; kidney and testes NO 8E-2 NA 100



NA rat NA; kidney and NO 8E-2a NA 100
and testes




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


NA dog NA; body weight ND 1E-13 NA 100
gain, blood
chemistry
(also see Table B)

DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT

NA mouse NA; hepatic lesions ND 1E-2 NA 100


NA mouse NA; hepatic lesions ND 1E-33 NA 1000




hamster rat olfactory degenera- 5E-1 (1E-1) 3E-2 100 300
tlon; hepatotoxklty




Reference
Inhalation/Oral

U.S. EPA, 1988/
Ell Lilly and
Co., 1980;
U.S. EPA, 1984
1988
U.S. EPA, 1988/
E11 Lilly and
Co., 1980;
U.S. EPA, 1984
19B8

U.S. EPA, 1987/
Chevron Chemical
Corp.. 1986;
U.S. EPA, 1984.
1987
U.S. EPA. 1987/
Chevron Chemical
Corp., 1986;
U.S. EPA, 1984,
1987
U.S. EPA, 1988

U.S. EPA, 1987/
SRI, 1982b;
U.S. EPA, 1987
U.S. EPA, 1987/
SRI, 19826;
U.S. EPA. 1986.
1987

Feron et al. .
1979; U.S. EPA,
1988/SRI, 1981;
U.S. EPA. 1987


0059h
                                                                            A-43

-------
                           HEALTH EFFECTS ASSESSMENTS SUMMARY  TABLE  A:  SUBCHRONIC  AND  CHRONIC  TOX1CITY  (OTHER  THAN  CARCINOGENIC1TY)
                                                                  Update:   September,  1969
Compound
chronic (RfD)
Glyctdaldehyde
subchronk (RfOg)
chronic (RfDs)
Heptachlor
subchronk (RfDs)
chronic (RfO)
n-Heptane
Hexabromobenzene
subchronk (RfDs)
chronk (RfD)
Exposure Species
Inhalation; Oral Inhalation Oral
20 ppm (7? mg/m3), 6 hamster rat
hours/day, 5 days week
for 13 weeks (13 rag/kg);
11 mg/kg, 5 days/week
for 13 weeks (7.9 mg/kg/
day)
10 ppm (29 mg/m3), 4 rat rat
hours/day, 5 days/week
for 12 weeks (HEC, 3.5
mg/m3); 1.1 mg/kg/day
10 ppm (29 mg/m3). 4 rat rat
hours/day, 5 days/week
for 12 weeks (HEC, 3.5
mg/m3); 1.1 mg/kg/day
NA; 3 ppm 1n diet for NA rat
2 years (0.16 mg/kg/day)
NA; 3 ppm 1n diet for NA rat
2 years (0.15 mg/kg/day)
DATA
NA; 40 ppm In the diet NA rat
for 12 weeks
(2 mg/kg/day)
NA; 40 ppm 1n the diet NA rat
for 12 weeks
(2 mg/kg/day)
Effect of Concern Reference Dose Uncertainty Factor
Inhalation; Oral Inhalation Oral Inhalation Oral
[ng/n3 (wg/kg/day)] (mg/kg/day)
olfactory degenera- 5E-2 (1E-2) 3E-3a 1000 3000
tlon; hepatotoxkUy
decreased body weight 1E-2 4E-3 300 300
and kidney effects;
decreased body weight
and kidney effects
decreased body weight 1E-3 4E-4a 3000 3000
and kidney effects;
decreased body weight
and kidney effects
(also see Table B)
NA; Increased liver ND 5E-4 NA 300
weight
NA; Increased liver ND 5E-4a NA 300
weight (also see
Table B)
INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA; Induced ND 21-2 NA 100
carboxylesterase
activity
NA; Induced ND 2E-3a NA 1000
carboxylesterase
activity
Reference
Inhalation/Oral
Feron et al.,
1979; U.S. EPA,
19B8/SRI, 1981;
U.S. EPA, 1967
Hlne et al..
1961; U.S. EPA,
1989/Hlne et
al.. 1961; U.S.
EPA, 1987. 1969
H1ne et al.,
1961; U.S. EPA,
1989/Hlne et
al., 1961; U.S.
EPA, 1987, 1989
U.S. EPA, 1987a/
Velslcol
Chemical, 1955;
U.S. EPA, 19B7b
U.S. EPA, 1987a/
Velslcol
Chemical. 1955;
U.S. EPA, 1987b
U.S. EPA. 1989/
U.S. EPA, 1989
U.S. EPA. 1985/
Hendoza et al. ,
1977; U.S. EPA.
1964. 1985
U.S. EPA. 1985/
Mendoza et al.,
1977; U.S. EPA,
1984. 1985
OOS9h
A-44
01/11/90

-------
                           HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE  A:  SUBCHRONIC  AND  CHRONIC  TOXICITY  (OTHER  THAN CARCINOGEN 1C ITY)
                                                                  Update:   September.  1989
Compound
Hexachlorobenzene
subchronlc (RfO$)



chronic (RfD)



Hexachlorobutadlene
subchronlc (RfDg)



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

Effect of Concern Reference Dose Uncertainty factor
Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/n3 (mg/kg/day)] (mg/kg/day)

NA; liver and hema- ND BE -4 NA 100
tologlc effects


NA; liver and hema- ND 8E-4a NA 100
tologlc effects
(also see Table B)


NA; kidney toxlclty ND 2E-3 NA 100



NA; kidney toxlclty NO 2E-3a NA 100
(Cancer: see
Table B)



NA; liver and NO 3E-3 NA 100
and kidney toxlclty


NA; liver and ND 3E-4a NA 1000
kidney toxlclty
(Cancer: see
Table B)
Reference
Inhalation/Oral

U.S. EPA. 19B4/
Arnold et al.,
1985; U.S. EPA,
1988
U.S. EPA. 1984/
Arnold et al. .
1985; U.S. EPA,
1988

U.S. EPA, 1984/
Koclba et al.,
1977; U.S. EPA,
1985
U.S. EPA. 1984/
Koclba et al.,
1977; U.S. EPA.
1985


U.S. EPA, 1984/
Zoecon Corp. .
1983; U.S. EPA,
1986
U.S. EPA, 1984/
Zoecon Corp. ,
1983; U.S. EPA.
1986
Hexachlorocyclopentadlene
subchronlc (RfDs)







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)


respiratory tract 7E-4 (2E-4) 7E-2 100 100
lesions; fore-
stomach lesions





Battelle
Northwest
Laboratories,
1984; U.S. EPA.
19B4/SRI, 1981a;
Abdo et al.,
1984; U.S. EPA.
1985
0059h
                                                                             A-45
01/11/90

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                           HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE A: SUBCHRONIC AND CHRONIC TOXICITY (OTHER THAN CARCINOGEN!CITY)
                                                                   Update:  September, 1989
      Compound
                              Exposure
  Inhalation; Oral
                              Species
Inhalation  Oral
Effect of Concern
Inhalation; Oral
                                                Reference Pose
    Inhalation
[mg/n>3 (mg/kg/day)]
  Oral
(mg/kg/day)
Uncertainty Factor
InhalationOra1
   Reference
Inhalation/Oral
  chronic (RfD)
Hexachloroethane
  subchronU (RfO$)
  chronic (RfO)
Hexachlorophene
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.
S days/week for 13
weeks (7.1 mg/kg/day}
NA; 16 week dietary       NA         rat
study (1 mg/kg/day)
NA; 16 week dietary       NA         rat
study (1 mg/kg/day)
                     respiratory tract
                     lesions;  fore-
                     stomach lesions
                        7E-5 (2E-5)
                     NA;  kidney degenera-   NO
                     tlon
                     NA;  kidney degenera-   NO
                     tlon (also see
                     Table B)
                       7E-3*      1,000     1,000    Battelle
                                                     Northwest
                                                     Laboratories,
                                                     1984;  U.S.  EPA,
                                                     1988/SRI,  1981a;
                                                     Abdo et al.,
                                                     1984;  U.S.  EPA,
                                                     1985,  1988
                                          1E-2          NA       100    U.S.  EPA,  1987a/
                                                                        Gorztnskl
                                                                        et  al.,  1985;
                                                                        U.S.  EPA,  1987b.
                                                                        1989

                                          1E-3*         NA      1000    U.S.  EPA,  1987a/
                                                                        Gorrlnskl
                                                                        et  al.,  1985;
                                                                        U.S.  EPA,  1987b,
                                                                        1989
subchronU (RfDg)




chronic (RfD)




Hexamethylenedlamlne
N-Hexane
subchronlc (RfDj)



NA; 30 ppm In the diet NA
for 13 weeks (0.75 mg/
kg/day)


NA; 30 ppm In the diet NA
for 13 weeks (0.75 mg/
kg/day)




200 ppm (705 mg/m3) rat
12 hours/day, 7 days/
week for 24 weeks (HEC,
352 mg/m3); 570
mg/kg/day
dog NA; nervous NO 3E-3
system effects
(also see
Table B)

dog NA; nervous NO 3E-4*
system effects
(also see
Table B)

DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT

rat axonopathy and nerve 4E-1 6E-1
condition altera-
tions; neuropathy or
testlcular atrophy

NA 300 U.S. EPA, 198B/
Nationwide Cheat.
Corp. 1974;
U.S. EPA, 1986,
1988
NA 3000 U.S. EPA, 1988/
Nationwide Chem.
Corp. 1974;
U.S. EPA, 1986,
1988
U.S. EPA. 1985

1000 1000 Ono et al.,
1982; U.S. EPA,
1989/Krasavage
et al., 1980;
U.S. EPA. 1989
00591)
                                                     A-46
                                                                                                                                                 11/24/89

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                           HEALTH EFFECTS ASSESSMENTS SUMMARY  TABLE  A:  SUBCHRONIC  AND  CHRONIC  TOXICI1Y  (OTHER  THAN CARCINOGENICITY)
                                                                  Update:   September,  1989
Compound
chronic (RfO)
2-Hexanone
p-Hydroqulnone
subchronlc (RfD$)
chronic (RfD)
Iron
Isobutyl alcohol
suchronlc (RfD$)
chronic (RfD)
Isophorone
subchronlc (RfOj)
chronic (RfO)
Isopropal In
subchronlc (RfDg)
Exposure
Inhalation; Oral
200 ppm (705 mg/m3)
12 hours/day, 7 days/
week for 24 weeks (HEC,
352 mg/m3); 570
mg/kg/day

NA; 300 nig/day for 3-5
months (4.29 mg/kg/day)
NA; 300 nig/day for 3-5
months (4.29 mg/kg/day)

NA; 316 mg/kg/day 1n the
diet for 13 weeks
NA; 316 mg/kg/day In the
diet for 13 weeks
NA; 90-day oral
(capsules) study
(ISO mg/kg/day)
NA; 90-day oral
(capsules) study
(150 mg/kg/day)
NA; 250 ppm In the diet
for 90 days (IS mg/kg/
day)
Species Effec| of Concern Reference Dose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/n>3 (rog/kg/day)) (mg/kg/day)
rat rat axonopathy and nerve 4E-2 6E-2 10,000 10,000
condition altera-
tions; neuropathy or
testlcular atrophy
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA human NA; hematologlcal NO 4E-1 NA 10
effects
NA human NA; hematologlcal NO 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-1& NA 1000
and ataxla
NA dog NA; kidney lesions NO 2E+0 NA 100
NA dog NA; kidney lesions ND 2E-1* NA 1000
(Cancer: see
Table B)
NA rat NA; hematologlcal ND 1.5E-1 NA 100
effects, altered
organ weights
Reference
Inhalation/Oral
Ono et al.,
1982; U.S. EPA,
1989/Krasavage
et al., 1980;
U.S. EPA. 1989
U.S. EPA, 1989
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.c
U.S. EPA, 1986a/
U.S. EPA,
1986a,b.c
U.S. EPA, 1987/
Rohm and Haas.
1972; NTP, 1986;
U.S. EPA, 1986
U.S. EPA. 1987/
Rohm and Haas,
1972; NTP. 1986;
U.S. EPA. 1986
U.S. EPA. 1986/
Ell Lilly Co.,
1985; U.S. EPA.-
1984. 1986
0059h
A-47
12/01/89

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                           HEALTH EFFECTS ASSESSMENTS  SUMMARY  TABLE  A:  SUBCHRONIC  AND  CHRONIC  TOXICITY (OTHER  THAN  CARCINOGENICITY)
                                                                  Update:   September,  1969
Compound
chronic (RfO)
LactonUHIe
Lead
subchrontc (RfOj)
chronic (RfD)
Lead alkyls: tetrabutyl
tetraethyl, tetramethyl
tetrapropyl, trlethyl,
trlmelhyl, trlpropyl,
trlmethylethyl.
dlmethylethyl,
methyltrlethyl
subchronlc (RfOj)
chronic (RfD)
Exposure
Inhalation; Oral
NA; 250 ppn In the diet
for 90 days (15 mo/kg/
day)

NA; NA
NA; NA
»
t
NA; 0.00017 mg/kg/day
by gavage for 20 weeks
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
[ing/ma (»g/ko7day)J (mg/kg/day)
NA rat NA; hematologlcal NO 1.5E-2" NA 1000
effects, altered
organ weights
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA NA NA; NA NOP NO NA NA
NA NA CNS effects; HOP NOQ NA NA
CNS effects
(also see Table B)
NA rat NA; liver and NO 1E-6 NA 1000
neuronal damage
NA rat NA; liver and NO 1E-7* NA 10,000
neuronal damage
Reference
Inhalation/Oral
U.S. EPA, 19B6/
Ell Lilly Co.,
1985; U.S. EPA,
1984, 1986
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, 19B5/
Schepers, 1964;
U.S. EPA, 1985
U.S. EPA, 1985/
Schepers, 1964;
U.S. EPA, 1985
Llndane (see Hexachlorocyclohexane. gamma)
Llnuron
subchronk (RfO$)
NA; 25 ppm In the diet
for 2 years (0.625 mg/
kg/day)
NA dog NA; hematologlcal ND 2E-3 MA 300
U.S. EPA, 1986/
Du Pont de
Nemours and Co..
1962; U.S. EPA,
1984, 1986
0059h
                                                                             A-48
H/24/89

-------
                           HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE  A:  SUBCHRONIC AND CHRONIC  TOXICITY  (OTHER  THAN  CARCINOGENICITY)
                                                                  Update:   September,  1989
Compound
chronic (RfO)
Malathlon
subchronlc (RfOg)
chronic (RfD)
Malelc anhydride
subchronlc (RfD$)
chronic (RfD)
Malelc hydra zlde
subchronlc (RfDj)
chronlc(RfD)
Exposure Species
Inhalation; Oral Inhalation Oral
NA; 25 ppm In the diet NA dog
for 2 years (0.625 mg/
kg/day)
NA; 16 ing/day In cap- NA human
sules for 47 days
(0.23 mg/kg/day)
NA; 16 mg/day 1n cap- NA human
sules for 47 days
(0.23 mg/kg/day)
NA; 10 mg/kg/day 1n 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)
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-3*>U NA 300
(also see Table B)
NA; hematologlcal ND 2E-2 NA 10
NA; hematologlcal ND 2E-2" NA 10
NA; kidney lesions ND 1E-1 NA 100
NA; kidney lesions ND l£-la NA 100
(also see Table B)
NA; altered kidney ND 5E-1 NA 1000
function
NA; altered kidney ND 5E-1 NA 1000
function
Reference
Inhalation/Oral
U.S. EPA. 1986/
Du Pont de
Nemours and Co.,
1962; U.S. EPA,
1984, 1986
U.S. EPA. 1987/
Hoe Her and
Rider, 1962;
U.S. EPA, 1984,
1987
U.S. EPA, 1987/
Hoeller and
Rider, 1962;
U.S. EPA. 1984,
1987
U.S. EPA, 1988/
Jessup et al. ,
1982; Preache,
1983; U.S. EPA,
1986, 1988
U.S. EPA, 1988/
Jessup et al. ,
1982; Preache,
1983; U.S. EPA.
1986, 1988
U.S. EPA, 1989/
Van der Haljden
et al., 1981;
U.S. EPA, 1988,
1989
U.S. EPA, 1989/
Van der Haljden
et al.. 1981
U.S. EPA, 1988.
1989
0059h
                                                                            A-49
11/24/89

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                           HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE A: SUBCHRONIC AND CHRONIC TOXICITY (OTHER THAN CARCINOGENICITY)
                                                                   Update:  September, 1989
Compound
Malononltrlle
subchronlc (RfD§)
chronic (RfD)
Mancozeb
subchronlc (RfOs)
chronic (RfO)
Maneb
subchronlc (RfOg)
chronic (RfO)
Manganese
subchronlc RfDg)
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 b 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 ppn In diet for
6 months (5 mg/kg/day)
NA; 300 ppm In diet for
6 months (5 mg/kg/day)
0.3 mg/m3 occupational
(2.1 mg/day); 1050 ppm
Mn from Mn304 from
day 1 of gestation
through 224 days of age
(52.5 mg Mn/kg/day)
Species Effect of Concern Reference Dose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/i»3 (mg/kg/day)) (mg/kg/day)
NA rat NA; liver and ND 2E-4 NA 1000
spleen
NA rat NA; liver and ND 2E-5<* NA 1000
spleen
(also see
Table B)
NA rat NA; goltrogenlc ND 3E-2 NA 100
effects
NA rat NA; goltrogenlc ND 3E-2 NA 100
effects
NA monkey NA; Increased ND 5E-2 NA 100
thyroid weight
NA monkey NA; Increased ND 5E-2 NA 100
thyroid weight
human rat CNS; reproductive 1E-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; Maneb
Data Task Force,
1986; U.S. EPA,
1984, 1987
U.S. EPA, 1984/
Rohm and Haas
Co.. 1977; Maneb
Data Task Force,
1986; U.S. EPA,
1984. 1987
Sarlc et al.,
1977; U.S. EPA,
1984a,b/Laskey
et al.. 1982;
U.S. EPA.
1984a,b
0059h
A-50
11/24/89

-------
                           HEALTH EFFECTS ASSESSMENTS SUMMARY  TABLE  A:  SUBCHRONIC  AND  CHRONIC  TOXICITY  (OTHER THAN CARCINOGENICITY)
                                                                  Update:   September,  1989
Compound
Exposure
Inhalation; Oral
Species
Inhalation Oral
Effect of
Inhalation
Concern
; Oral

[mg/
Reference
Inhalation
m3 (mg/kg/day)]
Dose
Oral
(mg/kg/day)
Uncertainty
Inhalation
Factor
Oral
Reference
Inhalation/Oral
  chronic (RfD)         0.3 mg/m3 occupational     human
                        (2.1 mg/day);  1  mg
                        MnCl2.4 H20/l  for  >2
                        years (22 mg Mn/kg/day
                        day) 1n drinking water
MCPA (see 2-Nethyl-4-chlorophenoxyacet1c add)

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

MCPP (see 2-<2-Hethyl-4-chlorophenoxy)prop1on1c acid)
                                     rat      CNS;  CNS1
Mephosfolan
  subchronlc (RfOs)
  chronic (RfO)
Mercury, alkyl and
Inorganic
  subchronlc (RfD$)
  chronic (RfD)
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)
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
                                1E-3(3E-4J
                  2E-1
             100
100
rat      NA; liver and
         kidney weights,
         reduced plasma,
         RBC and brain
         chollnesterase
         activities

rat      NA; liver and kidney
         weights, reduced
         plasma, RBC and
         brain chollnesterase
         activities
human    NA; CNS effects
ND
9E-4
                                                                                                    NA
                                                                         100
ND
                                                                                                              9E-5
                                                                                                    NA
                                        1000
                                                                     NO
                  3E-4
                                                                                                    NA
                                                                          10
human    NA;  CNS effects
                                                                                            ND
                                                                                      3E-4a-r
                                                                                                                            NA
                                                                         10
Sarlc et al.,
1977; U.S.  EPA.
1984/Leung
et al., 1981;
Lai et al.,
1982c; U.S. EPA.
1984a,b
       U.S.  EPA,  1984/
       U.S.  EPA,  1984
                              U.S.  EPA,  1984/
                              U.S.  EPA,  1984
                              U.S.  EPA,  19BS/
                              Clarkson et al..
                              1976;  Nordberg
                              Strangart.  1976;
                              MHO,  1976;  U.S.
                              EPA.1980.  1984,
                              1985

                              U.S.  EPA,  1985/
                              Clarkson et al.,
                              1976;  Nordberg
                              Strangart,  1976;
                              WHO.  1976;  U.S.
                              EPA,1980,  1984,
                              1985
OOS9h
                                                     A-51
                                                                                                                                                 11/24/89

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                           HEALTH EFFECTS ASSESSMENTS  SUMMARY  TABLE  A:  SUBCHRONIC  AND CHRONIC  TOXICITV  (OTHER  THAN  CARCINOOENICITY)
                                                                  Update:   September,  1989
Compound
Mercury, mercurial
subchronlc (RfOg)








chronic (RfO)








Merphos
subchronlc (RfDg)




chronic (RfD)




Merphos oxide
subchronlc (RfD$)




chronic (RfD)




ExDOture Species
Inhalation; Oral Inhalation Oral

NA; several oral and NA rat
parenteral studies In
the Brown Norway rat






NA; several oral and NA rat
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



Effect of Concern Reference Dost Uncertainty factor
Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/»3 (fto/kg/day)] (*o/kg/day)

NA; kidney effects NO 3E-4 NA 1000








NA; kidney effects1 ND 3E-4J NA 1000









NA; ataxla, ND 3E-4 NA 100
delayed neuro-
toxlclty


NA; ataxla, NO 3E-5« NA 1000
delayed neuro-
toxlclty



NA; ataxla, ND 3E-4 NA 100
delayed neuro-
toxlclty


NA; ataxla, ND 3E-5* NA 1000
delayed neuro-
toxlclty


Reference
Inhalation/Oral

U.S. EPA, 1984/
FHzhugh
et al., 1950;
Dru et al.,
1978; Bernaudln
et al., 1981;
Andres, 1984;
U.S. EPA, 1987,
1988
U.S. EPA, 1984/
FUzhugh
et al., 1950;
Dru et al..
1976; Bernaudln
et al., 1981;
Andres, 1984;
U.S. EPA, 1987,
1988

U.S. EPA, 1987/
Abou-Oonla
et al.. 1980;
U.S. EPA, 1984.
1987
U.S. EPA, 1987/
Abou-Oonta
et al., 1980;
U.S. EPA, 1984,
1987

U.S. EPA. 1987/
Abou-Donia
et al., 1979;
U.S. EPA, 1984,
1987
U.S. EPA, 1987/
Abou-Oonla
et al., 1979;
U.S. EPA, 1984,
1987
0627h
A-52
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                           HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE  A:  SUBCHRONIC AND CHRONIC  TOXIC1TY  (OTHER  THAN  CARCINOGENIC ITY)
                                                                  Update:   September.  1989
Compound
Hethacrylonltrlle
subchronk (RfOg)







chronic (RfD)







Met homy 1
subchronk (RfDs)



chronic (RfOs)



Methoxychlor
subchronk (RfDs)


chronic (RfO)


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
5 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/mj) 7 hours/day
5 days/week for 90 days
(0.32 mg/kg/day)


NA; 100 ppm 1n 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


NA; 200 ppm (10 mg/kg/ NA rat
day In diet during
gestation
NA; 200 ppm (10 mg/kg/ NA rat
day) In diet during
gestation
Effect of Concern Reference Dose Uncertainty factor
Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
Increased SGOT and 7E-3 (2E-3)m lE-3b 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)"1 lE-4a>b 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; kidney lesions NO 3E-2 NA 100



NA; kidney lesions NO 3E-2a NA 100




NA; fetotoxlclty NO lE-1bb NA 100


NA; fetotoxlclty NO lE-l1'00 NA 100


Reference
Inhalation/Oral
Pozzanl et al. ,
1968; U.S. EPA,
1987b/Pozzan1
et al., 196B;
U.S. EPA, 1987b



Pozzant et al.,
1968; U.S. EPA,
1987b/Pozzan1
et al., 1968;
U.S. EPA, 1987b




U.S. EPA, 1988/
Kaplan and
Sherman, 1977;
U.S. EPA. 1988
U.S. EPA. 1988/
Kaplan and
Sherman, 1977;
U.S. EPA. 1988

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

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

0627h
A-53
01/11/90

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                           HEALTH  EFFECTS ASSESSMENTS  SUMMARY TABLE A: SUBCHRONIC AND CHRONIC TOXICITY (OTHER THAN CARC1NOGENICITY)
                                                                  Update:  September, 1989
Compound
2-Hethoxyethanol
subchronlc (RfOs)






chronic (RfD)






Exoosure
Inhalation; Oral
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)
rabbit rabbit fetotoxlclty and 1E-1 (3E-2)«.bo 1E-2D'bb 100 100
testlcular effects;
fetotoxlclty and
testlcular effects



rabbit rabbit fetotoxlclty and 1E-2 (3E-3)°.°D l£-3M,bb 1000 1000
testlcular effects;
fetotoxlclty and
testlcular effects
(also see Table B)



Reference
Inhalation/Oral
Miller et al.,
1982; U.S. EPA,
1986/Mlller
et al., 1982;
U.S. EPA, 1986



MHIer et al.,
1982; U.S. EPA,
1986/MHIer
et al., 1982;
U.S. EPA, 1986



2-Hethoxyethanol acetate
  subchronlc (RfOs)     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
  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;  rabbits
NA; rabbits
                    NA;  testlcular
                    degeneration
                       NO
                  2E-2°
NA; testlcular
degeneration
(also see Table B)
NO
2E-3b
              NA       100    U.S.  EPA,  1987/
                              Miller  et  al..
                              1982; U.S. EPA,
                              1987
NA      1000    U.S.  EPA, 1987/
                Miller et al.,
                1982; U.S. EPA,
                1987
subchronlc (RfD$)
NR; SOO mg/kg/day NA
methanol by gavage for
90 days x 74.08/32.04
(molecular weight ratio)
rat NA; liver NO
damage
10 NA 100 U.S. EPA, 19B6/
Toxlclty
Research Labora-
tory, 1986;
U.S. EPA, 1986
0627h
                                                                             A-54
                                                                                                                                                 11/28/89

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                           HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE  A:  SUBCHRONIC  AND  CHRONIC  TOXIC1TY  (OTHER  THAN CARCINOGENICJTY)
                                                                  Update:   September.  19B9
Compound
chronic (RfO)
Methyl acrylate
subchronlc (RfOg)
chronic (RfO)
Methyl bromide
subchronlc (RfO$)
chronic (RfO)
Methyl chloride
Methyl Chlorocarbonate
Exposure
Inhalation; Oral
NR; 500 mg/kg/day
methanol by gavage for
90 days x 74.08/32.04
(molecular weight ratio)
NA; 15 ppm (53 mg/m^)
x 6 hours/day x 5 days/
week for 2 years x 0.5
absorption factor
NA; 15 ppm (53 mg/m3)
x 6 hours/day x 5 days/
week for 2 years x 0.5
absorption factor
NA; 2 mg/kg/day x 5
days/week by gavage for
13 weeks
NA; 2 mg/kg/day x 5
days/week by gavage for
13 weeks


2-Hethyl-4-chlorophenoxy-
acetk add (MCPA)
subchronlc (RfDs) NA; 6 ppm In the diet
for 52 weeks (0.15 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; liver NO 199 NA 1000
damage (also see
Table B)
NA rat NA; no effect NO 3E-2 NA 100
NA rat NA; no effect NO 3E-2 NA 100
(also see Table B)
NA rat NA; eplthe- NO 1.4E-2 NA 100
Hal hyper -
plasla of fore-
stomach
NA rat NA; eplthe- NO 1.4E-3*.' NA 1000
Hal hyper -
plasla of fore-
stomach
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
(also see Table B)
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA dog NA; kidney and ND 5E-4 NA 300
and liver
Reference
Inhalation/Oral
U.S. EPA. 1986/
Toxldty
Research Labora-
tory, 1986;
U.S. EPA, 1966
U.S. EPA, 1987/
Kllmlsch and
Relnlnghaus,
1984; U.S. EPA.
1987
U.S. EPA, 1987/
Kllmlsch and
Relnlnghaus,
1984; U.S. EPA.
1987
U.S. EPA. 1986
Danse et al . ,
1984; U.S. EPA.
EPA, 1988
U.S. EPA. 1986
Danse et al..
1984; U.S. EPA.
EPA. 1988
U.S. EPA. 1986
U.S. EPA. 1989
U.S. EPA. 1988/
Industry Task
Force, 1986;
U.S. EPA. 1984.
1988
0627h
A-55
                                                                                                                                                 11/28/89

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                           HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE A: SUBCHRONIC AND CHRONIC TOX1CITY (OTHER THAN  CARCINOGENICITY)
                                                                   Update:   September, 1969
Compound
chronic (RfO)
Exposure
Inhalation; Oral
NA; 6 ppm In the diet
for 52 weeks (0.15 mg/
kg/day)
4-(2-Hethyl-4-chlorophenoxy)-
buturlc add (MCPB)
subchronlc (RfOs) NA; 12 mg/kg/day In the
diet for 13 weeks
chronic
NA; 12 mg/kg/day In the
diet for 13 weeks
2-(2-Methyl-4-ch1orophenoxy)-
proplonlc add (MCPP)
subchronlc (RfDs) NA; 50 ppm In the diet
for 90 days (3 mg/kg/
day)
chronic (RfO)
Methylcyclohexane
Hethylene bromide
subchronlc (RfO$)
NA; 50 ppm In the diet
for 90 days (3 mg/kg/
day)

NA; 25 ppm (17B mg/m^)
x 6 hours/day x 63 days/
90 days for 90 days x
0.5 absorption factor
(11.0 mg/kg/day)
Species
Inhalation Oral
NA dog
NA rat,
dog
NA rat,
dog
NA rat
NA rat
DATA
NA rat
Effect of Concern Reference Dose Uncertainty Factor
Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/i»3 (mg/kg/day)] (mg/kg/day)
NA; kidney and NO SE-4a NA 300
and liver
NA; reproductive NO 1E-1 NA 100
toxlclty In dogs,
liver and kidney
effects In rats
NA; reproductive NO 1E-28 NA 1000
toxlclty 1n dogs,
liver and kidney
effects 1n rats
NA; kidney weight ND 1E-2 NA 300
NA; kidney weight ND 1E-34 NA 3000
INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA; Increased ND IE-ID NA 100
carboxyhemoglobln
Reference
Inhalation/Oral
U.S. EPA, 1988/
Industry Task
Force, 1986;
U.S. EPA, 1984,
1988
U.S. EPA, 1987/
Rhodla Inc..
WOa.b;
U.S. EPA, 1984,
1987
U.S. EPA, 1987/
Rhodla Inc.,
1970a,b;
U.S. EPA, 1984,
1987
U.S. EPA, 1988/
BASF Akt., 1985;
U.S. EPA, 1984,
1988
U.S. EPA, 1988/
BASF Akt., 1985;
U.S. EPA, 1984.
1988
U.S. EPA, 1984
U.S. EPA, 1987/
Keyes et al.,
1982; U.S. EPA,
1987
0627h
A-56
                                                                                                                                                  11/28/89

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                           HEALTH  EFFECTS ASSESSMENTS SUMMARY TABU A: SUBCHRONIC AND CHROMIC TOXICITY (OTHER THAN CARCINOGfNICITY)
                                                                  Update:  September, 1989
Compound
Exposure
Inhalation; Oral
Species
Inhalation Oral
Effect of Concern
Inhalation; Oral
Reference Dose
Inhalation Oral
[mg/m3 (mg/kg/day)) (mg/kg/da
Uncertainty Factor
Inhalation Oral
y)
Reference
Inhalation/Oral
  chronic (RfO)
Hethylene chloride
(dUhloromethane)
  subchronlc (RfD$)
NA; 25 ppm (178 mg/m3)     NA
x 6 hours/day x 63 days/
90 days for 90 days x
0.5 absorption factor
(11.0 mg/kg/day)
200 ppm (694.8 mg/m3)      rat
6 hours/day, 5 days/week
for 2 years; 24-month
drinking water study
[5.85 mg/kg/day (males)
6.47 mg/kg/day (females)]
                                                            rat
rat
         NA;  Increased
         carboxyhemoglobln
         (also see
         Table B)
NA; liver  toxkUy;
                       NO
  chronic (RfO)
200 ppm (694.8 mg/m3)
6 hours/day. 5 days/week
for 2 years; 24-month
drinking water study
[5.85 mg/kg/day (males)
6.47 mg/kg/day (females)]
                                                  rat
rat
NA; liver toxlclty;
(Cancer:  see
Table B)
                                                                                            3J
4.4'-Methylened1phenyl
Isocyanate
                          DATA INADEQUATE  FOR  QUANTITATIVE RISK ASSESSMENT
lE-2b         NA      1000    U.S.  EPA.  1987/
                              Keyes et al.,
                              1982; U.S.  EPA,
                              1987
6E-2         100       100    NUschke et  al..
                              1988/ National
                              Coffee Associa-
                              tion. 1982;
                              U.S.  EPA. 1985
6E-2*        100       100    NUschke et  al.,
                              19B8;/Nat1ona)
                              Coffee  Associa-
                              tion, 1982;
                              U.S.  EPA.  1985
                                                                                                                                            U.S.  EPA.  1985
Methyl ethyl benzenes (see Ethyltoluene)
subchronlc (RfDg) 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)
chronic (RfO) 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)S 5E-)b>bb 100 100 LaBelle and
BMeger, 1955;
U.S. EPA. 1985/
LaBelle and
Brleger. 1955;
U.S. EPA. 1985.
1989
rat CNS; fetotoxlclty 3E-1 (9E-2)* 5E-2a>t>t1'bb1000 1000 LaBeJle and
Brleger. 1955;
U.S. EPA. 1985/
LaBelle and
Brleger. 1955;
U.S. EPA, 1985,
1989
062/h
                                                    A-57
                                                                                                                                                 12/01/89

-------
                           HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE  A:  SUBCHRON1C  AND CHRONIC  TOXICITY (OTHER  THAN  CARCINOGENICITY)
                                                                   Update:   September.  1989
Compound
Methyl Isobutyl ketone
subchronlc (RfD$)
chronic (RfD)
Methyl Isocyanate
Methyl methacrylate
subchronlc (RfD$)
chronic (RfO)
Methyl parathlon
subchronlc (RfD§)
chronic (RfD)
Exposure
Inhalation; Oral
SO ppm (205 mg/m3)
6 hours/day, 5 days/
week for 90 days
(23.3 mg/kg/day);
50 mg/kg/day by gavage
for 13 weeks
50 ppm (205 mg/m3)
6 hours/day. 5 days/
week for 90 days
(23.3 mg/kg/day);
50 mg/kg/day by gavage
for 13 weeks

NA; 60 ppm for 4 months
then 70 ppm for 20
months In drinking water
(7.5 mg/kg/day)
NA; 60 ppm for 4 months
then 70 ppm for 20
months In drinking water
(7.5 mg/kg/day)
NA; 0.5 ppm (0.025 mg/
kg/day) 1n diet for
2 years
NA; 0.5 ppm (0.025 mg/
kg/day) In diet for
2 years
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 liver and kidney 8E-1 (2E-1) 5E-1 100 100
effects; liver and
kidney effects
rat rat liver and kidney 8E-2 (2E-2) 5E-2* 1000 1000
effects; liver and
kidney effects
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA rat NA; Increased NO 8E-2 NA 100
relative kidney
weight
NA rat NA; Increased NO 8E-20 NA 100
relative kidney
weight
(also see
Table B)
NA rat NA; reduced hemo- NO 2.5E-4 NA 100
globln, hematocrlt
and RBCs, cholln-
esterase Inhibition
NA rat NA; reduced hemo- NO 2.5E-48 NA 100
globln, hematocrlt
and RBCs, cholln-
esterase Inhibition
Reference
Inhalation/Oral
Union Carbide
Corp., 1983b;
U.S. EPA, 1987/
Microbiological
Associates,
1986; U.S. EPA,
1987
Union Carbide
Corp., 1983b;
U.S. EPA, 1987/
Microbiological
Associates,
1986; U.S. EPA,
1986, 1987
U.S. EPA, 1986
U.S. EPA, 1985/
Borgelleca
et al.. 1964;
U.S. EPA, 1985
U.S. EPA, 1985/
Borgelleca
et al., 1964;
U.S. EPA. 1985
U.S. EPA. 1984/
Monsanto Co. .
1983; U.S. EPA,
1986
U.S. EPA, 1984/
Monsanto Co.,
1983; U.S. EPA.
1986
0627h
A-58
11/28/89

-------
                           HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE A: SUBCHRONIC AND CHRONIC TOXIC1TY (OTHER THAN CARCINOGENICITY)
                                                                   Update:   September, 1989
Compound
Hcthyl styrene
(Industrial mixture)
subchronlc (RfDj)





chronic






Methyl styrene, alpha
subchronlc (RfDg)




chronic (RfD)
subchronlc (RfDj)



Exposure Species
Inhalation; Oral Inhalation Oral


10 ppm (48.3 mg/m3) 6 mouse mouse
hours/day, 5 days/week
for 103 weeks (11.2 rag/
kg/day): 10 ppm (48.3
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

970 mg/m3, 7.5 hours/ rat NA
day, 5 days/week for
200 days (69 mg/kg/day);
NA

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


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




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






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



liver and kidney; ND 7E-2b NA 1000
NA



Reference
Inhalation/Oral


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


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




U.S. EPA. 1987;
Wolf et al..
1956/U.S. EPA,
1987; Wolf
et al., 1956
U.S. EPA. 1987;
Wolf et al..
1956/U.S. EPA,
1987; Wolf
et a}., 1956
N1rex
  subchronlc (RfDj)
  chronic (RfD)
NA; 0.1 ppm 1n diet,
mu1t1generat1onal study
(0.015 mg/kg/day)
NA
NA; 0.1 ppm 1n diet.      NA
onuH1 generational study
(0.015 mg/kg/day)
prairie  NA; decreased pup      NO
vole     survival
           prairie  NA;  decreased pup      ND
           vole     survival  (Cancer:
                    see  Table B)
2E-6
                                                  2£-6a
NA    10,000
              NA    10,000
U.S. EPA, 1987a/
Shannon, 1976;
U.S. EPA, 1987b

U.S. EPA, 1987a/
Shannon, 1976;
U.S. EPA, 1987b
0627h
                                                     A-59
                                                                                                11/28/89

-------
                           HEALTH EfffCrS ASSESSMENTS SUMMARY TABLE A:  SUBCHRONIC AND CHRONIC TOXICITY (OTHER THAN CARCINOGENICITY)
                                                                   Update:   September, 1989
Compound
Mollnate
subchronlc (RfOj)




chronic (RfO)




Honochlorobutanes
subchronlc (RfOg)



chronic (RfO)


Naphthalene
subchronlc (RfDj)



chronic (RfD)



1.4-Naphthoqu1none
Nickel
subchronlc (RfD$)



chronic (RfD)



Exposure
Inhalation; Oral

NA; 0.2 mg/kg/day by
gavage



NA; 0.2 mg/kg/day by
gavage




NA; 120 ing/kg. 5 days/
week for 13 weeks by
gavage

NA; 60 ing/kg, 5 days/
week for 103 weeks by
gavage

NA; 10-20 mg/day 1n
diet 6 days/week for
=700 days (41 mg/kg/
day)*
NA; 10-20 mg/day 1n diet
6 days/week for =700
days (41 mg/kg/day)5



NA; 100 ppm N1 from
nickel sulfate In diet
for 2 years
(5 mg N1 /kg/day)
NA; 100 ppm N1 from
nickel sulfate In
diet for 2 years
(S mg N1/kg/day)
Species
Inhalation Oral

NA rat




NA rat





NA rat



NA rat



NA rat



NA rat



DATA

NA rat



NA rat



Effect of Concern Reference Dose Uncertainty factor
Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/n>3 (mg/kg/day)] (mg/kg/day)

NA; reporducMve NO 2E-3 NA 100
toxldty



NA; repor due live NO 2E-3a NA 100
toxldty




NA; reduced body NO 9E-1 NA 100
weight gain;
hyperaetlvlty.
convulsions
NA; mortality NO 4E-1 NA 100



NA; ocular and ND 4E-3* NA 10000
Internal lesions


NA; ocular and ND 4E-39.t NA 10000
Internal lesions


INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT (also see Table B)

cancer; reduced NO 2E-2 NA 300
body and organ
weight

cancer (see Table ND 2E-2* NA 300
B); reduced body
and organ weight

Reference
Inhalation/Oral

U.S. EPA, 1984/
Stauffer
Chemical Co.,
1981; U.S. EPA,
1988
U.S. EPA, 1984/
Stauffer
Chemical Co.,
1981; U.S. EPA.
1988

U.S. EPA, 1989/
NTP, 1986; U.S.
EPA. 1989

U.S. EPA, 1989/
NTP, 1986; U.S.
EPA. 1989

U.S. EPA. 198B/
Schmahl, 1955;
U.S. EPA, 1988

U.S. EPA, 1988/
Schmahl, 1955;
U.S. EPA, 1986;
1988
U.S. EPA. 1986

U.S. EPA, 1984/
Ambrose
et al., 1976;
U.S. EPA, 1987
U.S. EPA, 1984/
Ambrose
et al., 1976;
U.S. EPA. 1987
0627h
A-60
11/28/89

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                           HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE  A:  SUBCHRON1C  AND  CHRONIC  TOXICITY  (OTHER THAN CARCINOGENICITY)
                                                                  Update:   September.  1989
Compound
NUottnonttrtle
Nitrite
subchronlc (RfDs)
chronic (RfD)
N1 troan! lines (o-, m-,
Nitrobenzene
subchronlc (RfOg)
chronic (RfD)
Nltrofurantoln
Subchronlc (RfDs)
chronic RfO
NUrofurans. other: see
txpu&fl-e
Inhalation; Oral

NA; 10 ppm nitrate In
drinking water
NA; 10 ppm nitrate In
drinking water
P-)
5 ppro (25 mg/m3)
6 hours/day, 5 days/
week for 90 days
(HEC-4.5 mg/ffl3!;
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
(H£C=4.5 mg/m3);
5 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)
Table B
fifties 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 human NA; methemoglo- NO 1E-1 NA 10
blnemla
NA human NA; methemoglo- NO 1E-T NA 10
blnemla
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
mouse mouse hematologlcal, 2E-2 (6E-3) 5E-3b 300 1000
adrenal, renal and
hepatic lesions;
hematologlcal,
adrenal, renal and
hepatic lesions;
mouse mouse hematologlcal. 2E-3J (6E-4) 5E-4b>z 3000 10.000
adrenal, renal and
hepatic lesions;
hematologlcal,
adrenal, renal and
hepatic lesions;
NA mouse NA; testlcular NO 7E-1 NA 100
damage
NA mouse NA; testlcular NO 7E-2 NA 1000
damage

Reference
Inhalation/Oral
U.S. EPA. 1967
U.S. EPA. 1989/
Walton. 1951;
U.S. EPA, 1986.
1989
U.S. EPA. 1989/
Walton. 1951;
U.S. EPA. 1986.
1989
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
U.S. EPA. 1987/
SRI. 1980;
U.S. EPA. 1987
U.S. EPA, 1987/
SRI, 1980;
U.S. £PA. 1987

0627H
A-61
12/01/89

-------
HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE  A:  SUBCHRONIC  AND  CHRONIC  TOX1CITY  (OTHER  THAN CARC1NOGEN1CITY)
                                        Update:   September,  1969
Compound
Nitrogen oxides
Nltromethane
Nltrophenols
p-N1trosod1phenylam1ne
Nltrotoluenes (o-. m-,
subchronlc (RfD$)
chronic (RfD)
Oc tame thy Ipyrophos-
phoramlne
subchronlc (RfD$)
chronic (RfO)
Octobromodlphenyl ether
subchronlc (RfOg)
chronic (RfO)
Ozone and other
photochemical oxldants
0627h
Exposure
Inhalation; Oral




P-)
NA; 200 mg/kg/day
o-nltrotoluene x
5 days/week by gavage
for 6 months
NA; 200 mg/kg/day
o-nltrotoluene 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)
NA; 2.5 mg/kg/day by
gavage for 90 days
NA; 2.5 mg/kg/day by
gavage for 90 days


Species Effect of Concern Reference Dose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
[rng/rn3 (mg/kg/day)] (mg/kg/day)
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 NO 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
NA rat NA; liver NO 3E-2 NA 100
histology
NA rat NA; liver ND 3E-3a NA 1000
histology
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
A-62
Reference
Inhalation/Oral
U.S. EPA, 1982
U.S. EPA, 1965
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
U.S. EPA, 1986/
Carlson, 1980;
U.S. EPA, 1983.
1986
U.S. EPA, 1986/
Carlson, 1980;
U.S. EPA, 1983,
1986
U.S. EPA, 1986
11/28/89

-------
                           HEALTH EFFECTS  ASSESSMENTS  SUMMARY  TABLE  A:  SUBCHRONIC  AND  CHRONIC  TOXICITY  (OTHER  THAN CARCINOGENICITY)
                                                                  Update:   September.  1989
Exposure Specie* Effect of Concern Reference Dose Uncertainty factor Reference
Compound
Paraldehyde
Parathlon
subchronlc (RfDg)
chronic (RfD)
Partlculate matter
and sulfur oxides
Pebulate
subchronlc (RfD$)
chronic (RfD)
Pend1methal1n
subchronlc (RfD$)
chronic (RfD)
Pentabromodlphenyl
subchronlc (RfDs)
chronic (RfD)
Inhalation; Oral Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral Inhalation/Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)

NA; CBI NA
NA; CBI NA

NA; 5 mg/kg/day NA
subchronlc feeding
study
NA; 5 mg/kg/day NA
subchronlc feeding
study
NA; 12.5 mg/kg/day, NA
7 days/week 1n capsules
for 2 years
NA; 12.5 mg/kg/day, NA
7 days/week In capsules
for 2 years
ether
NA; 1.8 mg/kg/day by NA
gavage for 90 days
NA; 1.8 mg/kg/day by NA
gavage for 90 days
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT (also see Table B)
human NA; chollnesterase ND 6E-3 NA
Inhibition
human NA; chollnesterase ND 6E-39 NA
Inhibition, cancer"
RISK ASSESSMENT VALUES NOT DERIVED
rat NA; anticoagulant ND 5E-2 NA
effects
rat NA; anticoagulant ND 5E-2 NA
effects
dog NA; liver ND 4E-2 NA
dog NA; liver ND 4E-2a NA
rat NA; liver ND 2E-2 NA
enzymes
rat NA; liver NO 2E-3a ' NA
enzymes
U.S. EPA,
10 U.S. EPA.
U.S. EPA,
10 U.S. EPA,
U.S. EPA,
U.S. EPA,
100 U.S. EPA,
U.S. EPA,
100 U.S. EPA,
U.S. EPA.
300 U.S. EPA,
American
Cyan1m1d,
U.S. EPA,
1987
300 U.S. EPA.
American
Cyanlmld,
U.S. EPA,
1987
100 U.S. EPA.
Carlson,
U.S. EPA.
1986
1000 U.S. EPA,
Carlson,
U.S. EPA,
1986
1986
1987/
1987
1987/
1987
1982
1984/
1984
1984/
1984
1987/
1979;
1984.
1987/
1979;
1984,
1986/
1980;
1983,
1986/
1980;
1983.
0627h
A-63
                                                                     11/28/89

-------
                           HIAI )H UflCIS ASSlbSMlNIS SUMMARY IABIF  A:  SUBCMRONIC AND CHRONIC lOXILIIt (UIHtH I HAN CARCINUUt NIU I Y )
                                                                   Update:   September,  1969
                              txposure
      Compound
  inhalation; Oral
                              Species
                                                 Inhalation  Oral
        iffeet of Concern
        Inhalation; Oral
         Reference Dose
    Inhalation         Oral       Inhalation
[mg/m3 (mg/kg/day))  (mg/kg/day)
      or   	Reference
    Oral   Inhalation/Oral
Pentachlorobenzene
  subchronlc (RfO$)     NA.  83 mg/kg/day In       NA
                        the  diet for 100 days
  chronic (RfD)         NA;  83 mg/kg/day In       NA
                        the  diet for 100 days
Pentachlorocyclopentadlene

Pentachloronttroben/ene
  subchronlc (RfOs)     NA;  30 ppm (0.7S mg/kg/   NA
                        day) In diet for ? years
  chronic (RfO)
Pentachlorophenol
  subchronlc (HfOs)
  chronic (RfO)
NA; 30 ppm (0.75 mg/kg/   NA
day) In diet for 2 years
NA; 3 mg/kg/day by        NA
gavage 6? days before
mating through gestation
NA; 3 mg/kg/day by        NA
gavage for 22-24 months
1,1,2,3,3-Pentachloropropene

n-Pentane

Phenanthrene
                                     rat      NA; liver and kidney   NO
                                              toxlclty
                                     rat      NA; liver and kidney   NO
                                              toxlclty
                                     OA1A INADEQUATE  FOR QUANTITATIVE RISK ASSESSMENT
                                     dog      NA;  liver toxlclty     NO
dog      NA; liver toxlclty     NO
         (Cancer:  see
         lable B)
rat      NA; fetotoxlclty       NO
rat      NA; liver and          ND
         kidney pathology
                                     DATA INADEQUATE  FOR QUAN111A1IVE  RISK ASSESSMENT

                                     DATA INADEQUATE  FOR QUANT NATIVE  RISK ASSESSMENT

                                     DATA INADEQUATE  FOR QUANTITATIVE  RISK ASSESSMENT
                                                  8E-3
                                                  8E
                                                  3F-3
                       31  3a
                       3E-2Db
                       3E-2a
                                     NA
                                     NA
  1000    U.S.  EPA.  1989/
          Llnder.  1980;
          U.S.  EPA.  1985.
          1989

10.000    U.S.  EPA,  1989/
          Llnder.  1980;
          U.S.  EPA,  1985,
          1989

          U.S.  {PA.  1988
NA



NA



NA
300 U.S.
Olln
1968
1987
300 U.S.
Olln
1968
1987
100 U.S.
EPA, 1986/
Corp .
; U.S. FPA.

tt'A. I986/
Corp. ,
; U.S. EPA,

EPA. 1984/
Schwet/ et al.,


NA
1978
1984
100 U.S.
; U.S. EPA,
. 1985. 1986
EPA. 1984/
Schwet/ et al . ,






1978
1984
U.S.
U.S.
U.S.
1987
; U.S. EPA.
, 1985, 1986
EPA. 1983
EPA, 1987
EPA, 1984.

06?/h
                                                                             A M
                                                                                                                          12/29/89

-------
                           HEALTH EFFECTS ASSESSMENTS SUMMARY  TABLE  A:  SUBCHRONIC  AND  CHRONIC  TOXICITY  (OTHER  THAN CARCINOGENIC1TY)
                                                                  Update:   September,  1969
Exposure Species Effect of Concern Reference Dose Uncertainty Factor Reference
Compound
Phenol
subchronlc (RfDg)




chronic (RfD)


Inhalation; Oral Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral Inhalation/Oral
[mg/m3 {mg/kg/day)] (mg/kg/day)

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


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

rat NA; reduced ND
fetal body
weight


rat NA; reduced ND
fetal body
weight

6E-lbb NA 100 U.S. EPA,
Research
Triangle
Institute,
U.S. EPA.
6E-ia,bb NA 100 U.S. EPA.
Research
Triangle

1984/


1983;
1988
1984/


Phenylened1am1nes (o-, p-)
                                     DATA INADEQUATE  FOR  QUANTITATIVE  RISK  ASSESSMENT  (Cancer:  see Table  B)
m-Phenylened1am1ne
  subchronlc (RfDg)
  chronic (RfD)
NA; 6.0 mg/kg/day for
90 days
NA; 6.0 mg/kg/day for
90 days
NA
NA
Phosgene

Phthallc acid esters, selected (see Table B)

Phthallc adds (o-. m-)

p-Phthallc add
rat      NA;  liver lesions      ND
rat      NA; liver lesions      ND
                                     DATA INADEQUATE  FOR  QUANTITATIVE  RISK  ASSESSMENT
                                     DATA INADEQUATE  FOR QUANTITATIVE  RISK  ASSESSMENT
6E-2
6E-3a
NA
NA
                                                                                           Institute,  1983;
                                                                                           U.S.  EPA,  1988

                                                                                           U.S.  EPA,  1985
 100    U.S.  EPA,  1985/
        Hofer and  Hruby,
        1982; U.S.  EPA,
        1986

1000    U.S.  EPA,  1985/
        Hofer and  Hruby,
        1982; U.S.  EPA,
        1986

        U.S.  EPA,  1984
                                                                                           U.S.  EPA.  1986
subchronlc (RfD$)
chronic (RfD)
NA; 142 mg/kg/day In NA
diet for 2 years
NA; 142 mg/kg/day 1n NA
diet for 2 years
rat NA; hyperplasla ND
of bladder uro-
thellum
rat NA; hyperplasla ND
of bladder uro-
t he 11 urn
lEtO NA 100 U.S. EPA. 1986/
CUT, 1983;
Gross, 1974;
U.S. EPA. 1986
1E+0 NA 100 U.S. EPA. 1986/
CUT, 1983;
Gross. 1974;
U.S. EPA, 1986
0627n
                                                     A-65
                                                                                                11/28/89

-------
HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE  A:  SUBCHRONIC AND CHRONIC TOXICHY (OTHER THAN CARCINOGEN1CITY)
                                        Update:   September, 1989
Compound
Phthaltc anhydride
subchronlc (RfOs)
chronic (RfO)
Polybromlnated
blphenyls
subchronlc (RfOs)
chronic (RfO)
Prof luralln
subchronlc (RfOs)
chronic (RfO)
Propachlor
subchronlc (RfOs)
chronic (RfD)
Propazlne
subchronlc (RfOs)
U^ut-u fyi
ikiMi 	 	 Effect flf ConctCfl Reference Dose Uncertalntv factor Reference
Inhalation; Oral Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral Inhalation/Oral
[rog/m3 (mg/kg/day)] (mg/kg/day)
NA; 12.019 ppm (1S62 NA
mg/kg/day) In diet for
104 weeks
NA; 12,019 ppm (1S62 NA
mg/kg/day) In diet for
104 weeks
NA; Flremaster FF-1 NA
0.1 mg/kg by gavage,
5 days/week for 25 weeks
(0.07 mg/kg/day)
NA; Flremaster FF-1 NA
0.1 mg/kg by gavage,
5 days/week for 25 weeks
(0.07 mg/kg/day)

NA; subchronlc feeding NA
study; no details
provided
NA; subchronlc feeding NA
study; no details
provided
NA; 13.3 mg/kg/day NA
1n the diet for 90 days
NA; 13.3 mg/kg/day NA
1n the diet for 90 days
NA; 100 ppm 1n the NA
diet for 2 years
(5 mg/kg/day)
mouse NA; lung and kidney ND
hlstopathology
mouse NA; lung and kidney ND
hlstopathology
(also see Table B)
rat NA; elevated liver ND
weight and liver
lesions
rat NA; elevated liver ND
weight and liver
lesions
(also see Table B)

rat NA; NA ND
rat NA; NA NO
rat NA; decreased body ND
weight gain
rat NA; decreased body ND
weight gain
rat NA; decreased body ND
weight gain
2EtO NA 1000 U.S. EPA, 1986/
NCI, 1979.
U.S. EPA. 1988
2E*Oa NA 1000 U.S. EPA, 1986/
NCI, 1979.
U.S. EPA, 1988
7E-5 NA 1000 U.S. EPA, 1989/
NTP, 1983; U.S.
EPA, 1989
7E-6 NA 10,000 U.S. EPA. 1989/
NTP, 1983; U.S.
EPA. 1989

6E-3 NA NA U.S. EPA. 1984/
U.S. EPA, 1984
6E-3 NA NA U.S. EPA, 1984/
U.S. EPA, 1984
1.3E-1 NA 100 U.S. EPA, 1984/
Monsanto, 1964;
U.S. EPA, 1984.
1986
1.3E-2* NA 1000 U.S. EPA, 1984/
Monsanto. 1964;
U.S. EPA, 1984,
1986
2E-2 NA 300 U.S. fPA, 1987/
Gelgy. 1980;
U.S. EPA, 1984.'
1987
                                                 A-66
                                                                                                                      12/01/89

-------
                           HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE  A:  SUBCHRONIC  AND CHRONIC  TOXICITY  (OTHER  THAN  CARCINOGENICITY)
                                                                   Update:   September,  19B9
Exposure Species Effect of Concern Reference Dose
Compound Inhalation; Oral Inhalation Oral Inhalation; Oral Inhalation Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
chronic (RfD) NA; 100 ppm In the NA
diet for 2 years
(5 mg/kg/day)
2-Propeno1c add (see Acrylic acid)
Proplonltrlle
n-Propyl alcohol
rat NA; decreased body ND 2t-?a
weight gain
(also see Table B)

DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
Uncertainty Factor Reference
Inhalation Oral Inhalation/Oral
NA 300 U.S.
Gelgy
U.S.
1987

U.S.
U.S.
EPA. 1987/
, 1980;
EPA, 1984.

EPA.
EPA,

1985
1987
Propylene glycol
  subchronk (RfD$)
  chronic (RfD)
170-350 mg/m3 (mean:       rat
260 mg/m3) contin-
uously for 18 months
(166 mg/kg/day);  6X 1n
diet for 20 weeks
(3 g/kg/day)

170-350 mg/m3 (mean:       rat
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)
rat      none observed;  renal    6E+0 (2E+0)
         lesions
dog      none observed;  de-
         crease 1n RBC,
         hematocrlt,  hemo-
         globin 1n dogs
6EtO (2E+0)
                               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
Propylene glycol
monoethyl ether
subchronk (RfDj)
chronic (RfD)
NA; 30-day drinking NA
water (680 mg/kg/day)
NA; 30-day drinking NA
water (680 mg/kg/day)
rat NA; reduced weight ND
gain
rat NA; reduced weight ND
gain
7E+0 NA 100 U.S. EPA, 1984/
Smyth and
Carpenter, 1948;
U.S. EPA. 1984
7E-1 NA 1000 U.S. EPA. 1984/
Smyth and
Carpenter, 1948;
U.S. FPA, 1984
0627h
                                                     A-67
                                                                                    11/28/89

-------
                           HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE  A:  SUBCHRONIC AND CHRONIC TOXICITY (OTHER THAN CARC1NOGENICITY)
                                                                   Update:   September,  1989
Compound
Propylene glycol
monomethyl ether
subchronlc RfOg)






chronic (RfD)





Pyrene
Pyrldlne
subchronlc (RfD$)


chronic (RfO)


RDX (Cyclonlte)
subchronlc (RfD$)



chronic (RfD)



Ronnel
subchronlc (RfDj)



Uptuut* SfittMC
Inhalation; Oral Inhalation


1000 ppn (3685 mg/ra3) rat
6 hours/day, 5 days/
week for 13 weeks
(489 mg/kg/day);
947 mg/kg, 5 days/week
for 35 days (676 mg/
kg/day) by gavage
1000 ppra (3685 mg/ra3) rat
6 hours/day, 5 days/
week for 13 weeks (489
mg/kg/day); 947 mg/kg,
5 days/week for 35 days
(676 mg/kg/day) by gavage


NA; 1 mg/kg/day by NA
gavage for 90 days

NA; 1 mg/kg/day by NA
gavage for 90 days


NA; 0.3 mg/kg/day NA
for 105 weeks


NA; 0.3 mg/kg/day NA
for 105 weeks



NA; 5 mg/kg/day In NA
the diet for 2 years


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


rat liver hlsto- 2Etl (SEfO) 7E+0 100
pathology; liver
and kidney hlsto-
pathology



rat liver hlsto- 2E*0 (5E-1) 7E-1 1000
pathology; liver
and kidney hlsto-
pathology


DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT

rat NA; Increased ND 1E-2 NA
liver weight

rat NA; Increased ND 1E-3' NA
liver weight


rat NA; prostate Inflam- ND 3E-3 NA
(nation, hemoslderosls


rat NA; prostate Inflam- ND 3E-3a NA
(nation, hemoslderosls



rat NA; liver and ND 5E-2 NA
effects


factor Reference
Oral Inhalation/Oral


100 Miller et al..
1984; U.S. EPA.
1984/Rowe
et al.. 1954;
U.S. EPA, 1984


1000 Miller et al..
1984; U.S. EPA.
1984/Rowe
et al.. 1954;
U.S. EPA. 1984

U.S. EPA. 1984

100 U.S. EPA, 1987/
U.S. EPA.
1986a.b
1000 U.S. EPA, 1987/
U.S. EPA,
1986a,b

100 U.S. EPA, 1989/
Levlne et al. ,
1984; U.S. EPA,
1988. 1989
100 U.S. EPA. 19B9/
Levlne et al. ,
1984; U.S. EPA,
1988. 1969

100 U.S. EPA, 1984/
McColllster
et al.. 1959;
U.S. EPA, 1984
0627h
A-6B
12/01/89

-------
                           HEALTH  EFFECTS  ASSESSMENTS  SUMMARY TABLE A: SUBCHRON1C AND CHRONIC TOXICITY (OTHER THAN CARCINOGENICITY)
                                                                  Update:  September, 1989
Compound
chronic (RfO)
Selenium
subchronlc (RfD$)
chronic (RfO)
Slmazlney
Sodium cyanide
subchronlc (RfO$)
chronic (RfD)
Sodium dlethyldHMo-
carbamate
subchronlc (RfD$)
chronic (RfO)
Exposure
Inhalation; Oral
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)
NA: 3.2 mg/day from
diet of selenlferous
foodstuffs (0.046
mg/kg/day)

NA; 10.8 mg CN/kg/day
from diet containing
HCN (equivalent to
NaCN at 20.4 mg/kg/day)
NA; 10.8 mg CN/kg/day
from diet containing
HCN (equivalent to
NaCN at 20.4 mg/kg/day)
NA; 30 mg/kg/day for
90 days
NA; 30 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; liver and NO 5E-29 NA 100
effects
NA human NO; hair and nail NO 3E-3 NA 15
loss, dermatitis
NA human ND; hair and nail NO 3E-3a>9 NA IS
loss, dermatitis
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA rat NA; CNS ND 4E-2 NA SOO
NA rat NA; CNS NO 4E-2a NA 500
NA rat NA; decreased body NO 3E-1 NA 100
weight gain, renal
and hemotologlcal
effects
NA rat NA; cataracts and NO 3E-2a NA 1000
reduced body weight
In chronic study
(Cancer: see
Table B)
Reference
Inhalation/Oral
U.S. EPA, 1984/
McColllster
et al., 1959;
U.S. EPA. 1984
U.S. EPA, 19B9/
Yang et al.,
1983; U.S. EPA.
1985. 1969
U.S. EPA. 1989/
Yang et al. ,
1983; U.S. EPA.
1985, 19B9
U.S. EPA, 19B4
U.S. EPA, 1984/
Howard and
Hanzal, 1955;
U.S. EPA, 1984
U.S. EPA, 1984/
Howard and
Hanzal, 1955;
U.S. EPA. 1984.
1985
U.S. EPA, 1988/
Sunderman
et al., 1967;
U.S. EPA, 1988
U.S. EPA. 1988/
Sunderman
et al., 1967;
U.S. EPA. 1985
1988
0627h
A-69
                                                                                                                                                 11/28/89

-------
                           HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE A: SUBCHRONIC AND CHRONIC TOXICITY (OTHER THAN CARCINOGENICITY)
                                                                   Update:  September, 1989
Compound
Sodium metavanadate
subchronlc (RfOg)




chronic (RfO)




Styrene
subchronk (RfD$)



chronic (RfD)



Exposure
Inhalation; Oral

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 1n drink-
Ing water for 3 months
(1.32 mg sodium meta-
vanadate/kg/day)

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; Impaired kidney NO 1E-2 NA 100
function



NA rat NA; Impaired kidney NO 1E-3 NA 1000
function




NA dog NA; red blood cell NO 2E*0 NA 100
and liver effects


NA dog NA; red blood cell NO 2E*1» NA 1000
and liver effects


Reference
Inhalation/Oral

U.S. EPA. 1987/
Domingo
et al., 1985;
U.S. EPA, 1987

U.S. EPA, 1987/
Domingo
et al.. 1985;
U.S. EPA, 1987


U.S. EPA. 1985/
Quast et al.,
1979; U.S. EPA,
1984. 1985
U.S. EPA, 1985/
Quast et al.,
1979; U.S. EPA,
1984, 1985
Stlrophos (see Tetrachlorvlnphos)
Succ1non1tr11e
Sulfurlc add
subchronlc (RfDg)


chronic (RfO)


Temephos
subchronlc (RfDg)





0.066-0.098 mg/m3
occupational; NA

0.066-0.098 mg/m3
occupational; NA


NA; 200 ppm In the diet
for 99 days (11-24
mg/kg/day)

DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT

human NA respiratory; NA NDV NO NA NA


human NA respiratory; NA NDV NO NA NA



NA rats NA; no effect ND 2E-1 NA 100



U.S. EPA, 1987

Carson et al . ,
1981; U.S. EPA,
1984/NA
Carson et al. ,
1981; U.S. EPA
1984/NA

U.S. EPA, 19B4/
Galnes et al..
1967; U.S. EPA,
1984
0627h
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                           HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE  A:  SUBCHRONIC AND CHRONIC  TOX1CITY (OTHER  THAN  CARCINOGENICITY)
                                                                  Update:   September,  1989
Exposure
Compound Inhalation; Oral
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 (RfO) NA; 0.01 mg/kg/day In
the diet for 6 months
TerephthalU acid
Tetrachloroazobenzene (TCAB)
Tetrachloroazoxybenzene (TCAOB)
Tetrachlorocyclopentadlene
Tetrachloroethylene
( perch loroe thy lene)
subchronlc (RfDs) NA; 20 mg/kg 5 days/week
for 6 weeks
(14 mg/kg/day)
chronic (RfO) NA; 20 mg/kg S days/week
for 6 weeks
(14 mg/kg/day)
Tetrachlorohydrazobenzene (TCHB)
2.3,4,6-Tetrachlorophenol
subchronJc (RfDs) NA; 25 mg/kg/day for
90 days
chronic (RfO) NA; 25 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 rats NA; no effect NO 2E-2 NA 1000
NA dog NA; no effect ND 1E-49 NA 100
NA dog NA; no effect ND 1E-49 NA 100
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA mouse NA; hepatotoxldty ND 1E-1 NA 100
NA mouse NA; hepatotoxldty NO 1E-2a NA 1000
(Cancer: see
Table B)
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA rat NA; Increased liver ND 3E-1 NA 100
weights and centM-
lobular hypertrophy
NA rat NA; Increased liver ND 3E-2a ' NA 1000
weights and centrl-
lobular hypertrophy
Reference
Inhalation/Oral
U.S. EPA. 1984/
Galnes et al.,
1967; U.S. EPA,
1964
U.S. EPA, 19B4/
U.S. EPA, 1984
U.S. EPA, 1984/
U.S. EPA. 1984
U.S. EPA, 1984
U.S. EPA. 1985
U.S. EPA. 1985
U.S. EPA. 1988
U.S. EPA, 19B8/
Buben and
O'Flaherty,
1985; U.S. EPA,
1987
U.S. EPA. 1988/
Buben and
O'Flaherty,
1985; U.S. EPA.
1987
U.S. EPA, 1985
U.S. FPA. 1987a/
U.S. EPA, 1986.
1987b
U.S. EPA, 1987a/
U.S. EPA. 1986.
1987b
0627h
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                           HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE A: SUBCHRONIC AND CHRONIC TOXICITY (OTHER THAN CARCINOGENIC1TY)
                                                                   Update:  September. 1989
       Compound
                              Exposure
   Inhalation; Oral
                              Species
Inhalation  Oral
        Effect of Concern
        Inhalation; Oral
                                                Reference  Dose
    Inhalation         Oral
[mg/m3 (mg/kg/day)]  (mg/kg/day)
Uncertainty Factor
Inhalation    Oral
                                                                                                                                                Reference
                                                                                            Inhalation/Oral
Tetrachlorophenol, 2,3,4,5-,
2,3.5,6-

1,1,2,3-Tetrachloropropene
Tetrachlorovlnphos
(Stlrofos)
  subchronlc  (RfD$)
Tetrachlorovlnphos
(Stlrofos)
  chronic (RfD)
Thalllc oxide
[Thalllum(III) oxide]
  subchronlc (RfD$)
  chronic (RfD)
NA; 12S ppm 1n the        NA
diet for 2 years
(3.1 mg/kg/day)
NA; 125 ppm In the        NA
diet for 2 years
(3.1 mg/kg/day)
NA; 0.02 mg thallium/kg/  NA
day (from thallium
sulfate) for 90 days
NA; 0.02 mg thallium/kg/  NA
day (from thallium
sulfate) for 90 days
Thallium (In soluble salts)
  subchronlc RfOs)      NA; 0.20 mg thallium/kg/  NA
                        day (from thallium
                        sulfate) for 90 days
  chronic (RfD)
Thalllum(I) acetate
  subchronlc (RfDg)
NA; 0.20 mg thallium/kg/
day (from thallium
sulfate) for 90 days
 NA
NA; 0.20 mg thallium/kg/  NA
day (from thallium
sulfate) for 90 days
                                     DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
                                     DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
            dog      NA;  Increased  liver     NO                3E-2
                     and  ktdney wetgnts,
                     reduced  body
                     weight gain
            dog       NA;  Increased  liver     ND                 3E-2*
                     and  kidney  weights,
                     reduced  body weight
                     gain (Cancer:  see
                     Table B)
            rat       NA;  Increased  SCOT      ND                 7E-4
                     and  serum  LOH
                     levels,  alopecia
            rat       NA;  Increased  SGOT      ND                 7E-5V
                     and  serum  LDH
                     levels, alopecia
rat      NA; Increased SGOT     ND                7E-4
         and serum LDH
         levels,  alopecia

rat      NA; Increased SGOT     ND                7E-5
         and serum LDH
         levels,  alopecia
           rat       NA;  Increased SGOT     ND                9E-4
                     and  serum LDH
                     levels, alopecia
                                                                                            U.S.  EPA,  1987


                                                                                            U.S.  EPA.  1983
                                                                NA       100    U.S.  EPA, 1986/
                                                                                She?? Chem.  Co..
                                                                                1968; U.S.  EPA,
                                                                                1984, 1986
                                                                NA       100    U.S.  EPA,  1986/
                                                                                Shell  Chem.  Co.,
                                                                                1968;  U.S.  EPA,
                                                                                1984,  1986
                                                                NA       300    U.S.  EPA.  1988a/
                                                                                MRI.  1986;
                                                                                U.S.  EPA.  1986b
                                                                                1988b

                                                                NA      3000    U.S.  EPA,  1988a/
                                                                                MRI,  1986;
                                                                                U.S.  EPA,  1986b
                                                                                19886
                                     NA        300     U.S. EPA,  1988a/
                                                     MRI, 1986;
                                                     U.S. EPA,  1986b

                                     NA       3000     U.S. EPA,  1988a/
                                                     MRI, 1986;
                                                     U.S. EPA,  19865
                                                                NA       300    U.S.  EPA.  1988a/
                                                                                MRI.  1986;
                                                                                U.S.  EPA,  1986b.
                                                                                1988b
0627h
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                           HEALTH EFFECTS ASSESSMENTS  SUMMARY  TABLE  A:  SUBCHRONIC  AND  CHRONIC  TOXIC1TY  (OTHER THAN CARCINOGENICITY)
                                                                  Update:   September.  1989
Compound
Exposure
Inhalation; Oral
Species
Inhalation Oral
Effect of
Inhalation
Concern
; Oral

Reference
Inhalation
[mg/ra3 (mg/kg/day)]
Dose
Oral
(mg/kg/day)
Uncertainty
Inhalation
Factor
Oral
Reference
Inhalation/Oral
  chronic (RfO)
NA; 0.20 mg thallium/kg/
day (from thallium
sulfate) for 90 days
                          NA         rat      NA;  Increased SGOT
                                              and  serum LDH
                                              levels,  alopecia
                                                                                             ND
                                                  9E-5«         NA      3000    U.S.  EPA,  1988a/
                                                                                MRI.  1986;
                                                                                U.S.  EPA.  1986b.
                                                                                19885
Thalllum(I) carbonate
  subchronlc (RfD$)
  chronic (RfD)
NA; 0.20 mg thallium/kg/
day (from thallium
sulfate) for 90 days
                          NA
NA; 0.20 mg thallium/kg/  NA
day (from thallium
sulfate) for 90 days
rat      NA; Increased SGOT     ND
         and serum LDH
         levels, alopecia
                                     rat      NA;  Increased SGOT     ND
                                              and  serum LDH
                                              levels,  alopecia
                                                                                       8E-4
                                                                                                               BE-5
              NA       300    U.S.  EPA.  1988a/
                              MRI.  1986;
                              U.S.  EPA.  1986b.
                              19B8b

              NA      3000    U.S.  EPA,  1988a/
                              MRI,  1966;
                              U.S.  EPA,  1986b,
                              1988b
Thal11um(I) chloride
  subchronlc (RfOj)
  chronic (RfD)
NA; 0.20 mg thai Mum/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;  Increased SGOT     NO
                                              and  serum LDH
                                              levels,  alopecia
                                              NA;  Increased SGOT     ND
                                              and  serum LDH
                                              levels,  alopecia
                                                  8E-4          NA       300    U.S.  EPA.  1988a/
                                                                                MRI.  1986;
                                                                                U.S.  EPA.  1986b,
                                                                                1988b

                                                  8E-5a          NA      3000    U.S.  EPA.  1988a/
                                                                                MRI.  1986;
                                                                                U.S.  EPA.  1986b.
                                                                                1988b
Thalllum(I) nitrate
  subchronlc (RfDj)
  chronic (RfO)
NA; 0.20 mg thallium/kg/
day (from thallium
sulfate) for 90 days
                          NA
NA; 0.20 mg thallium/kg/  NA
day (from thallium
sulfate) for 90 days
rat      NA; Increased SGOT     ND
         and serum LDH
         levels, alopecia
                                     rat      NA; Increased SGOT     ND
                                              and serum LDH
                                              levels,  alopecia
9E-4          NA       300    U.S.  EPA.  1988a/
                              MRI,  1986;
                              U.S.  EPA,  1986b.
                              1988b

9E-5a         NA      3000    U.S.  EPA.  1988a/
                              MRI.  1986;
                              U.S.  EPA,  1986b.
                              1988b
Thallium selenlte (Tl2Se)
  subchronlc (RfOs)     NA; 0.20 mg thallium/kg/  NA
                        day (from thallium
                        sulfate) for 90 days
                                     rat      NA; Increased SGOT
                                              and serum LDH
                                              levels, alopecia
                                                                     ND
                                                                                       9E-4
                                                                NA       300    U.S.  EPA,  1988a/
                                                                                MRI,  1986;
                                                                                U.S.  EPA.  1986b.
                                                                                1986b
0627h
                                                     A-73
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                           HEALTH EFFECTS ASSESSNENTS SUMMARY TABLE  A:  SUBCHRON1C AND CHRONIC TOXICITY (OTHER THAN CARCINOGENICITY)
                                                                   Update:   September,  1989
Compound
Thallium selenlte (T12Se
chronic (RfD)



Thall1um( I) sulfate
subchronlc (RfD$)



chronic (RfD)



2-(Th1ocyanomethylth1o)-
benzothlazole (TCHTB)
subchronk (RfD$)


chronic (RfD)


Thlofanox
subchronlc (RfDj)

chronic (RfO)

Thlram
subchronlc (RfOj)



chronic (RfD)



Exposure
Inhalation; Oral
)
NA; 0.20 mg thallium/kg/
day (from thallium
sulfate) for 90 days


NA; 0.25 mg/kg/day for
90 days


NA; 0.25 mg/kg/day for
90 days




NA; 333 ppffl 1n the diet
diet, subchronlc (25 mg/
kg/day)
NA; 333 ppm In the diet
diet, subchronlc (25 mg/
kg/day)

NA; 0.025 mg/kg/day
for 8 days
NA; 0.025 mg/kg/day
for 8 days

NA; 0.61 mg/kg/day
for 24 weeks


NA; 0.61 mg/kg/day
for 24 weeks


Species Effect of Concern
Inhalation Oral Inhalation; Oral

NA rat NA; Increased SCOT
and serum LDH
levels, alopecia


NA rat NA; Increased SCOT
and serum LOH
levels, alopecia

NA rat NA; Increased SGOT
and serum LOH
levels, alopecia



NA rats NA; stomach
lesions

NA rats NA; stomach
lesions


NA dog NA; chollnesterase
Inhibition
NA dog NA; chollnesterase
Inhibition

NA ferret NA; Impaired
reproduction


NA ferret NA; Impaired
reproduction


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

ND 9E-5* NA 3000




NO BE -4 NA 300



NO 8E-5a NA 3000





ND 3E-1 NA 100


ND 3E-2 NA 1000



NO 3E-4 NA 100

NO 3E-49 NA 100


ND 6E-3 NA 100



ND 6E-3a NA 100



Reference
Inhalation/Oral

U.S. EPA, 1988a/
MRI, 1986;
U.S. EPA. 19866,
1988b

U.S. EPA. 1988a/
HRI, 1986;
U.S. EPA, 1986b,
1988b
U.S. EPA. 1988a/
HRI, 1986;
U.S. EPA. 1986b,
1988b


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. 19B9/
U.S. EPA, 1989

U.S. EPA, 1989/
Hornshaw et al . ,
1987; U.S. EPA,
1987, 1989
U.S. EPA. 1989/
Hornshaw et al . ,
1987; U.S. EPA,
1987, 1989
0627h
A-74
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                           HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE  A:  SUBCHRONIC  AND  CHRONIC  TOXICITY  (OTHER  THAN  CARCIN06ENICHY)
                                                                  Update:   September.  1989
Compound
Tin and Compounds
subchronlc (RfO$)
chronic (RfO)
Toluene
subchronlc (RfDs)
Exposure Species
Inhalation; Oral Inhalation Oral
NA; 2000 ppm stannous NA rat
chloride 1n diet for 2
years (62 mg Sn/kg/day)
NA; 2000 ppm stannous NA rat
chloride In diet for 2
years (62 mg Sn/kg/day)
40 ppm for 6 hours human rat
Effect of Concern
Inhalation; Oral
NA; liver and
kidney lesions
NA; liver and
kidney lesions
CNS effects, eyes
Reference
Inhalation
[mg/m3 (mg/kg/day)]
ND
ND
2E*0
Dose
Oral
(mg/kg/day)
6E-1
6E-1
4E-1
Uncertainty
Inhalation
NA
NA
100
Factor
Oral
100
100
100
Reference
Inhalation/Oral
U.S. EPA, 1987/
NTP. 1982;
U.S. EPA. 1987
U.S. EPA, 1987/
NTP, 1982;
U.S. EPA, 1987
Andersen et al. ,
  chronic (RfO)
                        (151  mg/m3);
                        590 mg/day 5  days/week
                        for 138 doses (42 mg/
                        kg/day) by gavage
40 ppm for 6 hours
(151 mg/m3);
300 ppm (1130 mg/m3)
6 hours/day, 5 days/
week for 24 months
(29 mg/kg/day)b
                                                  human
                                                             rat
                                              and nose Irritation;
                                              CNS effects
                    CNS effects,  eyes      2E*Ol
                    and nose Irritation;
                    CNS effects1
                                                                                       3E-lb'z
Toluenedlamlne (2,3-, 3,4-)
                                     DATA INADEQUATE  FOR QUANTITATIVE  RISK  ASSESSMENT
Toluene-2,5-d1am1ne
  subchronlc (RfDs)
  chronic (RfO)
Toluene-2.6-d1am1ne
  subchronlc (RfDs)
NA; 2000 ppm of the
sulfate salt 1n the
diet for 78 weeks
(56 mg/kg/day)

NA; 2000 ppm of the
sulfate salt In the
diet for 78 weeks
(56 mg/kg/day)
NA; 500 ppm of the
dlhydrochlorlde In the
diet for 2 years (16
mg/kg/day)
NA
NA
NA
rat      NA;  no effect
rat      NA;  no effect
rat      NA; no effect
                                                                     ND
                                                                                             ND
                                                                     ND
                                                             6E-1
                                                             6E-1
                                                             2E-1
                                                                                1983;
                                                                                CUT.  1980;
                                                                                U.S. EPA,  1984/
                                                                                Wolf et  al..
                                                                                1956

                                                               100        100    Andersen et al..
                                                                                1983;
                                                                                CUT,  1980;
                                                                                U.S. EPA,  1984/
                                                                                CUT,  1980
                                                                                U.S. EPA,  1984.
                                                                                1985a,b

                                                                                U.S. EPA.  1984
NA       100    U.S. EPA. 1984/
                NCI, 1978;
                U.S. EPA, 1984
NA       100    U.S.  EPA, 1984/
                NCI,  1978;
                U.S.  EPA, 1984
NA       100    U.S.  EPA,  1984/
                NCI,  1980;
                U.S.  EPA,  1980
0627h
                                                                             A-75
                                                                                                                                                 11/28/89

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                           HEALTH EFFECTS ASSESSMENTS  SUMMARY TABLE A: SUBCHRON1C AND CHRONIC TOXICITY (OTHER THAN CARCINOGENICITY)
                                                                  Update:  September, 1989
Compound
chronic (RfO)
n-Toluldlne
TMallate
subchronlc (RfOg)
chronic (RfO)
1 ,2,4-TMbromobenzene
subchronlc (RfDj
chronic (RfO)
Exposure
Inhalation; Oral
NA; 500 ppm of the
dlhydrochlorlde In the
diet for 2 years (16
mg/kg/day)

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 1n the
diet for 45 or 90 days
Species Effect of Concern Reference Dose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/nfl (mg/kg/day)] (mg/kg/day)
NA rat NA; no effect ND 2E-1 NA 100
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
NA dog NA; spleen and NO 1.3E-2 NA 100
and liver
NA dog NA; spleen and liver ND 1.3E-2" NA 100
and liver
NA rat NA; liver weight ND 5E-2 NA 100
and enzyme
Induction
NA rat NA; liver weight ND 5E-3* NA 1000
and enzyme
Induction
Reference
Inhalation/Oral
U.S. EPA, 1984/
NCI, 1980;
U.S. EPA, 1980
U.S. EPA, 1984
U.S. EPA, 1986/
Monsanto Co.,
1979; U.S. EPA,
1986
U.S. EPA, 1986/
Monsanto Co.,
1979; U.S. EPA,
1986
U.S. EPA, 1986/
Carlson and
Tardlff, 1977;
U.S. EPA, 1984,
1986
U.S. EPA, 1986/
Carlson and
Tardlff. 1977;
U.S. EPA. 1984.
1986
TMbromome thane (see Bromoform)

1,2,4-TMchlorobenzene
  subchronlc (RfD$)      3 ppm (22 mg/ra3)  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-       9E-2 (3E-2)
                    phyrAn;  Increased
                    llver-to-body
                    weight ratio
2E-1
100       100    Watanabe et  al.,
                 1978;  U.S. EPA.
                 1987/Carlson and
                 Tardlff. 1976;
                 U.S.  EPA.  1987
06?7h
                           A-76
                                                                                                                                                 11/28/89

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                           HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE  A:  SUBCHRONIC  AMD  CHRONIC  TOXICITY  (OTHER  THAN CARCINOGENICITY)
                                                                  Update:   September.  1989
      Compound
                              Exposure
  Inhalation; Oral
                              Species
                                                 Inhalation  Oral
                   Effect of Concern
                   Inhalation;  Oral
         Reference Dose
    Inhalation         Oral
[mg/m3 (mg/kg/day)]  (mg/kg/day)
          Uncertainty Factor     Reference
          Inhalation    Oral  Inhalation/Oral
  chronic (RfO)
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
Trlchlorocyclopentadlene
rat        rat      Increased uropor-
                    phyrln;  Increased
                    llver-to-body
                    weight ratio
     9E-3 (3E-3)
                                     DATA INADEQUATE  FOR QUANTITATIVE  RISK ASSESSMENT
2E-2V       1000      1000    Uatanabe et al..
                              1978; U.S.  EPA.
                              1987/Carlson and
                              Tardlff, 1976;
                              U.S.  EPA. 1986.
                              1987

                              U.S.  EPA. 1988
subchronlc (RfDg) 500 ppra (2730 mg/m3) guinea
7 hours/day, 5 days/ pig
week for 6 months
(304 mg/kg/day); 500
ppm (2730 mg/m3) 7
hours/day for 6 months
(90 mg/kg/daylb
chronic (RfO) 500 ppm (2730 mg/m3) guinea
7 hours/day. 5 days/ pig
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-TMchloroethane
subchronlc (RfOs) NA; 3.9 mg/kg/day by NA
drinking water for 90
days


chronic (RfO) NA; 3.9 mg/kg/day by NA
drinking water for 90
days


Trlchlorofluoromethane (F-11)
subchronlc (RfDs) 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)
guinea hepatotoxldty; 1E + 1 (3E*0)S
pig hepatotoxldty




guinea hepatotoxldty: 1E+0 (3E-1)S
pig hepatotoxldty'





mouse NA; clinical NO
chemistry altera-
tions


mouse NA; clinical ND
chemistry altera-
tions (Cancer:
see Table B)


rat elevated BUN. lung 7EtO (2E+0)
lesions; mortality




9E-1D 100 100 Torkelson et
al.. 1958;
U.S. EPA, 1986/
Torkelson et
al.. 1958;
U.S. EPA, 1986

9E-2a-b 1000 1000 Torkelson et
al., 1958;
U.S. EPA, 1986/
Torkelson et
al.. 1958;
U.S. EPA. 1986


4E-2 NA 100 U.S. EPA, 1984/
White et al..
1985; Sanders
et al.. 1985;
U.S. EPA. 1988
4E-33 NA 1000 U.S. EPA. 1984/
White et al.,
1985; Sanders
et al., 1985;
U.S. £PA, 1988

7E-1 -1000 1000 Jenkins et al..
1970; U.S. EPA.
1987/NCI. 1978;
U.S. EPA, 1987


                                                                             A-77
                                                                                                                                                 11/28/89

-------
                           HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE A: SUBCHRONIC AND CHRONIC TOX1CITY (OTHER THAN CARCINOGENICITY)
                                                                   Update:  September, 19B9
Compound
chronic (RfD)
2,4,4'Trlchloro-
2'-hydroxyd1pheny1 ether
subchronlc (RfO$)
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)
NA; 500 mg/kg. 6 days/
week for 4 weeks (429
mg/kg/day)
NA; NA
Species Effect of Concern Reference Oose Uncertainty Factor
Inhalation Oral Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day )J (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
Reference
Inhalation/Oral
Jenkins et al.,
1970; U.S. EPA.
1987/NCI, 1978;
U.S. EPA. 1985,
1987
U.S. EPA, 1987/
Lyman and
FuMa, 1969;
U.S. EPA. 1987
U.S. EPA, 1987/
U.S. EPA, 1987
Trlchloromethane (see Chloroform)
Trlchlorophenol, 2,3.4-.
2.3,6-, and 3,4,5-
2,4.5-Trkhlorophenol
subchronlc (RfDg)
chronic (RfO)
2,4,6-Trlchlorophenol -
1,1,1-Trlchloropropane
1,2,2-Trkhloropropane
2,3,5-,
NA; 1000 ppm of diet
for 98 days (100 mg/
kg/day)
NA; 1000 ppm of diet
for 98 days (100 mg/
kg/day)
see Table B


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

DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
U.S. EPA, 1987
U.S. EPA. 1984.
1987/McColllster
et al., 1961;
U.S. EPA. 1984.
1987
U.S. EPA, 1984,
1987/McColllster
et al.. 1961;
U.S. EPA. 1984,
1985. 1987

U.S. EPA. 1987/
U.S. EPA. 1987
U.S. EPA. 1987/
U.S. EPA. 1987
0627h
A-78
11/28/89

-------
HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE  A:  SUBCHRONIC  AND  CHRONIC  TOXICITY  (OTHER  THAN CARCINOGENICITY)
                                       Update:   September.  1989
Compound
1,1.2-TMchloropropane
subchronlc (RfOs)
chronic (RfD)
1 ,2,3-Trlchloropropane
subchronlc (RfDj)
chronic (RfD)
l.2.3-Tr1chloropropene
subchronlc (RfDg)
chronic
2,3,6-TMchlorotoluene
subchronlc (RfD$)
chronic {RfD)
0627h
Exposure Species
Inhalation; Oral Inhalation Oral
NA; 100 mg/l In drinking NA rat
water for 13 weeks
(15 mg/kg/day)
NA; 100 mg/l 1n drinking NA rat
water for 13 weeks
(15 mg/kg/day)
NA; 8 mg/kg 5 days/week NA rat
for 120 days (5.7
mg/kg/day)
NA; 8 mg/kg 5 days/week NA rat
for 120 days (5.7
mg/kg/day)
3 ppm (18 mg/m3), dogs NA
6 hours/day. 5 days/week
for 66 weeks; NA
3 ppm (18 mg/m3), dogs NA
6 hours/day, 5 days/week
for 66 weeks; NA
NA; 0.5 ppm 1n diet NA rat
(0.05 mg/kg/day) for
28 days
NA; NA NA NA

Effect of Concern Reference Dose Uncertainty Factor
Inhalation; Oral Inhalation Oral Inhalation Oral
[mg/m3 (mg/kg/day)} (mg/kg/day)
Mstopathologlcal ND 5E-2 NA 300
lesions In liver,
kidney and thyroid
hlstopathologlcal NO 5E-3« NA 3000
lesions In liver,
kidney and thyroid
NA; transient cllnl- ND 6E-2 NA 100
cal signs, liver
and kidney lesions,
decrease 1n RBC,
hematocrH and
hemoglobin
NA; transient cllnl- ND 6E-3a NA 1000
cal signs, liver
and kidney lesions,
decrease In RBC,
hematocrH and
hemoglobin
eye Irritation; ND 5E-3b NA 100
NA
eye Irritation; NO 5E-3b NA 100
NA
NA; liver kidney, ND 5E-5 NA 1000
thyroid lesions
NA; NA ND ND NA NA
A-79
Reference
Inhalation/Oral
U.S. EPA, 1987a/
Vlllaneuve
et al.. 1985;
U.S. EPA, 1987b
U.S. EPA, 1987a
Vlllaneuve
et al., 1985;
U.S. EPA. 1987b
U.S. EPA, 1987/
NTP, 1983a;
U.S. EPA. 1987
U.S. EPA, 1987/
NTP, 1983a;
U.S. EPA. 1986.
1987
U.S. EPA. 1983/
McKenna et al. ,
1978; U.S. EPA.
1983
U.S. EPA. 1983/
McKenna 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
11/28/89

-------
                           HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE A: SUBCHRON1C AND CHRONIC TOXIC1TY (OTHER THAN CARCINOGENIC ITY)
                                                                   Update:  September. 1989
Compound
0,2.6-TMchloro-
toluene
subchronlc (RfD$)



chronic (RfD)

1.1.2-Tr1ch1oro-1,2,2-
trlf luoroethane
subchronlc (RfD$)






chronic (RfO)






TMMuralln
subchronlc (RfOg)



chronic (RfD)



Tr tme thy Iberuenes
Exposure
Inhalation; Oral


NA; 0.5 ppm In diet
(0.05 mg/kg/day) for
28 days

NA; NA



5358 rag/m3 occupational
for 2.77 years (273
mg/kg/day); NA




5336 mg/m3 occupational
for 2.77 years (273
mg/kg/day); NA





NA; 30 ppm In the diet
for 12 months (0.75
mg/kg/day)

NA; 30 ppm In the diet
for 12 months (0.75
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; liver, kidney, ND 5E-5 NA 1000
thyroid lesions


NA NA NA; NA ND NO NA NA



human NA psychomotor Impair- ND 3Efl NA 10
ment; NA





human NA psychomotor Impair- ND 3E»1D>Z NA 10
ment; NA






NA dog NA; Increased liver ND 7.5E-3 NA 100
weight, methemo-
gobllnemla

NA dog NA; Increased liver ND 7.5E-33 NA 100
weight, metbemo-
gobllnemla (Cancer:
see Table B)
DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
Reference
Inhalation/Oral


U.S. EPA, 1987/
Chu et al. ,
1984; U.S. EPA.
1987
U.S. EPA. 1987/
U.S. EPA. 1987


Imbus and
Adklns. 1972;
U.S. EPA, 1983,
1985/Imbus and
Adklns, 1972;
U.S. EPA, 1983,
1985
Imbus and
Adklns, 1972;
U.S. EPA. 1983,
1985/Imbus and
Adklns, 1972;
U.S. EPA, 1983.
1985

U.S. EPA, 1989/
Hoechst. 1984;
U.S. EPA, 1984.
1989
U.S. EPA, 1989/
Hoechst, 1984;
U.S. EPA. 1984,
1989
U.S. EPA, 1987
0627h
                                                                             A-80
11/28/89

-------
                           HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE  A:  SUBCHRONIC  AND  CHRONIC  TOXICITY  (OTHER  THAN  CARC1NOGEN1CITY)
                                                                   Update:   September,  1989
Compound
Exposure
Inhalation; Oral
Species
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
1,3,5-Trlnltrobenzene
  subchronlc (RfOs)
  chronic (RfD)
Trlnltrophenols

Vanadium
  subchronlc (RfD$)
  chronic (RfD)
Vanadium pentoxlde
  subchronlc (RfDj)
NA; 3 ppm 1,3-dlnltro-    NA
benzene In drinking water
for 16 weeks (0.4 mg/kg/
day equivalent to O.S1
mg/kg/day 1,3,5-trlnltro-
benzene)

NA; 3 ppm l,3-dln1tro-    NA
benzene In drinking water
for 16 weeks (0.4 mg/kg/
day equivalent to 0.51
mg/kg/day l,3,5-tr1n1tro-
benzene)
NA; 5 ppm vanadium        NA
from vanadyl sulfate
In drinking water for
lifetime (0.7 mg/kg/day)

NA; 5 ppm vanadium        NA
from vanadyl sulfate
In drinking water for
lifetime (0.7 mg/kg/day)
NA; 10 ppm vanadium       NA
In diet from vanadium
pentoxlde for lifetime
(0.9 mg vanadium pent-
oxlde/kg/day)
rat      NA; Increased spleen   NO                5E-4          NA
         weight
rat      NA; Increased spleen   NO                5E-5          NA
         weight
                                     DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
rat      NA; none observed      NO                7E-3          NA
rat      NA; none observed      NO                7E-39         NA
rat      NA; none observed      NO                9E-3          NA
  1000    U.S.  EPA,  1989/
          Cody  et al..
          1981; U.S.  EPA,
          1988, 1989
10,000    U.S.  EPA.  1989/
          Cody  et  al.,
          1981; U.S.  EPA,
          1988, 1989
                                                                                                                                            U.S. EPA,  1984
   100    U.S.  EPA.  1987/
          Schroeder
          et  al.,  1970;
          U.S.  EPA,  1987

   100    U.S.  EPA,  1987/
          Schroeder
          et  al.,  1970;
          U.S.  EPA,  1987
   100    U.S.  EPA,  1987/
          Stoklnger
          et al.,  1953;
          U.S.  EPA.  1987
chronic (RfO)
NA; 10 ppm vanadium NA rat NA; none observed NO
1n diet from vanadium
pentoxlde for lifetime
(0.9 mg vanadium pent-
oxlde/kg/day)
9E-3a NA 100 U.S. EPA, 1987/
Stoklnger
et al.. 1953;
U.S. EPA, 1986,
1987
0627h
                                                     A-B1
                                                                                                                                                  11/28/89

-------
                           HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE A: SUBCHRONIC AND CHRONIC TOX1C1TY (OTHER THAN CARC1NOGEN1CITY)
                                                                   Update:  September. 1969
Compound
Vanadyl sulfate
subchronlc (RfD$)
chronic (RfO)
Vernolate
subchronk (RfD$)
chronic (RfD)
Exposure Species
Inhalation; Oral Inhalation Oral
NA; 5 ppm vanadium from NA rat
vanadyl sulfate In
drinking water for life-
time (2.24 mg vanadyl
sul fate/kg/day)
NA; 5 ppm vanadium from NA rat
vanadyl sulfate 1n
drinking water for life-
time (2.24 mg vanadyl
sulfate/kg/day)
NA; 20 ppm In the diet NA rat
(1 mg/kg/day) reproduc-
tive
NA; 20 ppm In the diet NA rat
(1 mg/kg/day) reproduc-
tive
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-2 NA 100
NA; none observed ND 2E-2 NA 100
NA; decreased ND 1E-2 NA 100
body weight
NA; decreased ND 1E-3* NA 1000
body weight
Reference
Inhalat ton/Oral
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
U.S. EPA. 1983/
Stauffer Chem.
Co.. 1983;
U.S. EPA, 1983
4-V1nyl-l-cyclohexene

m-Xylene
  subchronlc (RfD$)
4750 mg/m3, 8 hours/
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)
rat
                                     DATA INADEQUATE FOR QUANTITATIVE RISK ASSESSMENT
rat      hepatomegaly; none     4EtO (1EtO)       4E*0
         observed
                                                                                           U.S.  EPA,  1983
1000       100    Tatral  et al.,
                  1981;  U.S.  EPA,
                  1989/NTP, 1986
chronic (RfD) 4750 mg/m3. 8 hours/ 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)
rat hepatomegaly; hyper- 7E-1 (?£-!)) 2EtO
activity, decreased
body weight, In-
creased mortality
at higher dosage
5000 100 Tatral et al..
1981; U.S. EPA,
1989/NTP, 1986;
U.S. EPA, 1986
0627h
                                                                             A-82
                                                                                                                                                 12/07/89

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                           HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE  A:  SUBCHRONIC AND CHRONIC  TOX1C1TY  (OTHER THAN  CARCINOGENICITY)
                                                                   Update:   September,  1989
      Compound
                              Exposure
  Inhalation; Oral
                              Species
Inhalation  Oral
Effect of Concern
Inhalation; Oral
                                                Reference Dose
    Inhalation
[mg/m3 (mg/kg/day)]
  Oral
(mg/kg/day)
Uncertainty Factor
Inhalation    Oral
   Reference
Inhalation/Oral
o-Xylenc
  subchronlc (RfD$)
  chronic (RfO)
ISO 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)
                     fetotoxlclty;  none
                     observed
                     hepatomegaly;  hyper -
                     activity,  decreased
                     body weight,  In-
                     creased mortality  at
                     higher  dosage
                        7E-1  (2E-1)
                       2E*0
                                                       100       100    Ungvary  et  al.,
                                                                        1980;  U.S.  EPA.
                                                                        1989/NTP. 1986
              5000        100    Tatral et al.,
                               1981; U.S. EPA,
                               1989/NTP, 1986;
                               U.S. EPA. 1986
p-Xylene
subchronlc (RfDj)



chronic (RfD)


Xylenes, mixed
subchronlc (RfDj)






chronic (RfD)






20 ppm 7.5 hours/day human
for 5 days (27 mg/m3);
NA

2C ppm 7.5 hours/day human
for 5 days (27 mg/m3);
NA

20 ppm 7.5 hours/day human
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
for 5 days (27 mg/m3);
250 mg/kg mixed
xylenes 5 days/week for
103 weeks (179 mg mixed
xylenes/kg/day)

rat CNS effects, nose 3E-1
and throat Irrita-
tion; NA

NA CNS effects, nose 3E-1
and throat Irrita-
tion; NA

rat CNS effects, nose 3E-1
and throat Irrita-
tion; none observed




rat CNS effects, nose 3E-l3
and throat Irrita-
tion; hyperactlvHy,
decreased body
weight and Increased
mortality at
higher dosage^
ND 100 NA Hake et al..
1981;
U.S. EPA, 1989/
U.S. EPA. 1989
ND 100 NA U.S. EPA, 1989/
U.S. EPA, 1989


4EfO 100 100 Hake et al.,
1981;
Litton Blo-
netlcs. 1978;
U.S. EPA. 1989/
NTP. 1986.
1987a,b
2E+Oa 100 100 Hake et al..
1981;
Carpenter et al.
1975; U.S. EPA,
1989/NTP. 1986;
U.S. EPA. 1987,
1989
0627h
                                                                            A-83
                                                                                                                         12/07/89

-------
                           HEALTH  EFFECTS ASSESSMENTS SUMMARY TABLE A: SUBCHRONIC AND CHRONIC T0XICITY (OTHER THAN CARCINOGENIC(TV)
                                                                  Update:  September, 1989
Compound
Zinc
subchronlc (RfO$)
chronic (RfO)
Zlneb
subchronlc (RfDj)
chronic (RfD)
Exposure Species
Inhalation; Oral Inhalation Oral
NA; 2.14 mg/kg/day NA human
therapeutic dosage
NA; 2.14 mg/kg/day NA human
therapeutic dosage
NA; 500 ppra In the diet NA rat
for 2 years (25 mg/kg/
day)
NA; 500 ppm 1n the diet NA rat
for 2 years (25 mg/kg/
day)
Effect of Concern
Inhalation; Oral
NA; anemia
NA; anemia
NA; thyroid
hyperplasla
NA; thyroid
hyperplasla
Reference Dose Uncertainty Factor Reference
Inhalation Oral Inhalation Oral Inhalation/Oral
[mg/m3 (mg/kg/day)] (mg/kg/day)
NO 2E-1 NA 10 U.S. EPA, 1984/
Porles et
al., 1967;
Prasad et al.,
1975; U.S. EPA,
19B4
NO 2E-1 NA 10 U.S. EPA, 1984/
Porles et al.,
1967; Prasad
et al., 1975;
U.S. EPA. 1984
NO 5E-2 NA 500 U.S. EPA, 1984/
Blackwell-Smlth
et al., 1953;
U.S. EPA, 19B4,
1986
NO 5E-2a NA 500 U.S. EPA, 19B4/
Blackwell-Smlth
et al., 1953;
U.S. EPA, 1984,
1986
'Verified, available on IRIS
b8ased on route-to-route extrapolation
cSpedf1ca11y related to organoleptlc  threshold  and  potential  for respiratory tract Irritation, not to systemic toxtclty.
dSpedfkally 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.
SUnder review by RfD Work Group
0627h
A-84
                                                                                                                                                 11/28/89

-------
''Because of background dietary exposure,  an KfO$o was n°t estimated.
'Verified 2 separate RfOs,  II  3 for food  and bl  4 for water
^Verified, Workgroup concurrence on final data base file, and IH1S Input pending
^Current drinking water standard of 1.3 mg/i;  Drinking Water Criteria Document concluded toxlclty data were Inadequate for calculation of an RfO for
 copper.
>CRAV( -verified as a CAG Group 0 substance
m1hese values differ from those In the HEED (U.S. EPA, 1987a) because the uncertainty factor for deriving the Inhalation RfO values presented herein were
 changed to correspond to those used by IRIS (U.S. EPA, 1987b) 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 RfO derived In  a more recent HfEP (U.S.  EPA,  1906).
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
rflased on RfD for methyl mercury
S7hese 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 on  IRIS.
*A 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  mg/day reference doses are Inappropriate because effects at portal  of entry depend on concen-
 tration In air.   An acceptable air concentration of 0.01 mq/rn^ was estimated by Carson et al.  (1981) from available data.
"(xperlment performed with o xylene.
xtrom  toxlclty data on tetraethyl  lead.
yuithdrawn from IRIS.
7The oral RfO, while still  available on IRIS.  Is being reconsidered by the  RfO 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.
 NA -  Not applicable or not available; NO - not  determined
Notes:  To estimate acceptable water concentrations from oral RfOj/RfD. multiply by 70 and divide by 2 i.
  If exposure occurs by both oral and Inhalation routes, the route-specific RfOj/RfD must  be proportionally reduced.


06?7h                                                                        A 85                                                                 12/29/89

-------
                                                HtALlH tmCTG ASSESSMENTS SUMMARY 1ABLL B: CAHCINOGlNICm
                                                                  Update:   September,  1989
Compound
Acephate




Acroleln

Acrylamlde





Acrylonltrlle







Aldrln









Aniline


Exposure Species
Inhalation; Oral Inhalation Oral
NA; 2-year dietary NA mice




NA; NA HA NA

NA; 2-year drinking NA rat
water




occupational; three human rat
drinking water
studies





three dietary Mouse mouse
studies"; three
dietary studies







NA; 2-year dietary NA rat


EPA Group/slope factor
Tumor Site or Unit Risk
Inhalation Oral Inhalation Oral
(wg/m-T1 (mg/kg/day)-'
[(mg/kg/dayrl]
NA liver NO C/8.7E-33
(also see Table A)



NA NA C/HOa C/NOa
(also see Table A)
NA CNS. B2/1.3E-3 B2/4.5*Oa
(also see mammary and [4.SEfO)a«')
Table A) thyroid
glands.
uterus, oral
cavity
lung multiple B1/6.8E-5 B1/S.4E-1*
[2.4E-l]a






liver liver B2/4.9E-3 B2/1.7Ev1a
(also see Table A) [1.7E+l]a>b








NA spleen NO B2/5.7E-3d


Reference
Inhalation/Oral
U.S. EPA. 1988/
Chevron Chemical
Company. 1982;
U.S. EPA. 19B4;
U.S. EPA. 1988
U.S. EPA. 1987a.t>/
U.S. EPA. 1987a.b
U.S. EPA. 1988/
Johnson et al . .
T986; U.S. EPA.
1985; U.S. EPA.
T988

O'Berg. 1980;
U.S. EPA. 1983.
1987a.b/Quast
et al., 1980;
Bio/dynamics,
Inc.. 1980a.b;
U.S. EPA. 1983.
1987a.b
NCI. 1977; Davis
and Htzhugh. 1962.
Epstein. 1975;
Davis. 1965; U.S.
IPA. 19Rb. 1987U/
MCI. 1977; Daviv
and HUhu
-------
                                                 HEALTH EFFECTS ASSESSMENTS SUMMARY  TABLE  B:  CARCINOGENICITY
                                                                  Update:  September, 1989
EPA Group/slope factor

Compound


Aramlte



Arsenic
Exposure Species
Inhalation; Oral Inhalation Oral


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


100-5000 |ig/m3 human human
continuous;
Tumor Site
Inhalation


Increased
Incidence
of liver
tumors
(also see Table
respiratory
tract

Oral


Increased
Incidence
of liver
tumors
A)
skin
or Unit
Inhalation
( vq/nfl ) ~ '
[(mg/kg/day)-']
B2/[2.5E-2]b



A/4.3E-3
[5.0£»l]a'P
Risk
Oral
(mg/kg/day)-1

B2/[2.5E-2]
(from oral
exposure)


A/NAk

Reference
Inhalation/Oral


U.S. EPA, 1989/ U.S.
EPA. 1989; Popper
et al., 1960; Oser
and Oser, 1962

Brown and Chu,
1983a,b,c; Lee-
r j.1.4.. LA.. 1OOO.
0.01-1.8 mg/t In
drinking water
                                                                       (also see Table A)
                                                                                                                                        Hlgglns. 1982;
                                                                                                                                        Enterllne and
                                                                                                                                        Marsh. 1982;
                                                                                                                                        U.S. EPA, 1984a,b,
                                                                                                                                        1988/U.S. EPA,
                                                                                                                                        1988
Asbestos
Azobenzene

Benzene






8enz1d1ne


occupational; human
dietary
NA; 2-year dietary NA

occupational; human
occupational"






occupational; human
occupational^


rat lung and
mesothelloma
rat NA

human leukemia






human urinary
bladder
(also see


large
Intestine
abdominal
cavity

leukemia






urinary
bladder
Table A)


A/2.3E-1 , A/ND
(fibers/mt)-' m
B2/3.1E-5 B2/l.lE-la

A/8.3E-6 A/2.9E-2a'b
[2.9E-2J9






A/6.7E-2 A/2.3E+2a'b
[2.3E+2]3


U.S. EPA, 1986.
1987/N1P, 1985;
U.S. EPA, 1985, 1987
U.S. EPA, 1988/
NCI, 1979; U.S. EPA,
1986, 1988
Ott et al., 1978;
Rlnsky et al., 1981;
Wong et al., 1983;
U.S. EPA, 1985,
1987a,b/0tt et al.,
1978; Rlnsky et al.,
1981; Wong et al.,
1983; U.S. EPA,
1985, 1987a,b
Zavon et al., 1973;
U.S. EPA. 1986b/
Zavon et al.. 1973;
U.S. EPA, 1980.
1986a,b, 1987
0625h
                                                                              B-2
                                                                                                                                                    11/28/89

-------
                                                  HEALTH EFFECTS  ASSESSMENTS  SUMMARY  TABLE  B:  CARCINOGENICITY
                                                                   Update:  September, 1989
Compound
Benzo(a)pyrene
Benzo(k)fluoranthene
Benzotrlchlorlde
Benzyl chloride
Beryllium
81s(2-cnloroethyl)
ether
Exposure Species Tumor Site
Inhalation; Oral Inhalation Oral Inhalation Oral
2.2-9.S mg/m3. 4.5 hamster mouse respiratory stomach
hours/day for <96.4 tract
weeks; 1-250 ppm
diet for =110 days
NA; NA NA NA NA NA
0.94E-3 mg/kg/day, mice mice lung lungs
0.5 hrs/day, 2
days/wk for 1 yr;
0.26 mg/kg/day,
2 days/week by gavage
for 25 weeks
NA; 0. 15. 30 mg/kg. NA rat NA thyroid
3 days/week by gavage
for 104 weeks
occupational; 5 ppm human rat lung total
1n drinking water tumors
for lifetime (also see Table A)
560-day oral studyb; mouse mouse liver liver
560-day oral study
EPA Group/slope factor
or Unit Risk Reference
Inhalation Oral Inhalation/Oral
(pg/m3)-' (mg/kg/day)-1
[ (mg/kg/day )-l]
B2/NOa B2/ND* Thyssen et al..
1981; U.S. EPA.
1987/Neal and
Rlgdon, 1967;
U.S. EPA. 1980,
1987
B2/ND B2/NO U.S. EPA. 1987
B2/8.6E-1 B2/1.3E+19 Yoshlmura et al.,
[3.0+3]9 1986/Fukuda et al.,
1978; U.S. EPA. 1986
NO B2/1.7E-1a U.S. EPA. 1989/
L1J1nsk1, 1986;
U.S. EPA, 1986, 1989
B2/2.4E-3 B2/NOa Wagoner et al.,
[8.4]a 1980; U.S. EPA,
1987, 198B/
Schroeder and
MHchener, 1975a;
U.S. EPA, 1986.
1988
B2/3.3E-4 B2/1.1E+03 Innes et al..
[l.l£tO]a.b 1969; U.S. EPA.
1980a. 1986;/Innes
et al.. 1969;
U.S. EPA. 1980a
1986, 1987
06250
                                                                              8-3
12/01/89

-------
                                                 HEALTH EfFECTS ASSESSMENTS SUMMARY TABLE B: CARCINOGEN1CITY
                                                                  Update:  September,  1989
Compound
Bls(chloromethyl)-
ether
B»s(2-chloro-1-methy1-
ethyl)ether
B1s(2-ethylhexyl)
phthalate
Bromodlchlorome thane
Bromoethene
(vinyl bromide)
Bromoform
1,3-Butadlene
Exposure Species
Inhalation; Oral Inhalation Oral
Inhalation 10-100 rat rat
days; Inhalation
10-100 days"
2-year gavage mouse mouse
studyb; 2-year
gavage study
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
two Inhalation mouse, rat NA
studies; NA
Tumor Site
Inhalation
respiratory
tract
liver, lung

Oral
NO
liver, lung
NA liver
(also see Table A)
NA liver
(also see Table A)
liver
NA
hematopoletlc
system,
Leydlg cell,
thyroid
NA
adenomatous
polyps or
adenocardno-
mas 1n the
large Intestine
(also see Table
NA
EPA Group/slope factor
or Unit Risk
Inhalation Oral
(cg/ir1)-' (mg/kg/day)-'
t(mg/kg/day)-l]
A/6.2E-2 A/2.2E»2a.b
[2.2£*2]a
C/2E-3 C/7E-2
[7E-2]b
B2/ND* B2/1.4E-2*
B2/ND B2/1.3E-1
B2/3.2E-2 B2/NO
[1.1-1]
B2/ND B2/7.9E-3
A)
B2/2.BE-4a.l NO
[1.8E+0]
Reference
Inhalation/Oral
Kuschner et al.,
1975; U.S. EPA,
1988/U.S. EPA,
1988
NTP, 1982;
U.S. EPA, 1987/
NTP 1982;
U.S. EPA. 1987
U.S. EPA. 1987/
NTP, 1982a,
U.S. EPA. 1986,
1988
U.S. EPA, 1987/
NTP, T986a;
U.S. EPA, 1987
Benya et al., 1982;
U.S. EPA. 1984/
U.S. EPA, 1984
U.S. EPA, 1989/
U.S. EPA. 1989;
NTP, 1988
Hazelton Labs, 1981;
U.S. EPA, 1985,
1987, 1989; U.S
EPA, 1987, 1989
0625h
B-4
12/01/89

-------
                                                HtALTH EFKCTS ASSESSMENTS SUMMARY TABLE B: CARC1NOGENICITY
                                                                  Update:   September.  19B9
Compound
Butyl benzyl phthalate
Cadmium
Captafol
Exposure Species
Inhalation; Oral Inhalation Oral
NA; NA NA; NA NA
occupational; NA human NA
NA; dietary study NA mice
(CBl)
Tumor Site
Inhalation
NA
(also see
respiratory
tract
(also see
NA
(also see
Oral
NA
Table A)
NA
Table A)
lymphosarcoma
Table A)
EPA Group/slope factor
or Unit Risk
Inhalation
[(mg/kg/day)-1]
NA
Bl/l.BE 3
[b.lEtO]3
C/NO
Oral
(mg/kg/day) "'
C/NOa
NO/NOC
C/8.6E-3
Reference
Inhalation/Oral
U.S. EPA. 19B7a.b/
U.S. EPA, 198/a.b
Ihun et al., 1985;
U.S. EPA. 1985.
1986/U.S. EPA. 1984,
1988
U.S. EPA. 1984/
U.S. EPA. 1984
Carbazole
NA; 96-veek dietary
study
Carbon tctr«chlor1de    sever*1 qavage
                        studies'1;  several
                        yavage studies
                                               NA
                                               several
mice
several
NA
                          liver
                                                                                                     B2/NO
                                                            B2/2E-2
           liver          liver
             (also see Table A)
                                                                             B2/l.5E-Sa-b'd    B2/1.3E-1*
                                                                             [1.3E-l]a-b
U.S. EPA. 198b/
Tsuda ct al.. 1982;
U.S. EPA. 198fa

Delia Porta et al..
1961; Edwards
et al.. 1942; HCl.
1976; U.S. EPA.
1984a.b. 19B6/
Delia Porta et
a I.. 1961; Edwards
et al.. 1942;
MCI. 1976;
U.S. tPA. 1984.
1986
Chloranll NA; 82-week oral NA mice NA liver and
Study luny

Chlordane two dietary mouse mouse liver liver
bloassays"; two (also see Table A)
dietary bloassays



C/NO C/4.03E-1 U.S. EPA. 1986/ ,
BRL. 1968; U.S. EPA.
T986
B2/3.7E-4 B2/T.3E*Oa 1ROC.
[T.3E*0]a-b 1977;
198b.
IRDC.
1977;
1986.

1973; NCI.
U.S. EPA.
1987. 1988/
1973; NCI.
U.S. EPA.
1987. 1988
062 bh
                                                                             B 5
                                                                                       09/25/89

-------
                                                  HEALTH  EFFECTS  ASSESSMENTS  SUMMARY  TABLE  B:  CARCINOGCNICITY
                                                                   Update:  September, 1989
Compound
Chlorodlbromoethane


Chloroethene
(see vinyl chloride)
Chloroform




Chloromethane




4-Chloro-2-methyl-
amlllne


4-Chloro-2-2-methyl-
amUlne hydrochlorlde


Chloromethyl methyl
ether

Exposure Species
Inhalation; Oral Inhalation Oral
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 studyb


NA; 0-4000 ppm In NA mice
the diet for 18
months

NA; 9-4000 ppm In NA mice
the diet for 18
months

NA; NA human NA


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



liver kidney
(also see Table A)



kidney kidney




NA vascular
hemanglomas
and hemanglo-
sarcomas
NA vascular
hemanglomas
and hemanglo-
sarcomas
lung NA


EPA Group/slope factor
or Unit Risk
Inhalation Oral
dig/m')-' (mg/kg/day)-'
[ (mg/kg/day H]
B2/ND 62/8. 4E -2




B2/2.3E-5 82/6. IE -3a
[8.1E-2J3



C/1.8E-6 C/1.3E-2&
[6.3E-3]



B2/NO B2/5.8E-10



B2/NO B2/4.6E-1



A/NOa A/NOa


Reference
Inhalation/Oral
U.S. EPA, 19B7/
NTP, 1985;
U.S. EPA, 1987


NCI, 1976; U.S. EPA,
1985, 1987, 1988/
Jorgenson et al.,
1985; U.S. EPA,
1987, 1988
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;
Melsburger et al..
1978
U.S. EPA. 1986/
U.S. EPA, 1986;
Welsburger et al..
1978
U.S. EPA, 1987.
1988/U.S. EPA.
1988
0625h
B-6
11/28/89

-------
                                                  HEALTH EFFECTS ASSESSMENTS SUMMARY  TABLE  B:  CARCINOGENICITY
                                                                   Update:  September, 1989
Compound
o-Chloron1 trobenzene
p-Chloronl trobenzene
Chlorthalonll
Chromium (VI)
Coal tars
Creosote
DDT
Exposure Species
Inhalation; Oral Inhalation Oral
NA; 18-month NA mice
dietary study
NA; 0-6000 ppm In NA mice
the diet for 18
months
NA; 80-week dietary NA rat
study
occupational; NA human NA
occupational; NA human NA
NA; NA NA NA
NA; several dietary mouse. mouse,
stud1esb rat rat
Tumor Site
Inhalation Oral
NA liver
NA vascular
tumors
NA kidney
(also see Table A)
lung NA
(also see Table A)
lung NA
NA NA
liver liver
(also see Table A)
EPA Group/slope factor
or Unit Risk Reference
Inhalation
(yg/mJ)-' .
[(mg/kg/day)-l)
B2/ND
B2/ND
B2/ND
A/1.2E-2
[4.1E*l]a
ND/6.2E-4
[2.2E»OJ*
Bl/NO*
B2/9.7E-5
[3.4E-lJa-b
Oral Inhalation/Oral
(mg/kg/dayH
B2/2.5E-2 U.S. EPA, 1985/
U.S. EPA, 1985;
Helsburger et al.,
1978
B2/1.8E-2 U.S. EPA, 1985/
U.S. EPA, 1985;
Helsburger et al.,
1978
B2/2.9E-3 U.S. EPA, 1984/
NCI, 1978; U.S. EPA,
1984
ND/NDC Mancuso, 1975; U.S.
EPA, 1984a.b,
1986/NA
NO/NO Redmond et al.,
1979; Mazumdar
et al., 1975; U.S.
EPA. 1984/NA
Bl/ND* U.S. EPA, 1987/
U.S. EPA, 1967
B2/3.4E-1' U.S. EPA, 1986a.b/
U.S. EPA, 1984,
1986a.b
0625h
                                                                              B-7
11/28/89

-------
                                                 HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE B: CARCINOGtNICITY
                                                                   Update:   September,  1989
Compound
Decabromodlphenyl
oxide (Decabromo-
dlphenyl ether)
Dlallate



Dlbromochloromethane



1,2-Dlbromoetnane



1 ,4-D1chlorobenzene9
(p-dkhlorobenzene)

3,3' -Dlchlorobenzldlne



1 ,4-D1chloro-2-butene



1,1-D1ch1oroethane


Exposure Species
Inhalation; Oral Inhalation Oral
NA; NA NA NA


NA; 19-month oral NA mice
study


NA; 105-week gavage NA mouse
study


88-103 week Inhala- rat rat
tlon study; 49-week
gavage study

NA; 103-week gavage NA mouse
study

NA; lifetime NA rat
dietary study


90-day Inhalation rat NA
study; NA


NA; gavage NA rat


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

NA liver
(also see Table A)


NA hepatocellular
adenomas or
carcinomas
(also see Table A)
nasal cavity forestomach



NA liver
(also see Table A)

NA mammary



nasal NA
passages
(also see Table A)

NA hemanglo-
sarcoma
(also see Table A)
EPA Group/slope factor
or Unit Risk
Inhalation Oral
lug/in*)-' (mg/kg/day)-'
[(mg/kg/day)-1]
C/NDf C/NOf


B2/ND B2/6.1E-2



C/ND C/8.4E-2



B2/2.2E-4 B2/8.5Etla
[7.6£-l]a


B2/ND B2/2.4E-2


B2/NDf B2/4.5E-lf



B2/2.6E-3 B2/ND
[9.3]


NO/NO B2/9.1E-2


Reference
Inhalation/Oral
U.S. EPA. 1964,
19B7/U.S. EPA,
1984, 1987
U.S. EPA. 1983/
BRL, 1968; Innes
et al., 1969;
U.S. EPA. 1983
U.S. EPA, 1989/
NTP, 1985; U.S.
EPA, 1987, 1989

NTP. 1982; U.S. EPA,
1984, 1987b/NCI,
1978; U.S. EPA,
1984. 1987a,b
U.S. EPA. 1987/
NTP, 1986;
U.S. EPA. 1987
U.S. EPA. 1988/
Stula et al..
1975; U.S. EPA,
1988
El Dupont de
Nemours, 1986;
U.S. EPA, 1987/
U.S. EPA. 1987
U.S. EPA. 1984/
NCI, 1978; U.S.
EPA, 1985
0625h
B-8
11/28/89

-------
                                                 HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE B:  CAKCINOGEN1CITY
                                                                  Update:  September.  I9B9
Exposure Species
Compound Inhalation; Oral Inhalation Oral
l.2-D1chloroethane gavage*1; gavage rat rat
(ethylene chloride)


1.1-Okhloroethylene 10 and 25 pp* for mouse rat
(vlnyltdene chloride) 12 Months; gavage




1 .2 D1chloropropane9 HA; gavage HA wtuse


1.3-Dkhloropropene NA; 104-week NA rat
gavage study


Dleldrln several dietary amuse mouse
studies'*; several
dietary studies













EPA Group/slope factor
Tumor Site or Unit Risk Reference
Inhalation Oral Inhalation Oral Inhalation/Oral
(ng/mJ)-' (mg/kg/day)-1
[(mg/kg/day)-1]
circulatory circulatory B2/2.6E-5 B2/9.1E-28 NCI. 1978; U.S. EPA,
system system [9.1E-2]a«b 1985. 1986/
NCI. 1978; U.S. EPA.
1985. 1986
kidney adrenal C/5E-5 C/6E-la Maltonl et al..
(also see Table A) [1.2E+OJ4 1985; U.S. EPA,
1985. 1987/
NTP. 1982;
U.S. EPA. 1985.
1987. 1988
HA liver B2/HO B2/6.8E-2 U.S. EPA. 1987/
(also see Table A) NTP, 1986;
U.S. EPA. 1987
NA forestomach. B2/NO B2/1.8E-la U.S. EPA, 1985.
(also see liver, adrenal. 1987/NTP. 1985;
Table A) thyroid U.S. EPA, 1985,
1987
liver liver B2/4.6E-3 B2/1.6E*1a Thorpe and Walker.
(also see Table A) [1.6E+l]a-b 1973; Davis. 1965;
Walker et al..
1972; Tennekes
ct al.. 1981;
Nelerhenrey et al..
1983; NCI. 1978;
U.S. EPA. 1987b/,
Thorpe and Walker.
1973; Davis, 1965;
Walker et al..
1972; Tennekes
et al.. 1981;
Heiertienrey et al..
1983; NCI. 1978;
U.S. EPA. 1987a.b
0625h
                                                                              B-9
                                                                                                                                                   09/25/89

-------
                                                  HEALTH mtCTS ASSESSMENTS SUMMARY TABLE B: CARC1NOGENICITY
                                                                   Update:  September,  1989
Compound
3,3'-Dtmethoxybeni1dtne



2.4-01methylan11tne


2,4-01methylan111ne
hydrochlorlde

3,3'-D1methylbenz1d1ne


1,1-Dlmethylhydrazlne


1,2-Dlmetnylhydrazlne


Dimethyl sulfate


2,4-D1n1troto1uene


2,6-Dlnltrotoluene


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


NA; 18-month dietary NA mouse
study with the HC1 salt

NA; 18-month dietary NA mouse
study

NA; 30-day gavage NA rat
study

NA; lifetime drinking NA mouse
water study

NA; 73-week drinking NA mouse
water study

NA; NA NA NA


NA; 2-year dietary NA rat
study

NA; NA NA NA


EPA Group/slope factor
Tumor Site or Unit Risk
Inhalation Oral Inhalation Oral
(iifl/m^)-' (rog/kg/day)-'
l(mg/kg/day)-1]
NA forestomach B2/ND B2/1.4E-2



NA lung C/ND C/7.SE-1


NA lung C/ND C/5.8E-1


NA mammary B2/ND B2/9.2E+0


NA vascular system C/ND C/8.7E»09


NA vascular system Bl/ND B1/1.4E+30


NA NA B2*/ND 82*/ND


NA liver, B2/NO' B2/6.BE-lf ."
mammary
gland
NA NA B2/ND B2/6.BE-lf>n


Reference
Inhalation/Oral
U.S. EPA, 19B7/
Sellakumar et al.,
1969; OSHA/NIOSH,
19BO; 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
U.S. EPA, 1984/Toth
and Wilson, 1971;
U.S. EPA, 1984
U.S. EPA, 1985,
19B7/U.S. EPA. 1985.
1987
U.S. EPA. 1987/
Ellis et al.. 1979;
U.S. EPA, 1987,
U.S. EPA, 1987/
Ellis et al., 1979;
U.S. EPA. 1987
Qf»25h
                                                                              B-10
10/10/69

-------
                                                  HEALTH  EFFECTS  ASSESSMENTS  SUMMARY  TABLE  B:  CARCINOGEN 1C ITY
                                                                   Update:  September, 1989
Compound
1 ,2-D1phenylhydraz1ne
Direct Black 38
Direct Blue 6
Direct Brown 95
Direct Sky Blue 6B
EpIchlorohydHn
Exposure Species Tumor Site
Inhalation; Oral Inhalation Oral Inhalation Oral
2-year dietary rat rat liver liver
studyb; 2-year
dietary study
NA; 190-1500 ppm In NA rat NA liver
diet for 93 days
NA; 190-1500 ppm In NA rat NA liver
diet for 91 days
NA; 190-1500 ppm In NA rat NA liver
diet for 91 days
NA; NA NA NA NA NA
Inhalation exposure rat NA respiratory NA
for 30 days, observed tract
for llfespan; NA (also see Table A)
EPA Group/slope factor
or Unit Risk
Inhalation Oral
(jig/mj)-' (mg/kg/day)-'
[(mg/kg/dayj-l]
B2/2.2E-4 B2/8.0E-1*
tB.OE-lja.b
A/ND A/8.7E+0
A/ND A/B.lEtO
A/ND A/9.3E+0
B2/ND B2/ND
B2/1.2E-6 ND
(4.2E-3]a
Reference
Inhalation/Oral
NCI. 1978;
U.S. EPA. 1980.
1986/NCI. 1978;
U.S. EPA. 1980.
1986, 1987. 1988
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
Laskln et al.,
1980; U.S. EPA.
1984. 1985. 1986/
U.S. EPA. 1984.
1985. 1986
0625h
                                                                              B-J1
11/28/89

-------
                                                 HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE B: CARCINOGENICITY
                                                                   Update:   September,  1989
Compound
Ethyl acrylate
Ethylene dtbromlde
Ethylene oxide
Ethylene thlourea
Folpet
Formaldehyde
Furazolldone
Furl urn
Glycldaldehyde
Exposure Species
Inhalation; Oral Inhalation Oral
NA; 104-week NA rat
gavage study
(see 1,2-Dlbromoethane)
2-year Inhalation rat NA
study; NA
NA; 5-500 ppm 1n NA rat
diet for 2 years
NA; 112-113-week NA mice
dietary study
24-month Inhalation rat NA
study; NA
NA; 45-week NA rat
dietary study
NA; 28-week dietary NA mouse
study
NA; 70-week study NA rats
(gastric Intubation)
EPA Group/slope factor
Tumor Site or Unit Risk
Inhalation Oral Inhalation
(yg/ra3)-1 ,
Umg/kg/day)-l]
NA forestomach B2/NO

blood cells, NA B1/1E-4
brain [3.5E-1J9
NA thyroid B2/ND
NA digestive B2/NO
tract
nasal cavity NA Bia/1.3E-5'
[4.5E-2]
NA mammary B2/NO
NA leukemia B2/ND
NA NA B2/ND
Oral
(mg/kg/day)-'
B2/4.8E-2

ND
B2/3.6E-29
82/3. 5E -33
61 /ND
B2/3.8E+0
B2/5.0E*!
B2/ND
Reference
Inhalation/Oral
U.S. EPA. 1987/
NTP, 1986; U.S. EPA,
1987

SnelUngs et al. .
1981; U.S. EPA.
1985/U.S. EPA,
1985
U.S. EPA, 19B4/
U.S. EPA. 1984
U.S. EPA, 1987/
Chevron Chemical
Company, 1982;
U.S. EPA, 1984. 1987
U.S. EPA, 1985, 1988/
U.S. EPA, 1987/
U.S. DHEW. 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
11/28/89

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                                                 HEALTH EfFECIS  ASSESSMLNIS  SUMMARY  TABLE  B:  CAKClNOGlNICllY
                                                                  Update:  September. 1989
Compound
Heptachlor








Hexachlorobenzene




Hexachlorobutadlene





Hoxachlorocytlohexane-
alpha

Hexachlorocyclohexane-
beta


Hexachlorocyc lohexane-
delta



Exposure Species Tumor SUe
Inhalation; Oral Inhalation Oral Inhalation Oral
dietary studies'"; mouse mouse liver liver
dietary studies (also see Table A)







d1etb; diet hamster hamster liver liver
(also see Table A)



d1etb; diet rat rat kidney kidney
(also see Table A)




NA; 24-week dietary NA mice NA liver
study

NA; 110-week dietary NA mice NA liver
study


NA; 24-week dietary NA mice. NA liver
study rat



EPA Group/slope factor
or Unit Risk Reference
Inhalation Oral Inhalation/Oral
(iig/mj)~ ' (mg/kg/day) ~'
[ (mg/kg/day r1]
B2/1.3E-3 B2/4.5E+Oa Davis, 1965;
[4.5E+0]a-b Epstein, 1976; NCI.
1977; Reuber. 1977;
U.S. EPA. 1986.
I987b/0av1s. 1965;
Epstein. 1976; NCI.
1977; Reuber. 1977;
U.S. EPA. 1986
1987a,b
B2/4.9E 4 B2/1.7EfOf Cabral et al.. 1977;
[1.7EfO]b.f U.S. EPA. 1984,
1989/Cabral et al..
1977; U.S. EPA,
1984. 1985
C/2.2E 5 C/7.8E-2a Koctbaetal..
[7.8E-2]a-b 1977a; U.S. EPA,
1986/Kodba et al..
et al.. 1977a;
U.S. EPA. 1980,
1984. 1986
B2/1.8E-3 B2/6.3E*Oa U.S. EPA, 1986/Ito
[b.3E+0]a-b et al., 1973;
U.S. EPA. 1986, 1987
C/5.3E 4 C/1.8E+03 U.S. EPA. 1986/
[1.8EfO]a'b Thorpe and Walker.
1973; U.S. EPA.
1986. 1987
D/ND D/NOa U.S. EPA, 1986/
Ho et al.. 1973.
1975; Nagasaki
et al.. 1972.
U.S. EPA. 1986, 1987
0625h
                                                                              B  13
                                                                                                                                                   09/25/89

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                                                  HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE B: CARCINOGEN1CITY
                                                                   Update:   September,  1989
Compound
Hexachlorocyclohexane-
gamma (Llndane)
Hexachlorocyc lohexane-
epsllon
Hexachlorocyclohexane-
technUal
Hexachloroethane
Hydrazlne/hydrazlne
sulfate
Isophorone
Lead
2-Hethoxy-5-n1tro-
anlllne
Exposure Species
Inhalation; Oral Inhalation Oral
NA; diet NA mouse
NA; mixture of NA mice
delta and epsllon In
the diet for 26 weeks
NA; 6-20-month NA mice
dietary study
90-week gavage mouse mouse
study0; 90-week
gavage study
hydrazlne vapor rat mouse
Inhalation for
1 year; 25-week
exposure by gavage
to hydrazlne sulfate
NA; 2-year gavage NA rat
study
NA; NA NA NA
NA; 0.4X, 0.8X In NA rat
diet for 104 weeks
Tumor Site
Inhalation Oral
NA liver
(also see Table A)
NA liver
NA liver
liver liver
(also see Table A)
nasal cavity liver
NA kidney,
preputtal
gland
(also see Table A)
NA NA
(also see Table A)
NA skin
EPA Group/slope factor
or Unit Risk
Inhalation Oral
Ug/mi)-' (mg/kg/day)-'
t(mg/kg/day)-l]
B2-C/NO B2-C/1.3E*0«
0/NO D/ND*
B2/S.1E-4 B2/1.BE+oa
n.BE+Oja.b
C/4.0E-6 C/1.4E-23
[1.4E-2]a.|>
B2/4.9E-3 82/3. OE+0
[17.1E+0]*
C/NO C/4.1E-39
B2/NDa B2/N03
B2/NO B2/4.6E-2
Reference
Inhalation/Oral
U.S. EPA, 1984/
Thorpe and Walker,
1973; U.S. EPA,
19B4. 1986
U.S. EPA, 1986/
Goto et al., 1972;
U.S. EPA, 1986, 1987
U.S. EPA, 1986/
Munlr et al., 1983;
U.S. EPA, 1986, 1987
NCI, 1978; U.S. EPA,
1986, 1989/NCI. 1978;
U.S. EPA, 1980a,
1986, 1987, 1989
NacEwen et al., 1981;
U.S. EPA, 1984, 1987/
B1anc1flor1, 1970;
U.S. EPA, 1984, 1987
U.S. EPA, 1987/
NTP, 1986; U.S.
EPA, 1986a, 1987
U.S. EPA, 1984,
1988/U.S. EPA,
1984, 1988
U.S. EPA, 1987/NCI,
1978; U.S. EPA. 1987
0625h
B-14
11/28/89

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                                                  HEALTH EFFECTS  ASSESSMENTS  SUMMARY  TABLE  B:  CARCINOGENICITY
                                                                   Update:  September, 1989
Compound
2-Hethylan111ne
2-Methylan»11ne
hydrochlorlde
Methyl chloride
4,4-Methyleneb1s
benzelamlne
4.4'-Methylene
bls(N.N'-dlmethyl)
aniline
Methylene chloride
(dUhloromethane)
Methyl Ethyl Ketone
Methylhydrazlne
2-Methyl-5-N1troan1l1ne
Exposure Species
Inhalation; Oral Inhalation Oral
NA; 2-ntethylantllne- NA rat
hydrochlorlde In
diet for 93 weeks
NA; 93-week dietary NA rat
study
2-year Inhalation mouse NA
study
NA; 2-year drinking NA rat
water
NA; In diet for NA rat
59 weeks
Inhalation study; mouse mouse
Inhalation and
drinking water
studies
NA; NA NA NA
NA; lifetime NA hamster
oral study
NA; In diet for NA mouse
98 weeks
Tumor Site
Inhalation Oral
NA skin
NA skin
kidney NA
NA liver
NA thyroid
lung, liver liver
(also see Table A)
NA NA
(also see Table A)
NA liver
NA liver
EPA Group/slope factor
or Unit Risk
Inhalation Oral
(yg/m^)-' (mg/kg/day)-'
Hmg/kg/dayH]
B2/NO B2/2.4E-1
B2/NO B2/1.8E-1
C/l. 26xlO-2 C/NO
NO ND/2.SE-1
B2a/N0 B2a/4.6E-2a
B2/4.7E-7f B2/7.5E-3™
D/NOf D/NOf
NA/NO NA/1.1E+0
C/NO C/3.3E-2
Refer enc'e
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, 1967
CUT. 1983;
U.S. EPA, 1986/
U.S. EPA. 1986
NA/NTP, 1983;
U.S. EPA, 1984
U.S. EPA, 1985/
NCI, 1979;
U.S. EPA, 1969
NTP. 1986; U.S. EPA.
1984, 1986/NTP,
1986; NCA, 1983;
U.S. EPA, 19856, 1986
U.S. EPA. 1985. 1988/
U.S. EPA. 1965. 1988
U.S. EPA. 1984/Toth
and Sh1m1zu, 1972;
U.S. EPA, 1984
U.S. EPA. 1987/NCI,
1978; U.S. EPA, 1987
0625h
                                                                             B-15
12/01/89

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                                                 HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE B: CARCINOGENIC[TY
                                                                  Update:   September,  19B9
Compound
Mlrex
Niagara Blue 4B
Nickel
Exposure Species
Inhalation; Oral Inhalation Oral
Tumor Site
Inhalation
Oral
EPA
Group/slope factor
or Unit Risk
Inhalation Oral
Reference
Inhalation/Oral
(ug/ra3)-' (mg/kg/day)-1
[ (mg/kg/day Hi
NA; 2-year dietary NA rat
study
NA; NA NA NA
occupational; NA human NA
NA
(also see
NA
respiratory
tract
(also see
liver,
adrenal
Table A)
NA
NA
Table A)
B2/NO
B2/NO
B2/I.8E+0
B2/NO
nickel NO/NDC
refinery dust: A/
2.4E-4 [8.4E-l]a
nickel subsulMde:
A/4.8E-4 [1.7E+0]3
U.S. EPA, 1987/
NTP, 1987;
U.S. EPA, 1987
U.S. EPA, 1987/
U.S. EPA, 1987
U.S. EPA. 1986;
Chovll et al.,
1981; Enter line and
Marsh, 1982; Magnus
et al.. 1982; Peto
NHrofurazone
2-NUropropane
NA; 46-week dietary   NA         rat        NA
study
22-month Inhalation    rat        NA         liver
study; NA
                                                                                  mammary
      NA
                    82/ND
B2/9.369
                    B2/1.5E40
                                                                                           B2/ND9
et al., 1984;
U.S. EPA, 1987a,b/
U.S. EPA, 1984

U.S. EPA. 1987/
Erturk et al.,
1970c; U.S.  EPA,
1987

Lewis et al..  1979;
U.S. EPA. 1985X
U.S. EPA, 1985
N-NHrosodl-n-butyl-
amlne



Nltrosodlethanol-
amlne


drinking water for mouse mouse
life0; drinking
water for life


NA; 28 or 64 ppm In NA rat
drinking water for
100 weeks

bladder
esophagus



NA



bladder B2a/5.4a.o
esophagus



liver B2a/ND



B2a/5.4E+Oa Bertram and Craig,
1970; U.S. EPA,
1986a,b/Bertram and
Craig. 1970;
U.S. EPA, 1986a, b
B2a/2.8E+0 U.S. EPA. 1986, 1987/
LlJInsky and Kovatch,
1985; U.S. EPA, 1986,
1987
0625h
B-16
                                                                                                                                                 11/28/89

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N-N1trosomethyl-
ethylamlne
                                                  HEALTH  EFFECTS ASSESSMENTS SUMMARY TABLE B: CARCINOGENICITY
                                                                   Update:   September,  1989
Compound
N-Nltrosodlethyl-
amlne
N-NHrosodlmethyl-
amlne
N-NUrosodlphenyl-
amlne
N-N1trosod1-n-pro-
pylamlne
Exposure Species Tumor Site
Inhalation; Oral Inhalation Oral Inhalation Oral
drinking water rat rat liver liver
6 or 12 months;
drinking water
for 6 or 12 months
drinking water; rat rat liver liver
drinking water;
NA; 700-day dietary NA rat NA urinary
study bladder
NA; lifetime NA rat NA liver
drinking water
EPA Group/slope factor
or Unit Risk
Inhalation Oral
(pg/m^)-' (nig/kg/day)-'
[(mg/kg/day)-1]
B2a/1.5xl02 a'b B2a/1.5E+2a
B2a/5.1xl01a'b B2a/5.1E*l
B2/NDa 82/4.9E-33
B2a/ND B2a/7.0a
Reference
Inhalation/Oral
Peto et al.. 1984;
U.S. EPA. 1986a,b/
Peto et al., 1984;
U.S. EPA. 1986a,b
Peto et al.. 1984;
U.S. EPA, 1986a,b/
Peto et al., 1984;
U.S. EPA. 1986a,b
U.S. EPA. 1987a/
NCI, 1979; U.S.
EPA, 1980, 1986.
1987a,b
U.S. EPA, 1986, 1987,
Druckrey, 1967;
NA; 1n drinking
drinking water  for
lifetime
NA
rat
NA
liver
B2a/ND
B2a/2.2E+la
Druckrey et al., 1967;
U.S. EPA, 1986, 1987

U.S. EPA, 1986, 1987/
Oruckrey et al., 1967;
Druckrey, 1967;
U.S. EPA, 1986, 1987
N-Nltrosomethyl-
vlnylamlne
Parathlon
PCBs (see Polychlorlnated
1, 2.3.4. 5-Penta-
bromo-6-chloro-
cyclohexane
NA; NA
NA; NA
NA
NA
NA NA NA
NA NA NA
(also see Table
B2/ND
C/NDa
A)
B2/ND
C/NDa
U
U
U
U
.S.
.S.
.S.
.S.
EPA,
EPA.
EPA,
EPA,
1986/
1986
1987a,
1987a,

b/
b
blphenyls)
NA; 0-70 mg/kg/day NA
1n the diet for
2 years
rat NA large C/ND
Intestine
C/2.
.3E-21
U.S.
Blair
U.S.
EPA, 1985/
. 1981;
EPA, 1985
0625H
                                                                             B-17
                                                                                                                          11/28/89

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                                                  HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE  8:  CARCINOGENICITY
                                                                   Update:  September, 1989
Compound
Pentachloronltro-
beruene
o-Phenylenedlamlne
2-Phenylphenol
Polyaromatlc
hydrocarbons (PAH)
Polybromlnated
blphenyls
Polychlorlnated
blphenyls
Propylene oxide
Exposure Species
Inhalation; Oral Inhalation Oral
NA; 72-week oral NA mouse
study
NA; o-pheny1ened1~ NA rat
amtne dthydrocnlo-
rlde In diet for
546 days
NA; 2-phenyl- NA rat
phenol sodium
salt In diet for
637 days
Inhalation study hamster mouse
with benzo(a)pyrene;
dietary study with
benzo(a)pyrene
NA; Flremaster 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
EPA Group/slope factor
Tumor Site or Unit Risk
Inhalation Oral Inhalation Oral
(vg/m-»)-i (nig/kg/day)-'
[(mg/kg/day)-l)
NA liver C/NO C/2.6E-10.
(also see Table A)
NA liver B2/NO B2/4.7E-2
NA urinary C/ND C/1.94E-3
bladder
respiratory stomach B2/ND* B2/ND3
tract
NA hepato- B2/NO B2/8.9E+0
cellular
carcinoma
and neo-
plastlc
nodules
(also see Table A)
NA liver B2/NO B2/7.7EtOa
nasal cavity forestomach 82/3. 7E-6 B2/2.4E-lf
[1.3E-2]f
Reference
Inhalation/Oral
U.S. EPA, 19B6/
Innes et al., 1969;
U.S. EPA, 1986
U.S. EPA, 1985/
U.S. EPA, 1985;
Melsburger et al..
1978
U.S. EPA, 1984/
Hlraga and FuJ11,
1981; U.S. EPA,
1984
Thyssen et al.,
1981; U.S. EPA.
1987/Neal and
Rlgdon, 1967;
U.S. EPA, 1980,
1984. 1987
U.S. EPA, 1989/
NTP, 1983; U.S.
EPA, 1989
U.S. EPA, 1984,
1987b/Norback and
Meltman, 1985;
U.S. EPA, 1987a,b
NTP, 1985; Renne
et al., 1986; U.S.
EPA. 1985, 1989/
Dunkelberg, 1982;
U.S. EPA. 1985, 1989
0625h
B-18
                                                                                                                                                    11/28/89

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                                                  HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE  B:  CARCINOGENICITY
                                                                   Update:  September, 1989
Compound
RDX (CyclonUe)
Qulnollne
Sodium d1ethyld1th1o-
carbamate
2,3,7,8-TCOD
1,1,2,2-Tetrachloro-
ethane
Tetrachloroethy-
lene (perchloroe-
thylene)
p,a,a,o-Tetra-
chlorotoluene
Tetrachlorovlnphos
(stlrofos)
Exposure Species
Inhalation; Oral Inhalation Oral
NA; 2-year diet NA mouse
study
NA; 20-40-week NA rat
dietary study
NA; diet NA mouse
diet0; diet rat rat
gavage'1; gavage mouse mouse
Inhalation; gavage rat, mouse mouse
gavage studyb; mouse mouse
gavage study
NA; 560-day NA mice
dietary study
Tumor Site
Inhalation Oral
NA liver
hepato-
cellular
carcinomas
and adenomas
(also see Table A)
NA liver
NA hepatoma
(also see Table A)
several several
liver liver
leukemia, liver
liver
(also see Table A)
lung lung
NA liver
(also see Table A)
EPA Group/slope factor
or Unit Risk
Inhalation Oral
(vQ/nfl)-> (mg/kg/day)"1
[ (mg/kg/day )-']
C/NO C/l.lE-lf
C/NO C/12.5EH)
C/NO C/2.7E-1
B2J/3.3E-5 B2J/1.56E*5f
(pg/m*)-1
[1.56E*5]b'f
C/5.8E-5 C/2.0E-1*
[2.0E-1ja.b
B2/9.5E-7 B2/5.1E-29
[3.3E-3]
B2 B2/2.0Et1
C/NO C/2.4E-2
Reference
Inhalation/Oral
U.S. EPA. 1989/Llsh
et al.. 1984; U.S.
EPA, 1989
U.S. EPA. 1985/
Hlrao et al.. 1976;
U.S. EPA, 1985
U.S. EPA. 1988/
BRL. 1968a;
U.S. EPA, 1988
Koclba et al.,
1978; U.S. EPA,
1984/Kodba et al.,
1978; U.S. EPA. 1984
1985a,b
NCI. 1978; U.S. EPA.
1980. 1986/NCI.
1978; U.S. EPA.
1980. 1986
NTP, 1986; U.S. EPA
1986a. 1968/NCI.
1977; U.S. EPA,
1985a. 1988
Fukada et al.. 1979;
U.S. EPA. 1987/
Fukada et al.. 1979;
U.S. EPA. 1987
U.S. EPA. 1984/
NCI. 1978; U.S. EPA.
1984
0625h
                                                                              B-19
11/28/89

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                                                 HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE  B:  CARCINOGENICITY
                                                                  Update:  September, 1989
Compound
2,4-To1uened1am1ne


o-Toluldlne


p-Toluldlne
Toxaphene


2,4,6-TMchloroanlllne

2,4,6-TrlchloroanlHne
hydrochlorlde
1,1,2-Trlchloroethane


Exposure Species
Inhalation; Oral Inhalation Oral
NA; In the diet NA rat
for 103 weeks

NA; 511-day NA rat
dietary study
with HC1 salt

NA; 6-12 month NA mice
dietary study
with the HC1 salt
735-day dietary mouse mouse
studyb; 735-day
dietary study


NA; diet, HC1 salt NA mouse

NA; diet NA mouse
gavage*3; gavage mouse mouse


EPA Group/slope factor
Tumor Site or Unit Risk
Inhalation Oral Inhalation Oral
(ng/m-1)-' , (mg/kg/day)-1
[(mg/kg/day)-1]
NA mammary gland B2/NO 62/3. 2E»0


NA skin fibroma B2/NO B2/2.4E-1


NA liver C/NO C/1.9E-1
liver liver B2/3.2E-4 B2/l.lE*Oa


NA unspecified C/NO C/3.4E-2
tumors of the
vascular system
NA unspecified C/ND C/2.9E-2
tumors of the
vascular system
liver liver C/1.6E-5 C/5.7E-2*
(also see Table A) [5.7E-2ja.b


Reference
Inhalation/Oral
U.S. EPA, 1986/
NCI, 1979;
U.S. EPA. 1986
U.S. EPA, 1984/
Hecht et al. ,
1982; U.S. EPA.
1984
U.S. EPA, 1984/
Welsburger et al.,
1978; U.S. EPA, 1984
LUton B1onet1cs.
Inc., 1978;
U.S. EPA.1987b/
Litton B1onet1cs,
Inc. ,1978; U.S. EPA,
1980, 1987a,b
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, 1986/NCI,
1978; U.S. EPA,
1980, 1984. 1986
0625h
                                                                              B-20
                                                                                                                                                    11/28/89

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                                                 HEALTH EFFECTS ASSESSMENTS SUMMARY TABLE B:  CARCINOGENICITY
                                                                  Update:  September. 1969


Compound


TMchloroethylene




2.4,6-Trlchlorophenol



Trlfluralln



Trlmethyl phosphate


Vinyl bromide
(see bromoethene)
Vinyl chloride




Exposure Species
Inhalation; Oral Inhalation Oral


two Inhalation mouse mouse
studies; two
gavage studies



d1etb; diet mouse mouse



NA; In the diet NA rat
for 2 years


NA; 10-week gavage NA mice
study



1-year Inhalation rat rat
study; 10-50 ppm
diet



EPA Group/slope factor
Tumor Site or Unit Risk Reference
Inhalation Oral Inhalation Oral Inhalation/Oral
(jig/m3)-' (mg/kg/day)-'
[(mg/kg/day)-']
lung liver B2/1.7E-6 B2/l.lE-2h Maltonl et al.,
[1.7E-2]" 1986; Fukuda et.
al.. 1983/
NCI. 1976; NTP.
1983; U.S. EPA.
1985, 1987, 1988
liver liver B2/5.7E-6 B2/2E-2m NCI, 1979; U.S.
[2E-2]D-h EPA, 1980. 1986,
1987/NCI, 1979;
U.S. EPA, 1980,
1984
NA kidney. C/ND C/7.7E-3* U.S. EPA. 1987/
(see also bladder and Emmerson et al..
Table A) thyroid 1980; U.S. EPA.
1984, 1987
NA uterus B2/ND B2/3.7E-2 U.S. EPA. 1985/
MCI. 1978;
U.S. EPA. 1985


liver lung A/4.2E-5 A/2.3E+03 Maltonl et al..
[2.95E-1M] 1980, 1981; U.S.
EPA. 1985b; ATSOR.
1988/Feron et al.,
1981; U.S. EPA,
1984, 1985a
^Verified, on IRIS
bBased upon route-to-route extrapolation
cThere 1s Inadequate evidence for  cardnogenldty  of  this compound by the oral route.
Incorporates an absorption factor of  0.4.  Inhalation potency slope of 1.3E-1 (mg/kg/day}-1 as administered and 5.2£-2 (mg/kg/day)-1 as absorbed dose
0625h
B-21
                                                                                                                                                   01/03/90

-------
*Based on occupational data for coke oven workers
fVerified, Workgroup concurrpnrv on flndl data base file, and IRIS Input pending
Sunder review by CRAVf
"Values removed from IRIS pending further review
'Based on metabolized dose
Jfl2 classification Is for 2,3,7.8-lCDO alone.  Mixtures consisting of phenoxy herbicides and/or chlorophenols with 2,3,7.8-TCOO as a contaminant are
 classified as 81 carcinogens.
kA unit risk of 5E 5(wg/t)-1 has been proposed by the Risk Assessment Forum and this recommendation has been scheduled for SAB review.
'Slope factor Is for Internal  dose; ambient concentration was calculated by assuming an absorption factor of 54X.
"Verified and on IRIS, but under review
"This value applies to the mixture of 2.4-  and 2,6-dlnltrotoluene Isomers
°Based on results with 4-chloro-2~melhylanll1ne hydrochlor1de
PAn absorption factor of  30% Is used 1n calculation of the unit risk from the slope factor.
Q-Based on results with the alpha Isomer
 NA ^ Not applicable; NO  -  not  determined
0625h                                                                         8^22                                                                  12/29/89

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                 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.   They  should be  used in  conjunction  with the
radiation risk  assessment  guidance provided below and in Chapter
10  of  the  Human  Health  Evaluation  Manual   (OSWER Directive
9285.701A; formerly entitled the Superfund Public Health Evaluation
Manual).   As  risk assessment  methodologies are  refined, slope
factors and unit risk values will be revised and updated  in
Table C.
     The  U.S.  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  ionizing  radiation  induced cancers  in  humans.  Data
derived  from   both   human  epidemiological  studies   and animal
experiments are used by EPA  to  construct mathematical models of
exposure,  dose and  risk to  estimate  radionuclide  slope factor
values.  These complex models consider pathways of exposure, the
distinct metabolic behavior of each element by compound  and the
radiological characteristics  of each nuclide of  concern,  the time

                               C-l

-------
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  due to  low dose exposures  from risks  observed at
higher doses using  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 total lifetime excess
cancer incidence (i.e., total cancers) 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 pCi/m2 per year 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)  =  3.7x10"*  nuclear  transformations  per second)  for
consistency  with the  system used  for radionuclides in  the IRIS
database, and in the International  System (SI) units of becquerels
(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   the   users  also  apply  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/m3  (air) ,  risk  per  pCi/L  (water),  or  risk per  pCi/g
     (soil).
     Unit risk estimates for  air  and  drinking water  pathways
provided in Table C were calculated by multiplying the appropriate
inhalation and ingestion  slope factors by the inhalation rate (20
m3/day)  or the water  consumption rate  (2 L/day) , 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

     In Table  C,  the data listed  under the heading "Lung Class"
refer to the International Commission on Radiological Protection
(ICRP) classifications used to define the relative  clearance rates
of  inhaled  particulate radionuclides from the human lung and are
expressed as elapsed times on the order of days (D),  weeks  (W),  or
years  (Y).  Gaseous  radionuclides,  e.g.  Rn-222,  are assigned  to
class "*".   Data  listed under the  heading "GI Absorption Factors,
fl"  are values of  the fractional  amount of  each radionuclide
absorbed from the gastrointestinal tract into blood following  oral
intake.   Clearance rates and absorption  coefficients provided  in
the table  are  default  values used   by the  EPA  to  calculate
                               C-3

-------
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
                                                                 2
factors by  the effective  surface  density  of  soil (i.e.,  143 kg/m

«  0.10 m  (soil depth)  x  1.43xl03 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 pCi/m2
                                    per year)  x 143 kg/m*
                                    x  103  (g/kg) x  70 years



     External  exposure factors £o net  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,  the risk must be  calculated for  Cs-137  and

 Ba-137m in equilibrium concentrations of 1 pCi/g each (assuming
                               C-4

-------
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"4   total lifetime excess cancer risk


     The calculation must be done in this way because the external

exposure risk is due to the ionizing photon radiation from Ba-137m,

the short-lived decay product of the Cs-137  in soil.  In the same

manner, the total  lifetime excess cancer risk due to continuous,

lifetime  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,  especially  Pb-214 and  Bi-214,  as illustrated  in  the

example for Cs-137  and Ba-137m.

     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:
                                        IxlO"5
          pCi/m3 in air
                               unit risk in (pCi/m3)'1
                               C-5

-------
     To estimate  risk-specific concentrations in  water from the
unit risk in water as presented in Table C,  the specified level of
risk is divided by the  unit  risk for drinking water.  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
     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  =  	
                               unit  risk in (pCi/g)"1
                               c-6

-------
HEALTH EFFECTS ASSESSMEHT SUMMARY TABLE C:   RADIONUCLIDE CARCINOGENICITY   (Expressed in picocurie* (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
Am- 241
Am- 243
Ba-137m
Bi-214
C-14
Ce-144
Cm- 243
Cm- 244
Co-60
Cr-51
Cs-134
CS-135
Cs-137
Fe-59
H-3
1-129
1-131
K-40
Hn-54
Mo-99
**
ICRP
Lung
Class
U
U
D
U
*
Y
U
U
Y
Y
D
D
D
U
*
D
D
D
U
Y
*»*
Gl
Absorption
Factor (f^)
1.0E-03
1.0E-03
1.0E-01
5.0E-02
9.5E-01
3.0E-04
1.0E-03
1.0E-03
3.0E-01
1.0E-01
9.5E-01
9.5E-01
9.5E-01
1.0E-01
9.5E-01
9.5E-01
9.5E-01
9.5E-01
1.0E-01
8.0E-01
Inhalation
(pCi)"1
4.0E-08
4.0E-08
6.0E-16
2.2E-12
6.4E-15
3.4E-10
3. IE-OS
2.7E-08
1.6E-10
3.0E-13
2.8E-11
2.7E-12
1.9E-11
9.8E-12
7.8E-14
1.2E-10
2.4E-11
7.6E-12
5.3E-12
2.6E-12
Ingest ion
(pCi)'7
3.1E-10
3.0E-10
2.4E-1S
1.4E-13
9.1E-13
6.1E-12
2.3E-10
2.0E-10
1.5E-11
4.2E-14
4.2E-11
4.0E-12
2.8E-11
2.8E-12
5.5E-14
1.9E-10
3.6E-11
1.1E-11
1.1E-12
1.7E-12
Ground
Surface
(pCi/mVyr)"1
1.6E-12
3.6E-12
3.4E-11
8.0E-11
O.OE+00
1.2E-12
8.2E-12
S.8E-14
1.3E-10
1.9E-12
8.9E-11
O.OE+00
O.OE+00
6.2E-11
O.OE+00
1.5E-12
2.9E-11
7.8E-12
4.7E-11
9.0E-12
Air

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HEALTH EFFECTS ASSESSMENT SUMMIT TABLE C:  MDIONUCLIK CMCIMKEUCITY   (Expressed In pfcocuriM (pCi) )
                                       Stop* Factor

                            Age-averaged  lifetime excew total
                            cancer rltk per unit intake or
                           exposure
    PathMay-Speciflc Unit Risk

Age-averaged IIf•time  excess  total
cancer risk per  unit daily  Intake
or exposure for  70 years
Nuclide
Mb- 94
Np-237
P-32
Pb-210
Pb-214
Po-210
Po-214
Pu-238
Pu-239
Pu-240
Pu-241
Pu-242
Ra-226
Ra-228
Rn-222
Ru-106
S-35
Sr-89
Sr-90
Tc-99
**
ICRP
Lung
Cla*s
Y
U
0
0
0
U
U
Y
Y
Y
Y
Y
U
W
•
Y
D
0
0
U
»*»
Gl
Absorption
Factor (f,)
1.0E-02
1.0E-03
8.0E-01
2.0E-01
2.06-01
1.0E-01
1.0E-01
1.0E-03
1.0E-04
1.0E-04
1.0E-03
1.0E-04
2.0E-01
2.0E-01
--
5.06-02
8.06-01
3.06*01
3.06-01
8.06-01
Inhalation
2.16-10
3.6E-08
3.0E-12
1.7E-09
2.9E-12
2.7E-09
2.8E-19
4.2E-08
4.1E-08
4.1E-08
2.9E-10
3.9E-08
3.0E-09
6.5E-10
7.2E-13
4.46-10
1.96-13
2.96-12
5.66-11
8.36-12
Ingestion
(pCi)'1
2.16-12
2.7E-10
3.5E-12
6.5E-10
1.86-13
2.6E-10
1.0E-20
2.66-10
3.1E-11
3.1E-11
4.8E-12
3.0E-11
1.2E-10
1.06-10
--
9.66-12
2.26-13
3.06-12
3.36-11
1.36-12
Ground
Surface f
(pCi/eT/yr)"1
8.9E-11
1.86-12
0.06+00
1.86-13
1.5E-11
4.8E-16
4.7E-15
6.16-14
2.6E-14
5.9E-14
0.06+00
4.9E-14
4.2E-13
5.4E-20
2.2E-14
O.OE+00
O.OE+00
7.86-15
O.OE+00
3.46-17
Air - ,

-------
                             HEALTH EFFECTS ASSESSMENT SUMMIT TABU C:  RADIONUCLIDE CARCINQGENICITY   (Expr«M«d in picocuriM (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 intake or
                                                                                      exposure daily for 70 years

Muclide
Tc-99m
Th-230
Th-232
U-234
U-235
1CRP
Lung
Class
U
Y
r
Y
Y
•*•
GI
Absorption
Factor ; »D» (days), »W" (weeks), «Y» (years),  »*« (gas).
     Gastrointestinal (GI) absorption factors, i.e.  fractional  uptake of  a radionuclide  from the gut into blood.
                                                                        C-9

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MEALTH EFFECTS ASSESSMENT SUMMV TABLE C:  RAOIONUCLIOE CARCINOGENIC!TY   (Expressed In becquerels (Bq) )
                                      Slop* 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
Muclide
Am-241
Am-243
Ba-137N
BI-2U
C-U
Ce-144
Cm-243
Cm- 244
Co-60
Cr-51
Cs-134
Cs-135
Cs-137
Fe-59
H-3
1-129
1-131
K-40
Nn-54
Ho-99
ICRP**
Lung
Class
U
U
D
U
B
Y
U
U
Y
Y
D
D
D
U
s
0
D
D
U
Y
•ft*
Gl
Absorption
Factor (f|)
1.0E-03
1.0E-03
1.0E-01
5.0E-02
9.5E-01
3.0E-04
1.0E-03
1.0E-03
3.0E-01
1.06-01
9.5E-01
9.5E-01
9.5E-01
1.0E-01
9.5E-01
9.5E-01
9.5E-01
9.5E-01
1.0E-01
8.0E-01
Inhalation
(Bq)''
1.1E-06
1.1E-06
1.6E-14
5.9E-11
1.7E-13
9.2E-09
B.4E-07
7.3E-07
4.3E-09
8.1E-12
7.6E-10
7.3E-11
. 5.1E-10
2.6E-10
2.1E-12
3.2E-09
6.5E-10
2.1E-10
1.4E-10
7.0E-11
Ingest ion
(Bq)'
8.4E-09
6.1E-09
6.5E-14
3.8E-12
2.5E-11
1.6E-10
6.2E-09
5.4E-09
4.1E-10
1. 16-12
1.1E-09
1.1E-10
7.6E-10
7.6E-11
1.5E-12
5.1E-09
9.7E-10
3.0E-10
3.0E-11
4.6E-11
Ground
Surface
(Bq/nVyr)'1
4.3E-11
9.7E-11
9.2E-10
2.2E-09
O.QE+00
3.2E-11
2.2E-10
1.6E-12
3.5E-09
5.1E-11
2.4E-09
O.OE+00
O.OE+00
1.7E-09
O.OE+00
4.1E-11
7.8E-10
2.1E-10
1.3E-09
2.4E-10
Air
(Bq/mV
S.6E-01
S.6E-01
8.2E-09
3.3E-05
6.7E-08
4.7E-03
4.3E-01
3.7E-01
2.2E-03
4.1E-06
3.9E-04
3.7E-05
2.6E-04
1.3E-04
1.1E-06
1.6E-03
3.3E-04
1.1E-04
7.2E-05
3.6E-05
Drinking
Water
(Bq/L)'1
4.3E-04
4.1E-04
3.3E-09
1.9E-07
1.3E-06
8.2E-06
3.2E-04
2.8E-04
2. IE -05
5.6E-08
5.6E-05
5.6E-06
3.9E-05
3.9E-06
7.7E-08
2.6E-04
5.0E-05
1.5E-05
1.5E-06
2.4E-06
External
Exposure
(Bq/g soil)'1
4.3E-04
9.7E-04
9.2E-03
2.2E-02
O.OE+00
3.2E-04
2.2E-03
1.6E-05
3.5E-02
5.1E 04
2.4E-02
O.OE+00
O.OE+00
1.7E-02
O.OE+00
4.1E-04
7.8E-03
2.1E-03
1.3E-02
2.4E-03
                                          C-10

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HEALTH EFFECTS ASSESSMENT SUMMARY TMLE C:  RAOIONUCLIDE CARCIHOGEHICITT   (Expressed in becquerels (Iq) )
                                      Stop* 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
Nb-94
Np-237
P-32
Pb-210
Pb-2U
Po-210
Po-ZU
Pu-238
Pu-239
Pu-240
Pu-241
Pu-242
Ra-226
Ra-228
Rn-222
Ru-106
S-35
Sr-89
Sr-90
Tc-99
ICRP"
Lung
Class
Y
W
0
D
D
U
U
Y
Y
Y
Y
Y
U
U
g
Y
D
D
D
U
Gl"*"
Absorption
Factor (ft)
1.0E-02
1.0E-03
8.0E-01
2.0E-01
2.0E-01
.OE-01
.OE-01
.OE-03
.OE-04
.OE-04
.OE-03
.OE-04
2. OE-01
2. OE-01
--
5.0E-02
8. OE-01
3. OE-01
3. OE-01
8. OE-01
Inhalation
(Bq)'1
5.7E-09
9.7E-07
8.1E-11
4.6E-08
7.8E-11
7.3E-11
7.6E-18
1.1E-06
1.1E-06
1.1E-06
7.8E-09
LIE -06
8.1E-08
1.8E-08
1.9E-11
1.2E-08
5.1E-12
7.8E-11
1.5E-09
2.2E-10
Ingest Ion
(Bq)1
5.7E-11
7.3E-09
9.5E-11
1.BE-08
4.9E-12
7.0E-09
2.7E-19
7.6E-09
8.4E-10
8.4E-10
1.3E-10
8.1E-10
3.2E-09
2.7E-09
--
2.6E-10
5.9E-12
8.1E-11
8.9E-10
3.5E-11
Ground
Surface
(Bq/w2/yr)"'
2.4E-09
4.9E-11
O.OE+00
4.9E-12
4.2E-10
1.3E-14
1.3E-13
1.6E-12
7.0E-13
1.6E-12
O.OE+00
1.3E-12
1.1E-11
1.5E-18
5.9E-13
O.OE+00
O.OE+00
2.1E-13
O.OE+00
9.2E-16
Air

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                              HEALTH EFFECTS ASSESSMENT SUMMIT TABLE C:  MDIONUaiOE CARCINOGEIIICITT   (Expressed fn becquerel* (Sq) )
U-238
2.0E-01
                                                                     Stqpt Factor

                                                          Age-averaged lifetime excess  total
                                                          cancer risk per unit  Intake or
                                                          exposure
6.5E-07
                                                                       3.5E-09
                                                          1.2E-12
                                                                                          Patlwey-Spectfic Unit Risk

                                                                                       Age-averaged lifetime  excess  total
                                                                                       cancer risk per unit daily  intake
                                                                                       or exposure for 70 years

Hue I Ida
Tc-99n
Th-230
Th-232
U-234
U-235
ICRP**
Lung
Class
U
Y
Y
Y
Y
Gl***
Absorption
Factor (f,)
8.0E-01
2.0E-04
2.0E-04
2.0E-01
2.0E-01

Inhalation
7.3E-13
8.4E-07
8.AE-07
7.3E-07
6.8E-07

Ingest Ion
1.4E-12
6.5E-10
5.9E-10
3.8E-09
3.5E-09
Ground
Surface
(Bo/alVyr)-1
2.2E-10
1.6E-12
1.2E-12
1.5E-12
2.66-10

<.W>"
3.7E-07
4.3E-01
4.3E-01
3.7E-01
3.SE-01
Drinking
Water
(Bq/t)'1
7.2E-08
3.3E-OS
3.0E-OS
1.9E-04
1.BE-04
External
Exposure
(Bq/g soil)*'
2.2E-03
1.6E-05
1.2E-05
1.5E-05
2.6E-03
3.3E-01
1.SE-M
1.2E-05
     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); "0" (days), "U" (weeks), "Y" (years), "g" (gas).
     Gastrointestinal (Gl) absorption factors,  i.e.,  fractional  uptake  of  a radionuclide from the gut into blood.
                                                                        C-12

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                                  REFERENCES

                      HEA  SUMMARY  TABLE  A: NONCARCINOGENS

Acenaphthene
U.S. EPA.   1987.   Health  Effects  Assessment for Acenaphthene.   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.

Acenaphthylene
U.S. EPA.   1987.   Health  Effects  Assessment for Acenaphthylene.   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.

Acephate
Chevron  Chemical  Company.  1987.  Confidential  Business  Information;  unpub-
lished data.  MRID No. 40504819.

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.   1989.   Integrated  Risk Information System (IRIS).  Reference Dose
(RfD)   for   Oral   Exposure   for  Acephate.    Online.    (Verification  date
01/18/89.)   Office  of  Health  and  Environmental  Assessment,  Environmental
Criteria and Assessment Office, Cincinnati,  OH.

Acetone
U.S.  EPA.   1986a.   Ninety-day  gavage  study  In  albino  rats  using  acetone.
Office of Solid Waste, Washington, DC.  (Cited  1n U.S. EPA,  1986b)

U.S. EPA.   1986b.   Integrated Risk Information System (IRIS): Reference Dose
(RfD)  for oral  exposure  for acetone.  Online.  (Verification date 05/30/86.)
Office  of  Health  and Environmental  Assessment, Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

U.S.  EPA.   1988.   Updated Health Effects  Assessment  for  Acetone.   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.

Acetone  cyanohydrln
Blank,  T.L.  and   D.C.  Thake.    1984.   Three-Month  Inhalation  Toxlclty  of
Acetone  Cyanohydrln  In Male and Female  Sprague-Dawley Rats.  Monsanto Report
Nop. MSL-4423.  TSCA  8{d)  submission 878216397  (OTS0510325).

Howard,  J.W.   and  R.F.  Hanzal.    1955.   Chronic toxlclty  for rats  of  food
treated  with  hydrogen cyanide.   J. Agrlc. Food Chem.  3: 325-329.  (Cited In
U.S. EPA, 1985a)
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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
and  Assessment  Office, Cincinnati,  OH  for   the  Office  of Drinking  Water,
Washington, DC.   Final Draft.

U.S. EPA.   1985b.   Health  and  Environmental  Effects  Profile for  Acetone
Cyanohydrln.  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  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.

Acetonitrile
Coate,  W.B.  1983.   90-Day  subchronlc  toxlclty study  of acetonHrlle  In
B6C3F1  mice.    Final   Report  (revised).   Submitted to  National  Toxicology
Program by Hazelton Laboratories America, Inc.

U.S. EPA.   1987a.   Health Effects Assessment for AcetonHrlle.   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.   1987b.   Integrated  Risk  Information  System  (IRIS):  Reference Dose
(RfD)  for  oral  exposure  for   acetonltrile.   Online.    (Verification  date
03/19/87.)   Office  of Health  and  Environmental  Assessment,  Environmental
Criteria and 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
Literature, VIII,  1971, A compilation  of technical  reports of the biological
effect  and  the   public   health  aspects  of  atmospheric  pollutants,  M.Y.
Nuttonson, Ed.  p. 79-93.

Hagan, E.C.,  W.H.  Hansen, O.G.  Fltzhugh, et  al.   1967.   Food flavorings and
compounds  of  related  structure.   II.  Subacute  and chronic  toxlclty.   Food
Cosmet. Toxlcol.   5(2): 141-157.

U.S. EPA.   1987a.   Health Effects Assessment for Acetophenone.   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.   1987b.   Integrated Risk Information System (IRIS:  Reference Dose
(RfD)  for  oral  exposure  for   Acetophenone.   Online.    (Verification  date
10/15/87.)   Office  of  Health  and  Environmental  Assessment,  Environmental
Criteria and Assessment Office, Cincinnati, OH.

Acrolein
Costa, D.L.,  R.S.  Kutzman, J.R.  Lehmann and  R.T. Drew.   1986.  Altered lung
function  and  structure in the  rat after  subchronlc  exposure  to  acrolein.
Am.  Respir. Dis.   133(2):  286-291.


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Kutzman,  R.S.   1981.   A subchronlc  Inhalation  study  of  Fischer  344  rats
exposed to 0, 0.4,  1.4  or 4.0  ppm acroleln.   Brookhaven  National  Laboratory,
National Toxicology Program.  Interagency Agreement No.  222-Y01-ES-9-0043.

Kutzman, R.S.,  E.A.  Popenoe,  M.  Schmaeler and  R.T.  Drew.   1985.   Changes  In
rat  lung  structure  and composition  as  a result  of subchronlc  exposure  to
acroleln.   Toxicology.  34:  139-151.

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.

Acrylamlde
Burek,  J.D.,  R.R.  Albee, J.E.  Beyer, et al.   1980.   Subchronlc  toxldty  of
toxlclty  of  acrylamlde  administered  to  rats  In  the  drinking  water  followed
by up to 144 days of  recovery.  J.  Environ. Pathol Toxlcol.  4: 157-182.

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.   1988.   Integrated  Risk Information System (IRIS).   Reference Dose
{RfD)   for   Oral   Exposure   for  Acrylamlde.   Online.   {Verification  date
02/24/88.)   Office  of   Health  and  Environmental  Assessment,  Environmental
Criteria and Assessment Office, Cincinnati, OH.

Acrylic acid
DePass  L.R.,  M.D.  Woodslde,  R.H.  Carman  and C.S.  Well.   1983.   Subchronlc
and  reproductive  toxicology studies on acrylic acid 1n drinking water of the
rat.  Drug Chem. Toxlcol.   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.   1985.   Integrated  Risk Information System (IRIS).   Reference Dose
(RfD)   for  Oral  Exposure   for   Acrylic  Acid.   Online.    (Verification  date
08/19/85.)   Office  of   Health  and  Environmental  Assessment,  Environmental
Criteria  and Assessment  Office,  Cincinnati,  OH.

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
Konsanto   Company.    1984.   Confidential  Business  Information;  unpublished
study.  Accession  No. 255953.
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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.  1986.  Integrated Risk  Information  System (IRIS).  Reference Dose
(RfD)   for   Oral  Exposure  for   Alachlor.   Online.    (Verification   date
03/11/86.)   Office  of  Health  and Environmental  Assessment,  Environmental
Criteria and Assessment Office,  Cincinnati, OH.

Aldrln
Fltzhugh, O.6.,  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.   1985.   Integrated  Risk Information System  (IRIS):  Reference Dose
(RfD) for oral exposure  for aldrln.   Online.   (Verification  date 12/18/85.)
Office  of  Health and  Environmental   Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati,  OH.

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.

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.  1978.   Short-term  toxlclty
of ally! alcohol In rats.  Toxicology.  9: 29-45.

U.S.  EPA.   1985.   Health  and  Environmental  Effects   Profile  for  Ally!
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.

U.S. EPA.  1986.  Integrated Risk  Information  System (IRIS).  Reference Dose
(RfD)  for  Oral  Exposure  for  Ally!  Alcohol.   Online.    (Verification  date
02/26/86.)   Office  of  Health  and Environmental  Assessment,  Environmental
Criteria and Assessment Office,  Cincinnati, OH.

Ally! chloride (3-Chloropropene)
ACGIH  (American  Conference of  Governmental  Industrial  Hyglenlsts).   1980.
Documentation  of  the  Threshold  Limit Values for  Substances  In  the  Workroom
Air, 4th ed.   Conclnnatl, OH.   p.  12.

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.
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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.
Ametryn
C1ba-Ge1gy.   1961.
MRIO 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.   1987.   Integrated Risk Information System (IRIS).  Reference
(RfD)   for  Oral   Exposure   for   Ametryn.    Online.    (Verification
02/18/87.)   Office  of  Health and  Environmental  Assessment,
Criteria and Assessment  Office, Cincinnati, OH.
                                                   Dose
                                                   date
                                           Environmental
 l-Amlno-2-naphtol and 1-Am1no-2-naphto1 hydrochlorlde
 U.S.  EPA.   1986.   Health and  Environmental  Effects  Profile  for  l-Am1no-2-
 naphtol  and  l-Am1no-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,
 IcHy   testing  of  m-am1nophenol   1n
 Toxlcol.   4: 98-104.
                   et al.  1984.  Results
                   Sprague-Dawley   rats.
of teratogen-
 Fund.  Appl.
 U.S.   EPA.   1985.   Health  and  Environmental  Effects  Profile  for  Amlno-
 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.
 o-Amlnophenol
 U.S.   EPA.   1985.   Health
 phenols.   Prepared  by  the
 Environmental  Criteria  and
 of Solid  Waste,  Washington,

 p-Am1nophenol
 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.
 4-Am1nopyr1d1ne
 Kohn, F.E.  1968.   Four-week  Subacute Oral Tox1c1ty 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.  COL: 229844-E.  (Cited 1n U.S.  EPA,  1980)
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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  H.C. Merrltt.   1958.   Effect of
certain chemicals  1n  water on the  flavor of brewed  coffee.   Food  Res.   23:
575-579.  (Cited In U.S.  EPA,  1981)

Carson, B.L.,  C.M.  Beall,  H.V.  Ellis,  III  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.   Environmental  Health  Criteria.   54.
Ammonia.  WHO, Geneva, Switzerland.

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.

Antimony and Compounds
ASARCO, Inc.   1980.   TSCA  8(e) submission  8EHQ-0580-0342.  B1o/tox  data on
antimony trloxlde.  OTS,  U.S.  EPA, Washington, DC.

Schroeder,   H.A.,  M. Mltchener and  A.P.  Nason.   1970.   Zirconium,  nlobllum,
antimony and lead In rats:  Life-time studies.  J. Nutr.   100: 59-69.

U.S.  EPA.   1985a.   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.   1985b.   Integrated  Risk  Information  System (IRIS):  Reference  Dose
(RfD)   for   oral   exposure   for   antimony.    Online.    (Verification  date
11/06/85.)    Office of Health  and Environmental  Assessment,  Environmental
Criteria and Assessment Office, Cincinnati,  OH.
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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.

Watt,  W.D.    1980.   Chronic  inhalation  toxlclty  of  antimony   trloxlde  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  trloxide.   OTS,  U.S.  EPA,
Washington, DC.   (Cited  In U.S. EPA,  1985)

Watt,  W.D.  1983.   Chronic inhalation toxlclty of  antimony trloxlde: Valida-
tion  of  the threshold  limit  value.   Diss. Abstr.  Int.  B  1983.   44(3):  739-
740.

Aramite

Oser,  B.L.  and  M. Oser.   1962.   2-(p-tert-butylphenoxy)1sopropyl  2-chloro-
ethyl  sulfHe  (aramite).   II.  Carclnogeniclty.   Toxicol.  Appl.  Pharmacol.
4:  70-88.

Popper,  H.,  S.S. Sternberg, B.L. Oser  and M. Oser.  1960.  The carcinogenic
effect of aramite  in  rats.  Cancer.   13(5): 1035-1046.

U.S.   EPA.  1989.   Health  and Environmental  Effects  Document  for Aramite.
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.   HRID No. 40431301.

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   1988.   Integrated  Risk  Information  System (IRIS).   Reference  Dose
 (RfD)   for   Oral  Exposure   for   Atrazine.    Online.    (Verification   date
 06/22/88.)   Office  of  Health  and  Environmental   Assessment,   Environmental
 Criteria and  Assessment Office, Cincinnati, OH.
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Barium
Perry, H.M., S.J. Kopp, R.W. Erlanger and  E.F.  Perry.   1983.   Cardiovascular
effects of  chronic  barium Ingestlon.   IJK Trace Substances  in Environmental
Health, XVII, D.D.  Hemphin,  Ed.   Proc.  Univ. Missouri's  17th Ann.  Conf.  on
Trace  Substances  1n  Environmental Health.   University  of  Missouri  Press,
Columbia,  MO.

Tarasenko, M., 0. Promln  and  A. SHayev.  1977.   Barium compounds  as Indus-
trial  poisons  {an  experimental  study).   J. Hyg. Epldem.  Microbiol.  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.   1985a.   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
shington,  DC.   External  Review  Draft.    Final  Draft  (on Public  Comment).
NTIS  PB 86-118031/AS.

U.S.  EPA.   1985b.   Integrated  Risk Information System (IRIS): Reference Dose
(RfD)  for  oral  exposure for barium.   Online.   (Verification date 07/22/85.)
Office of  Health  and  Environmental  Assessment,   Environmental  Clrteria  and
Assessment  Office,  Cincinnati,  OH.

Benefin
Eli  Lilly  and Co.   1972.    Confidential  Business  Information; unpublished
study.  MRIO  No. 00037678.

U.S.  EPA.   1984.    Health  and  Environmental  Effects  Profile  for  Benefin.
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.   1985.   Integrated  Risk Information System (IRIS).   Reference Dose
(RfD)   for   Oral   Exposure  for   Benefin.   Online.    (Verification  date
11/06/85.)   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 3.D. Prejeau.    1983.   Encepha-
 lopathy  in  rats and  nephropathy  in rats  and mice  after  subchronic  oral
exposure  to benzaldehyde.   Food Chem. Toxicol.  21:  245-250.
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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.   1987   Integrated Risk Information  System  (IRIS).   Reference  Dose
(RfD)  for  Oral   Exposure  for   Benzaldehyde.   Online.   (Verification  date
10/15/87.)   Office of  Health  and  Environmental  Assessment,  Environmental
Criteria and Assessment Office, Cincinnati, OH.

Benzaldehyde cyanohydrin
U.S.   EPA.     1988.     Health   and   Environmental   Effects   Document   for
Cyanohydrins.    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.

Benzidine
Llttlefleld,  N.A.. C.J.  Nelson  and  C.H.  Futh.   1983.  Benzidine  dihydro-
chlorlde:  lexicological  assessments  In  mice during  chronic  exposure.   J.
Toxicol. Environ. Health.  12: 671-68.

U.S. EPA.  1987a.   Health Effects  Assessment  for  Benzidine.   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.   1987b.   Integrated Risk Information  System  (IRIS)  Reference  Dose
(RfD)   for   oral  exposure   for   benzidine.    Online.    (Verification  date
7/16/87.)   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.    1987a.   Health   and  Environmental  Effects  Document  for  Benzole
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.

U.S. EPA.  1987b.   Integrated  Risk  Information System (IRIS):  Reference  Dose
(RfD)  for  oral  exposure   for  benzole  add.   Online.   (Verification  date
9/17/87.)   Office  of   Health  and Environmental  Assessment,  Environmental
Criteria and Assessment Office, Cincinnati, OH.

Benzyl Alcohol
NIP  (National  Toxicology   Program).   1988.   Toxicology  and  carcinogenesis
studies of benzyl  alcohol  (CAS No. 100-51-6)  in  F344/N rats  and  B6C3F1  mice
(gavage studies).  NTP Technical Report, NTP TR 343.   p. 1-161.
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U.S.  EPA.    1989.   Health  and  Environmental   Effects   Document  for
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 M.  Mltchner.   1975.   Life-time studies  In  rats:  Effects
of aluminum, barium, beryllium and tungsten.  J. Nutr.  105:  421-427.

U.S. EPA.   1985.   Integrated  Risk Information  System  (IRIS):  Reference  Dose
(RfD)   for   oral   exposure   for  beryllium.    Online.    (Verification  date
12/02/85.)    Office of  Health  and  Environmental  Assessment,  Environmental
Criteria and Assessment Office, Cincinnati,  OH.

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.

l.T-B1phenyl
Ambrose, A.M.,  A.N.  Booth,  F. De Eds  and A.J.  Cos,  Or.   1960.   A toxlcolog-
Ical study of blphenyl, a vltrous funglstat.  Food Res.  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.

U.S. EPA.   1985.   Integrated  Risk Information  System (IRIS).  Reference Dose
(RfD)  for   Oral  Exposure  for  1,l-B1phenyl.    Online.    (Verification  date
10/09/85.)   Office  of  Health and  Environmental Assessment,  Environmental
Criteria and Assessment Office, Cincinnati, OH.

Bls(2-ethylhexyl) phthalate
Carpenter,   C.P.,  C.S.  Well  and H.F.  Smyth.  1953.   Chronic  oral  toxldty of
d1(2-ethylhexyl)  phthalate  for rats, guinea pigs and dogs.   Arch.  Ind.  Hyg.
Occ. Med.  8: 219-226.

U.S. EPA.   1986.   Integrated  Risk  Information  System (IRIS):  Reference Dose
(RfD)  for  oral exposure  for  b1s(2-ethylhexyl)  phthalate.   Online.   (Verifi-
cation  date  01/22/86.)   Office   of  Health   and Environmental  Assessment,
Environmental Criteria and Assessment Office, Cincinnati, OH.

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.

Blsphenol A
NTP  (National  Toxicology  Program).   1982.   Cardnogenesls  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.
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U.S. EPA.   1984c.   Reproduction and  ninety-day  oral  toxicity study  in  rats
U.S. EPA/OPTS Public Files Fiche No. OTS0509954.

U.S. EPA.   1988.   Health and  Environmental  Effects  Document for  Bisphenol
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.

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.3.,  Or.  and  R.S. Fisher.   1972.   Toxicologic studies  on  borax  and
boric acid.  Toxicol. Appl. Pharmacol.  23{3): 351-364.

Brominated dibenzo-p-dioxins and Dibenzofurans
U.S. EPA.   1985a.   Health  and  Environmental  Effects  Profile  for  Brominated
Dibenzofurans.   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  Brominated
Dibenzo-p-dioxins.   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  Brominated
D1benzo-p-d1ox1ns  and  Dibenzofurans.   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  Carcinogenesis
Studies  of  Bromodichloromethane  in  F344/N  Rats  and  B6C3F1  Mice (Gavage
Studies).   NTP Tech. Report, Ser. No.  321, NIH Pub!. 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.


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U.S.  EPA.   1987a.   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.    1987b.   Integrated  Risk Information  System  (IRIS):   Reference
Dose  (RfD)  for oral exposure  for  bromodlchloromethane.   Online.   (Verifica-
tion  date   07/16/87.)   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 cardnogenesls  studies of trihalomethane  (bromoform)  (CAS No.
75-25-2) In F344 rats and B6C3F1 mice (gavage studies).  Board Draft.

U.S.  EPA.   1987a.   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.  1987b.   Integrated  Risk Information  System  (IRIS): Reference Dose
(RfD)   for   oral   exposure  for  bromoform.    Online.    (Verification  date
08/13/87.)    Office  of Health  and  Environmental  Assessment,  Environmental
Criteria and Assessment Office, Cincinnati, OH.

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.

Bromomethane
Danse,  L.H.,  F.L.   van  Velsen and  C.A.   vander  Heljden.   1984.    Methyl
bromide:  Carcinogenic  effects  In  the  rat  forestomach.   Toxlcol.   Appl.
Pharmacol.   72: 262-271.
Russo,   J.M.,
Neurobehavloral
the rabbit.  J.
W.K.   Anger,   J.V.  Setzer   and  W.S.
assessment  of chronic  low-level  methyl
Toxlcol.  Environ. Health.  14: 247-255.
BMghtwell.    1984.
bromide exposure  In
U.S.  EPA.    1986a.   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.   1988.   Integrated  Risk  Information System (IRIS):  Reference  Dose
(RfD)   for  oral  exposure  for  bromomethane.   Online.   (Revised  verification
date 05/26/88.)   Office  of  Health  and Environmental Criteria  and  Assessment
Office. Cincinnati,  OH.
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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,  F.,   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 In 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.

Bromoxynll
Union  Carbide  Agriculture  Products,  Inc.   1982.   Confidential  Business
Information;  unpublished  study.  MRID No. 00096521.

U.S.  EPA.   1984.  Health and Environmental  Effects  Profile for BromoxynH.
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.   Integrated  Risk Information System (IRIS).  Reference Dose
(RfD)  for   Oral   Exposure  for  Bromoxynll.   Online.     (Verification  date
09/16/87.)   Office  of  Health  and  Environmental Assessment,  Environmental
Criteria and  Assessment Office, Cincinnati, OH.

BromoxynH 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.   1987.   Integrated Risk Information System (IRIS).  Reference Dose
(RfD)  for  Oral  Exposure   for  Bromoxynll  Octanoate.   Online.   (Verification
date  09/16/87.)   Office   of  Health  and  Environmental  Assessment,  Environ-
mental 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.
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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  toxlclty 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.

Butylate
Stauffer Chemical  Company.   1987.   Confidential  Business  Information;  unpub-
lished study.   MIRO No. 40289101.

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.   1989.   Integrated Risk  Information  System (IRIS).  Reference Dose
(RfD)   for   Oral  Exposure   for   Butylate.   Online.    (Verification  date
01/18/89.)   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.
Hazel ton 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  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.  1989.  Health and Environmental Effects  Document  for  Butyl  Benzyl
Phthalate.   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.

t-Butylchlorlde
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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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.

Cadmi urn
U.S.  EPA.    1980b.   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.

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.   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.

Caprolactam
Powers,  W.3.3,   J.C.  Peckham,   K.M.  Sllno  and  S.C. Gad.   1984.   Effects  of
subchronlc  dietary  caprolactam  on  renal  function.   In;.   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.   1988a.   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.   1988b.   Integrated Risk Information System (IRIS):   Reference Dose
(RfD)   for   oral  exposure for   caprolactam.   Online.   (Verification  date
03/24/88.)   Office  of  Health  and  Environmental  Assessment,  Environmental
Criteria and Assessment Office,  Cincinnati, OH.
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 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.   1987.   Integrated Risk Information System (IRIS).  Reference Dose
 {RfD)   for   Oral  Exposure   for   Captafol.    Online.    (Verification  date
 05/20/87.)   Office  of Health  and  Environmental  Assessment,  Environmental
 Criteria and Assessment Office, Cincinnati, OH.

 Captan
 Chevron  Chemical  Company.  1982.   Confidential  Business  Information; unpub-
 lished study.  NRID 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.   1989.   Integrated Risk Information System (IRIS).  Reference Dose
 (RfOJ for Oral Exposure for  Captan.   Online.   (Verification date 01/18/89.)
 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.  Mammalian toxldty of
 1-naphthayl-n-methylcarbamate (Sevln  Insecticide).   J.  Agrlc.  Food Chem.   9:
 30-39.

 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.  1985.    Integrated Risk Information System (IRIS).  Reference Dose
 (RfD)  for  Oral   Exposure  for   Carbaryl.   Online.    (Verification   date
 05/31/85.)  Office of  Health  and   Environmental  Assessment,  Environmental
 Criteria  and Assessment Office,  Cincinnati,  OH.

 Carbofuran
 FHC  Corporation.    1983.    Confidential   Business  Information;  unpublished
 study. Accession  No.  250740-250755.

 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.
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U.S. EPA.  1987.  Integrated Risk  Information  System  (IRIS).   Reference Dose
(RfD)  for  Oral  Exposure   for   Carbofuran.    Online.    (Verification  date
03/18/87.)   Office  of  Health  and  Environmental  Assessment,  Environmental
Criteria and Assessment Office, Cincinnati,  OH.

Carbon tetrachlorlde
Bruckner, 3.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.

U.S. EPA.   1985.   Integrated Risk Information System  (IRIS):  Reference Dose
(RfD)  for oral exposure  for  carbon tetrachlorlde.    Online.   (Verification
date  05/20/85.)   Office  of Health  and  Environmental Assessment,  Environ-
mental Criteria and Assessment  Office, Cincinnati, OH.

Chloral
Sanders,  V.M., B.M. Kauffmann,  K.L.  White,  Jr.  1982.   Toxicology  of  chloral
hydrate 1n the mouse.  Environ. Health Perspect.  44:  146-173.

U.S.  EPA.  1988a.   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.   1988b.   Integrated  Risk Information System (IRIS): Reference Dose
(RfD)  for  oral exposure for  chloral.  Online.   (Verification date  3/24/88.)
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.   1989.   Integrated Risk Information  System (IRIS).  Reference Dose
for  Oral  Exposure   to  Chlordane.   Online.   (Verification  date  03/22/89).
Office  of  Health and  Environmental  Assessment,  Enviromental Criteria  and
Assessment Office, Cincinnati, OH.

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.
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Chloroacetlc Acid
IROC  (International  Research  and  Development  Corporation).   1982a.   Sub-
chronic oral  toxlclty  test  with  monochloroacetlc  add  1n 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-Ch1oroan1l1ne
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-Ch1oroan111ne
U.S.  EPA.    1987.   Health and  Environmental  Effects  Document  for  Chloro-
anHlnes.   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-Ch1oroan1l1ne
NCI  (National  Cancer   Institute).   1979.   Bloassay  of  p-chloroan1llne  for
possible cardnogenlclty.  NCI  Cardnogenesls  Tech Rep.  Ser.  No.  189.   NTIS
PB295896.

U.S.  EPA.    1987a.   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.   1987b.   Integrated Risk Information  System (IRIS):  Reference Dose
(RfD)  for  oral  exposure  for p-chloroan1l1ne.   Online.   (Verification  date
12/15/87.)   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.

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.
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p-Chlorobenzoic acid
Kieckebusch, W., W. Griem and  K.  Lang.   1960.   The tolerability of p-chloro-
benzolc  acid.   Arznelmi  Hel-Forsch.   10:  999-10001.   (In  German;  English
translation)

U.S.  EPA.   1987.    Health  and  Environmental  Effects Document  for  p-Chloro-
benzoic  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-Chlorobenzotrifluoride
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-
benzotrlfluoride.    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-butadiene
Du  Pont  de  Nemours and  Company,  Inc.    1985.   2-Year  Inhalation Carcinogen-
icity 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-butadiene  (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  Carclnogenesis
studies  of  n-butyl  chloride  in   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.

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
Cyclopentadienes.    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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Chlorodlbromomethane
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.   1987a.   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.    1987b.   Integrated Risk  Information  System  (IRIS):   Reference
Dose  (RfD)  for  oral exposure  for dlbromochloromethane.   Online.   (Verifica-
tion   date   08/13/87.)    Office   of  Health   and  Environmental   Assessment,
Environmental Criteria and Assessment Office, Cincinnati,  OH.

U.S.  EPA.    1987c.   Health  Effects  Assessment  for Trlmethylbenzenes.   Pre-
pared  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-Chloro-m-cresol
Madsen,  C.,  P.H.  Andersen,  0.  Meyer  and  6.  Wurtzen.   1986.   4-Chloro-e-
methylphenol:  Salmonella/mammal1an-m1crosome mutagenlclty test  and  subacute
toxldty test 1n  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.  Sortwell,  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.   1985.    Integrated  Risk  Information System (IRIS): Reference Dose
(RfD)   for   oral   exposure  for   chloroform.   Online.   (Verification  date
12/02/85.)   Office  of  Health and Environmental  Assessment,  Environmental
Criteria and Assessment  Office, Cincinnati,  OH.

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.

m-Chloron1trobenzene
U.S.  EPA.T985~;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.
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Chlorophenol.  3- and 4-
U.S. EPA.   1987.   Health and Environmental Effects  Document  for
Phenols.   Prepared by  the  Office  of  Health  and Environmental
Environmental  Criteria  and Assessment Office, Cincinnati, OH
of Solid Waste and Emergency Response, Washington, DC.
                                                                 Chlorinated
                                                                 Assessment,
                                                             for the  Office
U.S.  EPA.   1988.   Integrated Risk Information  System  (IRIS):  Reference  Dose
(RfD)  for  oral  exposure  for  2-chlorophenol.   Online.    (Verification  date
1/20/88.)   Office  of  Health   and  Environmental  Assessment,  Environmental
Criteria and Assessment Office, Cincinnati, OH.
2-Chlorophenol
Exon,  J.H.  and  L.D.  Koller.  1982.   Effects of  transplacental  exposure
chlorinated phenols.  Environ. Health Perspect.  46: 137-140.
                                                                          to
U S.  EPA.   1987a.  Health  Effects  Assessment  for  2-Chlorophenol  and 2,4-01-
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.
 2-Chloropropane
 Gage,  J.C.   1970.  The  subacute  inhalation
 Uals.   Br.  J.  Ind.  Med.  27(1):  1-18.
                                            toxicity 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.


 U~s	EPA   T985    Health  and  Environmental  Effects  Profile  for  Chloro-
 toluenes '  Prepared  by the  Office of  Health and  Environmental  Assessment,
 Environmental  Criteria and  Assessment  Office, Cincinnati, OH for  the  Office
 of Solid Waste, Washington,  DC.
                                Confidential  Business Information;  unpublished
Chlorpyrifos
Dow Chemical Company.   1972.
study.  Accession No. 112118.

U S   EPA    1984    Health and  Environmental  Effects  Profile  for  Chlorpyrifos
and'chlorpyrifos-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    1986.   Integrated  Risk  Information System (IRIS).   Reference Dose
(RfD)  for  Oral   Exposure  for   Chlorpyrifos.  Online.   (Verification  date
03/11/86.)   Office  of   Health  and  Environmental  Assessment,  Environmental
Criteria and Assessment  Office, Cincinnati, OH.
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ChiorpyrIfos-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  Business  Informa-
tion; unpublished  study.  Accession No.  111253.

U.S. EPA.   1986.   Integrated  Risk  Information  System (IRIS).  Reference Dose
(RfD)  for  Oral   Exposure for  Chlorthalonll.   Online.   (Verification  date
04/08/86.)   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  TMvalent  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.  1985.   Integrated Risk  Information System (IRIS):  Reference Dose
{RfD)  for  oral   exposure for  chromium (III).  Online.   (Verification date
11/21/85).   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  In   drinking
water  to rats.  Am.  Med 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.  1986.   Integrated Risk  Information System (IRIS): Reference Dose
 (RfD)   for  oral   exposure  for  chromlum(VI).   Online.    (Verification  date
 02/05/86.)  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.

m-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.

ToxicUy   Research   Laboratories.    1987.    o.m.p-Cresol.     90-Day   oral
subchronlc neurotoxlcity 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.   1987.   Integrated  Risk  Information System (IRIS): Reference  Dose
(RfD)   for   oral   exposure   for   m-Cresol.    Online.   (Verification   date
08/13/87.)   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  subchronic
toxldty   studies  1n  rats.    Sponsored  by  the  Office  of   Solid  Waste,
Washington, DC.

Toxicity   Research   Laboratories.     1987.    o.m.p-Cresol.    90-Day    oral
subchronlc  neurotoxlcity  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.
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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.   1987.   Integrated Risk Information System  (IRIS):  Reference Dose
(RfD)   for   oral   exposure   for   o-Cresol.   Online.    (Verification   date
08/13/87.)   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  1n  rats.    Sponsored   by   the   Office  of   Solid  Waste,
Washington, DC.

Toxlclty   Research   Laboratories.    1987.   o,mfp-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.   1987.  Integrated  Risk  Information System  (IRIS):  Reference Dose
(RfD)   for   oral  exposure  for    p-Cresol.    Online.     (Verification  date
08/13/87.)   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,  80 submission.  Microfiche #  OTS 0513229.

U.S.  EPA.   1987a.  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.   1987b.   Integrated Risk  Information  System  (IRIS).    Reference
Dose   {RfD)  for  oral  exposure  for  cumene.    Online.   (Verification date
09/17/87.)   Office  of  Health and  Environmental  Assessment,  Environmental
Criteria  and Assessment Office, Cincinnati, OH.

Wolf, M.A.. V.K.  Rowe,  D.D.  McColllster, R.L.  Holllngsworth  and  F. Oyen.
1956.  Toxlcologlcal Studies  of  certain  alkylated  benzene and benzenes  AMA
Arch. Ind.  Health.   14: 387-398.
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Cyanazine
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  Cyanazine.
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.   Integrated  Risk Information System (IRIS).  Reference Dose
(RfD)   for   Oral  Exposure   for  Cyanazine.    Online.    (Verification  date
05/25/88.)   Office  of Health  and  Environmental  Assessment,  Environmental
Criteria and Assessment Office, Cincinnati, OH.

Cyanide
Howard,  J.W. and  R.F. Hanzal.   1955.   Chronic  toxidty  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.   1985.  Integrated  Risk  Information System (IRIS): Reference Dose
(RfD)  for  oral  exposure  for  cyanide.  Online.  (Verification date 08/05/85).
Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria and
Assessment  Office,  Cincinnati, OH.

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.

Cvclohexylamine
Gaunt,  I.F.,  M.  Sharratt,  P.G.  Grasso, A.B.  Lansdown  and  S.D.  Gangolli.
1974.  Short-term toxidty of cyclohexylamine HC1 In the rat.   Food  Cosmet.
Toxlcol.   12:  609-624.

Gaunt.   I.F.,   J.  Hardy,   P.   Grasso,  S.D.   Gangolli  and  K.R.  Butterworth.
 1976.  Long-term  toxlcity of cyclohexylamine  hydrochlorlde  In the  rat.   Food
 Cosmet.  Toxlcol.   14(4):  255-268.

 U S  EPA   1987a   Health and Environmental  Effects  Document  for Cyclohexyl-
 amine   '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
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U.S. EPA.  1987b.  Integrated Risk  Information  System (IRIS):  Reference Dose
(RfD)  for  oral  exposure  for cyclohexylamlne.   Online.   (Verification  date
9/17/87.)   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,  HI.

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.   1987.  Integrated Risk Information System (IRIS).   Reference Dose
(RfD)   for  Oral   Exposure  for   Dacthal.    Online.    (Verification  date
02/18/87.)   Office  of Health  and  Environmental  Assessment,  Environmental
Criteria and Assessment Office,  Cincinnati, OH.

Dalapon  (sodium salt)
Paynter, O.E.,  T.W.  Tuslng,  D.D. McColllster  and V.K.  Rowe.  1960.   Toxi-
cology  of   dalapon sodium  (2,2-d1chloropropo1on1c  add,  sodium  salt).   J.
Agrlc. Food Chem.  8:  47-51.

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.   1988.  Integrated Risk Information System (IRIS).   Reference Dose
(RfD)   for  Oral   Exposure  for   Dalapon.    Online.    (Verification  date
06/22/88.)   Office  of Health  and Environmental  Assessment,  Environmental
Criteria and Assessment Office,  Cincinnati, OH.

2.4-DB
Rhodla  Inc.   1969.   Confidential  Business  Information;   unpublished  study.
MRID No. 0092165.

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.
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U.S. EPA.  1985.   Integrated  Risk  Information  System  (IRIS).   Reference  Dose
(RfD) for Oral  Exposure  for  2,4-DB.   Online.   (Verification  date  06/17/85.)
Office of  Health  and  Environmental  Assessment,  Environmental Criteria and
Assessment Office, Cincinnati, OH.

DDT
Laug, E.P.,  A.A.  Nelson,  O.G.  FHzhugh 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.   3. 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.   1985.  Integrated Risk  Information System  (IRIS):  Reference  Dose
(RfD)  for  oral  exposure  for  DDT.   Online.   (Verification date  12/18/85).
Office of  Health  and  Environmental  Assessment,  Environmental Criteria and
Assessment Office, Cincinnati, OH.

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.

Decabromodlphenyl  ether
Kodba,  R.J.,  L.O.  Frauson,  C.G.  Humlston,  et  al.    1975.   Results  of  a
two-year  dietary  feeding  study  with   decabromodlphenyl  oxide  (DBDPO)  1n
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.

U.S. EPA.   1985.  Integrated Risk  Information System  (IRIS).  Reference Dose
(RfD)  for  Oral  Exposure  for Decabromodlphenyl Ether.  Online.   (Verification
date  10/09/85.)   Office of  Health  and  Environmental  Assessment,  Environ-
mental Criteria  and Assessment Office,  Cincinnati, OH.

Decabromodlphenyl  oxide
Kociba,  R.J.,  L.O.  Frauson,  C.G.  Humlston,  et  al.    1975.   Results  of  a
two-year  dietary  feeding  study  with   decabromodlphenyl   oxide  (DCDPO)  in
rats.  Combust.  Toxicol.  2:  267-285.

Norris,  J.M.,  J.W.  Ehrmantraut,  C.L.  Gibbons,  et  al.  1973.   Toxlcological
and  environmental  factors   Involved  In the  selection  of  decadlbromophenyl
oxide as a fire retardant chemical.   Appl. Polym. Symp.  22: 195-219.

Norris,  J.M., J.W. Ehrmantraut, C.L. Gibbons, et al.   1975.   Toxicology  of
octabromoblphenyl  and  decabromodiphenyl  oxide.   Environ.   Health  Perspect.
11:  153-161.
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U.S. EPA.  1985.  Integrated Risk  Information  System (IRIS).   Reference Dose
(RfD) for  Oral  Exposure for Decabromodlphenyl.   Online.   (Verification date
10/09/85.)   Office  of  Health  and  Environmental  Assessment,  Environmental
Criteria and Assessment Office, Cincinnati, OH.

U.S. EPA.  1987.  Health and Environmental  Effects  Document for  Decabromodl-
phenyl    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.

Dlazinon
Davies,  D.8. and  B.J.  Holub.   1979.   Comparative susceptibility  of  male and
female rats to dietary diazlnon toxldty.  J. Nutr.  109(6): xxvlii.

Davies,  D.B.  and  B.J.  Holub.   1980a.   Comparative  subacute   toxldty  of
dietary  diazlnon  in  the  male  and female  rat.   Toxicol.  Appl.  Pharmacol.
54(3): 359-367.

Davies,  D.B.  and  B.J.  Holub.  1980b.   lexicological evaluation  of dietary
diazlnon  in the rat.  Arch. Environ.  Contam. Toxicol.  9(6): 637-650.

U.S.  EPA.   1984.   Health  and Environmental  Effects Profile for  Diazlnon.
Prepared  by  the  Office of  Health  and Environmental Assessment, Environmental
Criteria  and  Assessment  Office,  Cincinnati,  OH for  the  Office  of  Solid
Waste. Washington,  DC.

Dibenzofuran
U.S.  EPA.  1987.   Health  Effects Assessment  for  Dibenzofuran.   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  1,4-d1bromobenzene and
1,2,4-trlbromobenzene  on xenoblotlc  metabolism.  Toxicol.  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, Washington, DC.

U.S.  EPA.  1986.   Integrated  Risk Information System (IRIS).  Reference  Dose
 (RfD)  for Oral  Exposure for 1,4-D1bromobenzene.  Online.   (Verification  date
05/15/86.)   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.
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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.   1987.   Integrated  Risk  Information System (IRIS).   Reference  Dose
(RfD)  for   Oral  Exposure for  Dlbromochloromethane.   Online.   (Verification
date  08/13/89.)    Office  of  Health   and  Environmental Assessment,  Environ-
mental Criteria and Assessment Office, Cincinnati, OH.

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.

D1-n-buty1  phthalate
Smith,  C.C.  1953.   Tox1c1ty of  butyl  stearate,  dlbutyl  sebacate,  dlbutyl
phthalate and methoxyethyl oleate.  Arch. Hyg. Occup.  Med.  7: 310-318.

U.S.  EPA.   1986.  IRIS:  Reference  Dose  (RfD) for  oral exposure for  dlbutyl
phthalate.   Online.    (Verification   date  01/22/86).  Office  of Health  and
Environmental  Assessment,  Environmental  Criteria  and  Assessment  Office,
Cincinnati,  OH.

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.

1,2-Dlchlorobenzene
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  1,2-dlchlorobenzene  in  F344/N  rats and  B6C3F1  mice.   U.S. DHHS,
NIH  Tech.  Rep.   Ser.  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.

1.3-Dlchlorobenzene
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
RTfey    R~ATsT  Chart,   A.   Doss, et  al.   1980.  Para-dlchlorobenzene:
Long-Term Inhalation Study  In  the  Rat.   ICI  Report Nso.  CTL/P/447.   August,
1980.
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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 Haste and Emergency Response, Washington, DC.

Dlchlorodlfluoromethane
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-trichloroethane,  dlchlorodlfluoromethane  and  1,1-di-
chloroethylene.  Toxicol.  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.   1985.  Integrated Risk  Information System  (IRIS):  Reference Dose
(RfD)  for  oral   exposure for  dlchlorodifluoromethane.   Online. (Verification
date  07/22/85).    Office   of  Health  and  Environmental Assessment,  Environ-
mental Criteria  and Assessment Office, Cincinnati, OH.

1.1-Dichloroethane
Hofmann. H.T.. H.  Birnstiel and  P.  Jobst.   1971.  The  inhalation toxlclty of
1.1- and  1,2-dichloroethane.   Arch.  Toxikol.  27:  248-265.   (Cited  in U.S.
EPA. 1983b)

U.S.  EPA.   1983.  Drinking  Water   Criteria Document  for  l,l-D1chloroethane.
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.

U.S.   EPA.    1984.    Health   Effects  Assessment   for  1,l-D1chloroethane.
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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1,1-Dlchloroethylene
Quasi, J.F., C.G. Humiston, C.E. Wade,  et  al.   1983.   A chronic  toxicity  and
oncogenldty study  in rats and  subchronic  toxicity  study  1n  dogs  on  Ingested
vlnylldene chloride.  Fund. Appl. Toxlcol.   3: 55-62.

U.S.  EPA.   1984.    Health   Effects   Assessment  for  1,l-D1chloroethylene.
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  1,1-dlchloroethylene.   Online.   (Verification
date  01/22/85).    Office of  Health   and  Environmental Assessment,  Environ-
mental Criteria  and Assessment Office,  Cincinnati, OH.

U.S.  EPA.   1988.   Updated Health  Effects Assessment  for  1,1-Dichloroethy-
 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.

 1.2-c-Dichloroethylene
 U.S.  EPA.   1984.   Health  Effects   Assessment  for   1,2-c-D1chloroethylene.
 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.

 1.2-t-Dichloroethylene
 Barnes,  D.W.,  W.M.  Sanders,  K.L. Shite,  3r.,  et  al.   1985.   Toxicology of
 trans-l,2-dichloroethylene in  the mouse.   Drug Chem.  Toxlcol.  8: 373-392.

 U.S.  EPA.   1984.   Health  Effects  Assessment  for   1,2-t-D1chloroethylene.
 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.  Integrated Risk Information System  (IRIS).  Reference  Dose
 (RfD) for Oral  Exposure for  trans-1,2-Dichloroethylene.  Online.   (Verifica-
 tion  date  04/20/88.)   Office  of  Health   and  Environmental   Assessment,
 Environmental  Criteria  and Assessment Office,  Cincinnati, OH.

 2.4-Dichlorophenol
 ftSn	J  H.  and  L.D.   Koller.   1985.   ToxIcHy of  2-chlorophenol,   2,4-di-
 chlorophenol and 2,4,6-trichlorophenol.   Water  ChloMnatlon.  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  2,4-01-
 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.
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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.

Dlchlorophenol. 2.3-. 2-5. 2.6-. 3-4-. 3.5-
 -          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.    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.

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.

1.3-D1chloropropene
Dow  Chemical Co.  1973.   MRID  Nos.  0067977,  0039684.  U.S. EPA, Washington,
DC.

Stott   W T ,  3.T.  Young,  L.L.  Calhoun  and  J.E.  Battjes.  1988.  Subchronlc
tox1c1ty of  Inhaled  technical  grade 1 ,3-d1chloropropene  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   1987.  Integrated Risk Information System (IRIS).   Reference  Dose
 (RfD)   for   Oral  Exposure  for   1 ,3-D1chloropropene.   Online.    (Verification
 date  04/05/87.)   Office  of  Health  and  Environmental  Assessment,  Environ-
 mental Criteria and Assessment  Office, Cincinnati,  OH.

 U $    EPA     1989.     Health   and   Environmental  Effects   Document   for
 I's-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.


                  .  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.  Hlcroflche No. OTS204864.

 Litton  Blonetlcs, Inc.   1980.  Mammalian  Toxlcologlcal   Evaluation  of  DIMP
 and  DCPD.   (Phase  2).   Litton Blonetlcs,  Inc.,  Kensington,  MD.   Contract
  DAUB.  17-77-C-7003.  NTIS AD-A082685.
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U.S. EPA.   1987.   Health and Environmental  Effects  Document  for  Cyclopenta-
diene and D1cyclopentad1ene.   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,  3.  Robinson, et al.   1969.   The toxicology
and pharmacodynamlcs of  dleldrin  (HEOO):  Two-year  oral  exposures  of  rats and
dogs.  Toxlcol. Appl. Pharmacol.  15: 345-373.

U.S. EPA.   1987a.   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.

U.S. EPA.   1987b.   Integrated Risk Information System (IRIS): Reference Dose
(RfD)   for   oral   exposure   for  dleldrln.    Online.    (Verification  date
04/16/87).   Office  of   Health  and  Environmental  Assessment,  Environmental
Criteria  and Assessment  Office, Cincinnati,  OH.

N.N-D1ethv1an111ne
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  qlvcol 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.


                 ..  Arcos   and  C.   Hoch-Llgeti.    1965.   The   carcinogenic
 activity of protein-denaturing agents  hepatocarcinogenldty of  dioxane.   J.
 Natl.  Cancer Inst.   35: 949-958.

 U S  EPA    1986    Health and  Environmental  Effects Profile  for  Diethylform-
 amide    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.


 Li's" EPA Y   1Y984Z "Health and  Environmental  Effects Profile  for  1,2-Diethyl-
 hydrazine.   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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D1ethyl-p-n1tropheny1phosphate (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
toxldty study of  dlethyl  phthalate  1n the rat.   Food  Cosmet.  Toxlcol.   16:
415-422.

U.S. EPA.   1987a.   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.   1987b.  Integrated  Risk  Information System  (IRIS):  Reference  Dose
(RfD)  for  oral  exposure  for dlethyl phthalate.   Online.   (Verification  date
07/16/87).   Office  of  Health  and Environmental   Assessment,  Environmental
Criteria and Assessment Office, Cincinnati, OH.

Dlmethoate
American Cyanlmld  Company.   1986.  MRID  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.   1988.   Integrated Risk Information System (IRIS).   Reference  Dose
(RfD)   for   Oral   Exposure  for   Dlmethoate.    Online.    (Verification  date
03/23/88.)   Office  of  Health  and  Environmental  Assessment,  Environmental
Criteria and Assessment Office, Cincinnati, OH.

N.N-Dlmethylanlllne
Abdo,  K.,   M.  Wolfe  and  R.  H1les.   1984.   Subchronlc toxlclty  of  N,N-d1-
methylanlUne 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-
anlUne.   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.   Integrated Risk Information System (IRIS).  Reference Dose
(RfD)  for  Oral  Exposure  for  N,N-D1methylan111ne.  Online.   (Verification
date  01/06/87.)   Office of  Health and  Environmental   Assessment,  Environ-
mental Criteria and  Assessment Office, Cincinnati,  OH.

N.N-Dlmethy1formam1de
Beccl,  P.3.. K.A.  Voss, W.D.  Johnson,  M.A.  Gallo and  J.G.  Bablsh.    1983.
Subchronlc  feeding study of N,N-d1methylformam1de  In rats and mice.   J. Am.
Coll.  Toxlcol.  2(6): 371-378.
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U.S. EPA.  1986.  Health  and  Environmental  Effects  Profile  for  N,N-D1methyl-
formamide.  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-; 2.4-; 2.5-; 3.6-)
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.

2.6-D1methylpheno1
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.   1986.   Integrated Risk  Information  System (IRIS):  Reference Dose
(RfD)  for  oral  exposure for 2,6-dimethylphenol.  Online.  (Verification date
01/22/86).   Office  of  Health  and  Environmental  Assessment,  Environmental
Criteria  and Assessment Office, Cincinnati,  OH.

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.

3.4-Dimethylphenol
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.  1988.  Integrated  Risk  Information System (IRIS):  Reference Dose
(RfD)  for oral exposure  for  3,4-dimethylphenol.  Online.   (Revised; verifi-
cation  date  01/22/86).    Office  of  Health   and  Environmental   Assessment,
Environmental  Criteria  and Assessment Office, Cincinnati, OH.

Dimethyl  phthalate                                              nuiu
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.

Dimethyl  terephthalate
NCI  (National   Cancer Institute).   1979.   Blcassay of dimethyl terephthalate
for  possible  carcinogenlcity.  DHEW/PUB/NIH 79-1376,  NCI-CG-TR121.

U S  EPA   1984   Health and Environmental  Effects  Profile for  Dimethyl and
Methyl Terephthalate.   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.  1985.  Integrated Risk  Information  System (IRIS).   Reference  Dose
(RfD) for  Oral  Exposure for Dimethyl Terephthalate.   Online.   (Verification
date  10/09/85.)   Office  of Health  and  Environmental  Assessment,  Environ-
mental Criteria and Assessment  Office,  Cincinnati, OH.

N.N-Dimethylurea
U.S. EPA.  1984.  Health and Environmental  Effects  Profile for N,N-D1methyl-
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.  HHherup,  L. Hastings,  K. Stemmer and R.T. Christian.  1981.
1.3-Dlnltrobenzene: Toxic  effect in vivo  and in  vitro.   3. Toxlcol.  Environ.
Health.  7(5): 829-847.

U.S.  EPA.   1985.   Health  and  Environmental Effects  Profile  for  DinHroben-
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.   1988.   Integrated Risk  Information  System (IRIS).  Reference Dose
(RfD)  for  Oral  Exposure  for  m-Dlnltrobenzene.   Online.   (Verification  date
04/20/88.)   Office  of Health  and  Environmental  Assessment, Environmental
Criteria and Assessment Office, Cincinnati, OH.

Dlnltrobenzene  (o-.  p^l
Cody,  I.E.,  S.  WHherup,   L. Hastings,  K.  Stemmer and R.T. Christian.  1981.
1,3-Dlnltrobenzene:  Toxic  effect .in. vivo and in vitro.   J. Toxlcol.  Environ.
Health.  7(5):  829-847.

U.S.  EPA.    1985.   Health  and  Environmental Effects  Profile  for  D1n1troben-
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-Dlnltro-p-cresol
U.S.  EPA.   1984.   Health  and Environmental Effects Profile for 2,6-D1mtro-
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-Dinltro-o-cresol
ACGIH (American  Conference of  Governmental  Industrial   Hyglenists).   I98t>.
Threshold  Limit  Values.  ACGIH, Cincinnati, OH.

U.S.  EPA.   1986.   Health and  Environmental  Effects Profile  for  Dinitro-
 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.
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Dinitrophenols
U.S.  EPA.   1984.   Health  and  Environmental  Effects  Profile  for  Dinltro-
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
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.

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.  1986.   Integrated Risk Information  System (IRIS).  Reference Dose
(RfD)   for   Oral  Exposure   for   Dlnoseb.    Online.    (Verification   date
12/09/86.)   Office of  Health  and Environmental   Assessment,  Environmental
Criteria and Assessment Office, Cincinnati, OH.

N.N-Dlphenylamlne
Thomas, O.O., W.E. Rlbelln,  J.R.  Woodward and F.  DeEds.   1967.   The chronic
toxlclty 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.  1986.   Integrated Risk Information  System (IRIS).  Reference Dose
(RfD)  for   Oral  Exposure  for  Dlphenylamlne.   Online.    (Verification  date
07/22/86.)   Office of  Health  and Environmental   Assessment,  Environmental
Criteria and Assessment Office, Cincinnati, OH.

Direct lightfast 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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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.   1987a.   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.   1984b.  Integrated Risk  Information  System (IRIS):  Reference Dose
(RfD)  for   oral   exposure  for   endosulfan.    Online.    (Verification  date
03/18/87.)   Office of  Health  and  Environmental  Assessment,  Environmental
Criteria and Assessment Office,  Cincinnati, OH.

Endothall
Keller, 0.   1965.  Two-year chronic feeding  study of dlsodlum  endothall  to
beagle dogs.   Scientific Associates Report.   EPA  Pesticide  Petition 6G0503,
redesignated No.  7F0570, June 1966.  Accession No.  24601.

Pennwalt  Agchem.   n.d.   MRIO No. 00101735.  Available from  U.S.  EPA.   Write
to FOI, EPA, Washington, DC 20460.

U.S. EPA.   1986.   Integrated Risk Information  System (IRIS).  Reference Dose
(RfD)  for  Oral  Exposure  for  Endothall.   Online.  (Revised; verification date
11/25/86.)   Office  of  Health  and  Environmental  Assessment,  Environmental
Criteria and Assessment  Office, Cincinnati, OH.

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.

Endrin
Treon,  J.F., F.P. Cleveland  and J. Cappel.   1955.   Toxlcity  of  endrin for
laboratory  animals.  Agrlc. Food  Chem.  3: 842-848.

U.S. EPA.   1985a. Drinking  Water Criteria Document  for  Endrin.  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-84-176.   NTIS PB 86-117967.

U.S.  EPA.   1987.   Health  Effects  Assessment   for  Endrin.  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.  Integrated Risk  Information  System (IRIS):  Reference Dose
for  oral   exposure  for  Endrin.   Online.   (Verification  date  04/20/88.)
Office of  Health and Environmental  Assessment,  Environmental  Criteria and
Assessment Office, Cincinnati, OH.
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EpIchlorohydMn
Laskin, S., A.R. Sellakumar, M.  Kuschner,  et  al.   1980.   Inhalation  carcino-
genlcHy  of  epichlorohydrin  In  non-inbred  Sprague-Dawley  rats.   J.  Natl.
Cancer Inst.   65(4): 751-757.

Quast,  J.F.,   J.W.  Henck,  B.3.   Postma,   et  al.   1979.    Eplchlorohydrln
subchronlc studies.  I. A  90-day Inhalation  study  in Laboratory  Rodents.   80
submission.  Microfiche #206200.

U.S.  EPA.  1984.   Health  Assessment Document  for  Epichlorohydrin.   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.   Integrated Risk Information System (IRIS).  Reference Dose
(RfD)  for Oral  Exposure  for  Epichlorohydrin.  Online.   (Verification  date
12/18/85).   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.  Terrill,  D.J.  DeSousa and C.C. Conaway.
Inhalation  toxicology  of  ethylene  glycol   monoethyl  ether
rabbit.  Environ. Health Perspect.   57:  157-163.
                                                  1984. Subchronic
                                                   in  the  rat  and
 Doe,  J.E,
 monoethyl
 33-41.
  1984a.   Ethylene  glycol  monoethyl   ether  and  ethylene glycol
ether acetate  teratology  studies.  Environ. Health Perspect.  57:
                                    of  ethylene  glycol  and
                                     rats  and  B6C3F1  mice.
                                                   ethylene
                                                    Environ
glycol
Health
Melnlck,  R.L.   1984.   Toxlcitles
monoethyl  ether   in  Fischer  344/N
Perspect.  57:  147-155.

Stenger, E.G., A.  Lislott,  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.

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.
 0121h
                                     D-39
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2-Ethoxyethanol  acetate
Union  Carbide.   1984.   A  teratogenlc  evaluation of  Cellosolve Acetate  1n
Fisher  344   rats   and  New  Zealand  White  rabbits   following  Inhalation
exposure.     Bushy    Run   Research   Center,   Export,    PA,   October   1984.
FYI-AX-1184- 0360.

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 Haste 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.   Integrated  Risk  Information  System  (IRIS).   Reference
Dose  (RfD)  for  Oral  Exposure  for Ethyl  acetate.   Online.  (Verification date
06/11/86.)   Office  of  Health  and  Environmental  Assessment,  Environmental
Criteria and Assessment  Office,  Cincinnati, OH.

U.S.  EPA.   1986b.   Rat oral subchronic study with ethyl acetate.   Office of
Solid Waste, Washington. DC.

U.S.  EPA.   1986c.   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.

N-Ethvlaniline
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.   1985.   Integrated Risk  Information  System (IRIS): Reference Dose
{RfD)  for  oral  exposure  for  ethylbenzene.   Online.    (Verification  date
05/20/85.)   Office  of  Health   and  Environmental Assessment,   Environmental
Criteria and  Assessment  Office,  Cincinnati, OH.

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.
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Wolf, M.A., V.K. Rowe, D.D.  McColllster  et  al.   1956.   Toxlcological  studies
of certain alkylated benzenes and  benzene.   Arch.  Ind.  Health.   14:  387-398.
(Cited In 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.  (Cited 1n 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.  1987.   Integrated Risk Information System (IRIS).  Reference Dose
(RfD)   for  Oral   Exposure  for   S-Ethyl   Dlpropylthlocarbamate.    Online.
(Verification  date 05/20/87.)   Office  of  Health and  Environmental  Assess-
ment, Environmental Criteria and Assessment  Office, Cincinnati,  OH.

Ethylene cyanohydrln
Sauerhoff, M.W.,  W.H.  Braun,  O.C.  Ramsey,   C.B.  Humiston and  G.C.  Jersey.
1976.   lexicological evaluation  and pharmacoklnetlc  profile  of  B-hydroxy-
proplonltrlle  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.

Ethvlenedlamine
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
toxldty  of  ethylenedlamlne  in  laboratory  animals.   Fund. Appl.  loxicol.
3(6):  512-520.

Ethylene glycol                                                       ,  ,  .x
DePass,  L.R., R.H.  Garman, M.D.  Woodslde  et al.   1986a.   Chronic  toxlcity
and  oncogenlclty  studies of  ethylene glycol  1n  rats  and mice.  Fund. Appl.
Toxlcol.   7:  547-565.

Maronpot,  R.R., J.P.  Zelenak,  E.V.  Weaver  and  N.3.  Smith.   1983.  Terato-
genldty  study  of  ethylene  glycol  In  rats.   Drug.  Chenu  Toxlcol.   6(6):
579-594.
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U.S. EPA.   1987a.   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.   1987b.   Integrated Risk  Information  System  (IRIS):  Reference Dose
(RfD)  for  oral   exposure  for ethylene  glycol.   Online.   (Verification date
03/19/87.)   Office of  Health  and  Environmental  Assessment,  Environmental
Criteria and Assessment Office,  Cincinnati, OH.

Ethylene glycol  monobutyl  ether
Dodd, D.E., W.M. Snelllngs,  R.R.  Maronpot  and  B.  Balantyne.   1983.   Ethylene
glycol monobutyl ether: Acute,  9-day and 90-day  vapor  Inhalation  studies In
Fischer 344 rats.  Toxicol. 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 thiourea
U.S.  EPA.   1984.   Health  and  Environmental   Effects  Profile  for  Ethylene
Thiourea.   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  Biogenics Corp.   1986.   90-Day  gavage   study  1n  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  toxicity of  monomeric  ethyl  acrylate  and methyl methacrylate.
Toxicol. 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.
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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.

Fluoride
Hodge,  H.C.  and F.A.  Smith.   1965.   In:  Fluorine Chemistry, Vol.  IV,  J.H.
Simons, Ed.  Academic Press, New York, NY.  789 p.

U.S. EPA.  1986.   Integrated  Risk  Information System (IRIS).  Reference Dose
(RfD)  for  Oral  Exposure for  Fluoride.  Online.  (Verification date 02/26/86)
Office  of  Health  and   Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

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.

Flurldone
E11  Lilly and  Company.   1980.   Confidential  Business  Information;  unpub-
lished  study.   Accession  Nos. 070933, 070939.

U.S.  EPA.   1984.   Health and  Environmental  Effects Profile  for  Flurldone.
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.   Integrated Risk Information System (IRIS).  Reference Dose
(RfD)   for  Oral   Exposure   for   FluMdon.    Online.    (Verification  date
01/21/88.)   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.   1987.   Integrated Risk  Information System (IRIS).  Reference Dose
(RfD)  for  Oral  Exposure  for Folpet.  Online.  (Verification date  05/20/87.)
Office of Health  and  Environmental  Assessment,  Environmental  Criteria and
Assessment Office,  Cincinnati,  OH.

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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Furan
SRI  (Southern  Research  Institute).   1982b.   Subchronlc  toxlclty  report  on
furan  (C56202)  in  B6C3F1  mice.   Prepared  for  National Toxicology  Program
under Contract No. l-CP-95641-01, Bethesda, MD.

U.S. EPA.   1986.   Integrated  Risk Information System  (IRIS):  Reference Dose
(RfD) for  oral  exposure for furan.  Online.   (Verification  date 02/26/86.)
Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati,  OH.

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.

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  PavasHen  Kd Infection  SKV.  Hyg. Abt  1  orlg Relhe  B.
168(5-6): 442-451.

SRI  (Southern  Research  Institute).   1981.   90 day rat  report.   Unpublished
study performed for NTP.

U.S. EPA.   1987.   Integrated Risk Information System  (IRIS):   Reference Dose
(RfD)   for   oral   exposure   for  furfural.   Online.    (Verification   date
12/15/87.)   Office of   Health  and  Environmental   Assessment,  Environmental
Criteria and Assessment Office, Cincinnati, OH.

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.

Glycidaldehyde
Hlne,  C.H., R.J.  Guzman,  H.K.  Dunlap,  R.  Lima  and  G.S.  Loquvam.   1961.
Studies on the toxlclty of glyddaldehyde.  Arch.  Environ. Health.  2:  23-30.

U.S. EPA.   1987.   Integrated Risk Information System  (IRIS).   Reference Dose
(RfD)  for   Oral  Exposure for  Glycidaldehyde.  Online.   (Verification  date
12/15/87.)    Office of  Health  and Environmental  Assessment,  Environmental
Criteria and Assessment Office, Cincinnati, OH.

U.S.  EPA.    1989.   Health  and  Environmental  Effects  Document   for  Glycid-
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.

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 Waste
and Emergency Response,  Washington, DC.
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Heptachlor
Velslcol Chemical Corp.  1955.  MRID No. 00062599.  Available under FOI.

U.S.  EPA.   1987a.   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.   1987b.   Integrated Risk Information System (IRIS):  Reference Dose
(RfD)   for   oral  exposure   for   heptachlor.   Online.   (Verification  date
04/16/87.)   Office  of  Health  and  Environmental  Assessment,  Environmental
Criteria and Assessment  Office, Cincinnati,  OH.

Hexabromobenzene
Mendoza,  C.E..  H.M. V1Jay,  J.8.  Shields and  G.M.  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.   1985.  Integrated Risk  Information System  (IRIS).  Reference  Dose
 (RfD) for  Oral  Exposure for  Hexabromobenzene.   Online.   (Verification  date
 11/06/85.)   Office  of  Health and Environmental  Assessment,  Environmental
 Criteria  and Assessment  Office,  Cincinnati,  OH.

 Hexachlorobenzene                                           nrtoc          .
 Arnold,  D.L.,   C.A.  Hoodie.  S.M.  Charbonneau  et  al.   1985.   Long-term
 toxlclty  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
 bv 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   Integrated Risk  Information System (IRIS):  Reference Dose
 (RfD)  for  oral   exposure to  hexachlorobenzene.    Online.   (Verification date
 05/26/88.)   Office of  Health  and  Environmental  Assessment.  Environmental
 Criteria and Assessment Office, Cincinnati,  OH.

 Hexachlorobutadlene                                      Dac,,i*c   nf  ^  7 vpar
 Koclba,  R.J.,   D.G. Keys,  G.C.   Jersey,  et  al    1977.   Results   of  a  2-year
 chronic  toxlclty  study with  hexachlorobutadlene  In  rats.   Am.  Ind.  Hyg.
 Assoc. J.  38:  589-602.

 U  S    EPA     1984.    Health  Effects   Assessment  for  Hexachlorobutadlene.
 Prepared bv  the Office  of  Health and Environmental Assessment,  Environmental
 CrUerta and  Assessment Office,  Cincinnati,  OH  for  the Office  of Emergency
 and  Remedial Response,  Washington,  DC.
  01211.

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U.S. EPA.   1985.   Integrated  Risk Information System  (IRIS):  Reference  Dose
(RfO)  for   oral  exposure  for  hexachlorobutadlene.   Online.   (Verification
date  12/18/85.)   Office  of Health  and  Environmental  Assessment,  Environ-
mental Criteria and Assessment  Office,  Cincinnati, OH.

Hexachlorocyclohexane. gamma (Llndane)
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.   1986.   Integrated Risk  Information System (IRIS).   Reference  Dose
(RfD)  for  Oral Exposure  for gamma-Hexachlorocyclohexane.   Online.   (Verifi-
cation  date  01/22/86.)   Office  of   Health and  Environmental  Assessment,
Environmental  Criteria and Assessment Office, Cincinnati, OH.

Hexachlorocyclopentadlene
Abdo,  K.H., C.A.  Montgomery,  W.H.  Kluwe et al.   1984.  Toxldty  of  hexa-
chlorocyclopentadlene:  Subchronlc  (13-week)  administration  by  gavage to  F344
rats and 86C3F1 mice.   J. 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 ToxIcHy 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.   1985.   Integrated Risk Information  System  (IRIS):  Reference  Dose
(RfD)  for   oral  exposure to hexachlorocyclopentadlene.   Online.   (Verifica-
tion   date   10/09/85.)   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.   1987a.   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.   1987b.   Integrated  Risk Information  System (IRIS): Reference Dose
 (RfD)  for   oral exposure  for  hexachloroethane.    Online.   (Verification  date
04/16/87.)   Office  of  Health  and  Environmental  Assessment,  Environmental
Criteria and Assessment Office, Cincinnati,  OH.


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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.

Hexachlorophene
Nationwide  Chemical  Corporation.  1974.   Confidential  Business  Information;
unpublished study.  MRID No. 00055365.

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.   1988.   Integrated  Risk Information System (IRIS).   Reference Dose
(RfD)  for  Oral Exposure for  Hexachlorophene.    Online.   (Verification  date
02/25/88.)   Office  of  Health  and  Environmental Assessment,  Environmental
Criteria and Assessment  Office, Cincinnati, OH.

Hexamethylenediamine
U.S.  EPA.   1985.   Health  and  Environmental   Effects  Profile  for   Hexa-
methylenediamine.     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.O.,   J.L.  O'Donoghue,   G.D.  Dlvlncenzo  and  Terhaar.   1980.
Relative  neurotoxicity of methyl-n-butyl  ketone,  n-hexane  and their metabo-
lites.   Toxlcol. Appl. Pharmacol.  52(3):  433-441.

Ono, Y.,  Y.  Takeuchl,  N. Hlsanaga,  H.  Iwata, 3.  Kitoh and Y. Suglura.   1982.
Neurotoxicity  of  petroleum  benzene  compared  with  n-hexane.    Int.  Arch.
Occup.  Environ. Health.  50(3):  219-229.

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.

n-Hexanone
U.S. EPA.   1989.   Health and  Environmental Effects  Document for  n-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.

p-Hydroqulnone
Carlson,  A.J. and  N.R.  Brewer.   Toxlcity studies   on  Hydroguinone.   Proc.
Soc. Exp. Biol. Med.   84: 684-688.

U  S   EPA.   1987.   Health   and   Environmental  Effects  Document  for  Hydro-
quinone.  ' 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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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.   1986c.   Integrated  Risk  Information  System  (IRIS).   Reference
Dose  (RfD)  for  Oral  Exposure  for  Isobutanol.    Online.   (Verification  date
05/14/86.)  Office  of  Health  and Environmental  Assessment,  Environ- mental
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)  1n  F344/N  Rats  and B6C3F1  Mice
(Gavage Studies).  NTP Tech. Report Ser. No. 291, NIH Publ. No. 86-2547.

U.S.  EPA.   1986.  Integrated Risk Information  System  (IRIS):  Reference  Dose
(RfD)  for  oral  exposure  for  Isophorone.    Online.     (Verification  date
05/15/86.)   Office  of  Health  and  Environmental  Assessment,  Environmental
Criteria and Assessment Office, Cincinnati, OH.

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.

Isopropalln
Ell  Lilly  Company.   1985.   Confidential  Business  Information;  unpublished
study.

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.

U.S.  EPA.   1986.  Integrated  Risk  Information  System (IRIS).  Reference  Dose
(RfD)  for  Oral  Exposure  for  Isopropalln.   Online.     (Verification  date
06/24/86.)  Office of  Health  and Environmental Assessment,  Environmental
Criteria and Assessment Office, Cincinnati, OH.
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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.   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.

U.S.  EPA.   1986.   Integrated Risk  Information  System  (IRIS):  Reference Dose
(RfD)  for  oral  exposure  for  gamma-hexachlorocyclohexane.   Online.  (Verifi-
cation  date  01/22/86.)    Office  of  Health and Environmental  Assessment,
Environmental Criteria and Assessment Office, Cincinnati, OH.

Lead  alkyls
Scheper,   G.W.H.    1964.    Tetraethyl  lead  and  tetramethyl   lead.   Arch.
Environ. Health.  8: 277-295.

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.  Confidential Business Informa-
tion;  unpublished study.  HRID No.  00018374.

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.   1986.   Integrated  Risk  Information System (IRIS).  Reference Dose
(RfD)   for   Oral   Exposure  for   Llnuron.    Online.    (Verification   date
05/14/86.)   Office  of   Health  and Environmental  Assessment, Environmental
Criteria and  Assessment Office, Cincinnati,  OH.

Malathlon
Moeller,  H.C.  and   J.A.  Rider.    1962.   Plasma  and red  blood  cell-cholin-
esterase  activity as Indications  of the threshold  of  Incipient  toxlcity of
ethyl-p-nltrophenol  thlonebenzenephosphorate  (EPN) and  malathlon  In  human
beings.   Toxlcol. Appl.  Pharmacol.   4:  123-130.

U.S.  EPA.   1984.   Health  and  Environmental Effects Profile  for Malathlon.
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.   Integrated Risk  Information  System (IRIS).  Reference Dose
 (RfD)  for  Oral   Exposure   for   Malathlon.   Online.     (Verification  date
03/18/87.)    Office  of  Health  and  Environmental  Assessment, Environmental
Criteria  and  Assessment  Office,  Cincinnati, OH.
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Malelc anhydride
Jessup,  D.C.,   D.  AldMdge,  J.L.   Schardein  and  M.  Blair.   1982.   Three-
generation  reproduction  study  In  rats  (modified  to a  2-generat1on  study).
Malelc  anhydride  IR-79-358.   International  Research  and  Development  Corp.
for Monsanto Co., St. Louis, Mo.   Unpublished  80 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.   1988.   Integrated Risk  Information  System (IRIS).   Reference Dose
(RfD)  for  Oral Exposure  for  Malelc Anhydride.   Online.   (Verification date
03/24/88.)   Office  of  Health  and  Environmental  Assessment,  Environmental
Criteria and Assessment Office, Cincinnati, OH.

Malelc hydrazlde
U.S.  EPA.   1988.   Integrated Risk  Information System  (IRIS).   Chemical File
for   Malelc  Hydrazlde.    Online.    Office   of  Health   and  Environmental
Assessment, Environmental Criteria  and Assessment Office, Cincinnati,  OH.

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.

Van der  Heljden,  C.A.,  E.M.  Den Tonkelaar,  3.M.  Garbls-Berkvens  and G.J. Van
Esch.   1981.   Malelc hydrazlde, cardnogenlclty  study  1n  rats.   Toxicology.
19(2): 139-150.

MalononUrlle
Panov, I.,  M.  Zlateva and  G.  Antov.  1972.   Tox1colog1cal  characteristics of
dlcyanomethane.   Chronic  effects   In  white  rats.   Kh1g.  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.  MRIO No. 00161552.  (Cited 1n U.S.  EPA. 1987)
0121H                               D-50                             01/11/90

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Rohm and Haas Co.  1977.   MRID No. 00129980.  (Cited In U.S.  EPA,  1987)

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.  1987.   Integrated Risk Information System (IRIS).  Reference Dose
(RfD)  for  Oral  Exposure  for  Maneb.   Online.   (Verification  date  10/14/87.)
Office  of  Health  and Environmental  Assessment,  Environmental Criteria  and
Assessment Office,  Cincinnati, OH.

Manganese
Lai,  3.C.K.,  T.K.C.  Leung  and  L. Lim.   1982c.   Activities  of the mitochon-
dria!  NAD-linked  Isocitrlc  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.  Hein and  S.D.  Carter.   1982.   Effects of
chronic  manganese   (Mn304)   exposure   on   selected reproductive  parameters
1n  rats.   J. Toxlcol. Environ. Health.  9:  677-687.

Leung,  T.K.C.,  3.C.K. Lai  and  L. Lim.   1981.   The regional  distribution of
monoamlne  oxldase  activities  towards  different  substrates:  Effects  in  rat
brain of  chronic  administration  of  manganese chloride  and  of  aging.   3.
Neurochem.   36(6): 2037-2043.
 SaMc,  M.
 manganese.
S. Harkicevlc  and 0.  Hrustlc.
Br. 3. 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                                             P1,       __   .  c  ,
 US—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,  alkyl  and
 Clarkson,  T.W.,  L
 ceedlngs.   35(12):
        inorganic
       .  Amin-Zaki
        2395-2399.
and S.K.  Al-Tlkrltl.   1976.   Federation  Pro-
 Nordberg.  G.F.  and  P.  Strangert.    1976.   Estimations  of  a  dose-response
 curve  for  long-term  exposure  to  methylmercurlc  compounds  In human  be ngs
 taklnq into  account  variability of critical organ  concentration  and  blolog-
 Ua  haf-tlme: A  preliminary  communication.   In:  Effects  and Dose-Response
 Relationships of Toxic Metals    G.F.  Nordberg,  Ed.   Elsevler,  Amsterdam,   p.
 273-282.
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U.S.  EPA.   1980b.   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.   1985.   Integrated  Risk  Information System  (IRIS): Reference Dose
(RfD)  for  oral  exposure for  methyl  mercury.   Online.   (Verification  date
12/02/85.)    Office  of  Health  and  Environmental  Assessment,  Environmental
Criteria and Assessment Office, Cincinnati, OH.

WHO  (World Health Organization).   1976.   Environmental health criteria  for
mercury,  ^ru Environmental  Health Criteria 1.   WHO, Geneva.

Mercury, mercuric
Andres,  P.  1984.   IgA-IgG disease  1n  the Intestine  of  Brown Norway  rats
Ingesting mercuric chloride.  CUn.  Immunol.  Immunopathol.  20: 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
glomerulonephrltls   Induced  by  HgCl2  1n  the   Brown Norway  rat.    Ann.
Immunol.   129C: 777-792.

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  Review Workshop on  Mercury Issues.  October  26-27,
1987,   Summary   Report.    Environmental   Criteria   and Assessment   Office,
Cincinnati, OH.

Merphos
Abou-Don1a, M.B., D.G.  Graham,  P.R. Tlmmons and B.L.  Relchert.   1980.  Late
acute,  delayed neurotoxlc  and  chollnerglc effects of  S.S.S-trlbutylphos-
phorotrlthlolte (merphos) In hens.   Toxlcol. 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.  1987.  Integrated  Risk Information System (IRIS).   Reference Dose
(RfD)   for  Oral   Exposure  for    Merphos.    Online.   (Verification  date
08/13/87.)    Office  of  Health  and  Environmental  Assessment,  Environmental
Criteria and Assessment Office, Cincinnati, OH.
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Merphos oxide
Abou-Don1a, H.B.,  D.G.  Graham,  K.M.  Abdo  and  A.A. Kernel!.   1979.   Delayed
neurotoxlc,  late  acute and  chollnerglc effects  of S,S,S-tr1butylphosphoro-
trlthloate  (DEF):  Subchronlc  (90 days)  administration  In  hens.   Toxicology.
14: 229-243.

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.

U.S.  EPA.   1987.   Integrated  Risk Information System (IRIS).  Reference Dose
(RfD)  for  Oral  Exposure  for  Merphos  Oxide.   Online.   (Verification  date
08/13/87.)   Office  of  Health  and  Environmental  Assessment,  Environmental
Criteria and Assessment Office, Cincinnati,  OH.

MethacrylonUrlle
Pozzanl,  U.C., C.R.  Klnkead  and 3.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
N1tr1les.   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.   1987b.   Integrated Risk Information System  (IRIS): Reference Dose
(RfD)  for oral exposure  for  methacrylonltrlle.  Online.   (Verification date
09/17/87.)   Office  of Health  and  Environmental  Assessment, Environmental
Criteria  and Assessment Office, Cincinnati,  OH.

Hethomyl
Kaplan,   A.M.   and   H.   Sherman.   1977.    Toxlclty   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    1988.    Health  and  Environmental  Effects  Document for  Methomyl.
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~SEPA1984    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.


                ..  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.
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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.

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 Haste 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
Tox1c1ty  Research Laboratory.    1986.   Rat  oral  subchronlc  toxldty  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
KHmlsch,  H.J.  and  W.  Relnlnghaus.   1984.   Carc1nogen1c1ty 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  bromide
Danse,  L.H.O.C.,  F.L.  van Ve.sen and C.A.  van  der Heljden.  1984.   Methyl-
bromide:  Carcinogenic  effects   In   the  rat   forestomach.   Toxlcol.   Appl.
Pharmacol.  72: 262-271.

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.   1988.   Integrated Risk Information System (IRIS).  Reference Dose
(RfD)   for  Oral  Exposure  for  Methyl  Bromide.   Online.   (Verification date
05/26/88.)   Office  of  Health  and  Environmental   Assessment,  Environmental
Criteria and Assessment Office, Cincinnati,  OH.
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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-Hethy1-4-ch1orophenoxy acetic acid  (HCPA)
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.

U.S.  EPA.   1988.   Integrated Risk Information System (IRIS).  Reference Dose
(RfD)  for  Oral  Exposure for MCPA.   Online.   (Verification date 06/22/88.)
Office  of   Health  and  Environmental  Assessment,  Environmental  Criteria and
Assessment  Office, Cincinnati, OH.

4-(2-Methvl-4-chloroDhenoxv)  butyric  acid  (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   1987.  Integrated Risk Information System  (IRIS).   Reference Dose
 (RfD)  for  Oral  Exposure for MCPB.   Online.  (Verification  date  10/14/87.)
Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria and
Assessment  Office,  Cincinnati,  OH.

 2-(2-Methvl~4-ch1orophenoxv) propionic  acid (MCPP)
 BASF  Aktiegerellschaft.1985.ConfidentialBusiness  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.
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U.S. EPA.   1988.   Integrated  Risk  Information System (IRIS).  Reference Dose
(RfD)  for  Oral Exposure  for  MCPP.  Online.   (Verification  date 10/12/88.)
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.6.,   J.W. Henck,  6.C.  Jersey,  R.J.  Kodba,  D.J.  Schwetz  and  T.D.
Landry.   1982.   Methylene  bromide: A 90-day  repeated  Inhalation  toxiclty
study  1n  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  Toxiclty and  Oncogen-
icity  Study  of   Methylene  Chloride in  Rats.   Final  Report.   Prepared  by
Hazleton Laboratories America, Inc., Vienna. VA.  (Unpublished).

Nitschke. K.D.,  O.D.  Bured, T.J. Bell, et al.   1988.   Methylene chloride:  A
2-year  inhalation toxiclty and  oncogenlcity  study In  rats.  Fund.  Appl.
Toxicol.  (In  press)

U.S. EPA.   1985.   Integrated  Risk  Information System  (IRIS):  Reference  Dose
{RfD)  for  oral  exposure for   dlchloromethane.   Online.  (Verification  date
11/06/85.)   Office of  Health  and  Environmental  Assessment,  Environmental
Criteria and Assessment Office, Cincinnati, OH.

4.4'-Methy1enediphenyl  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  ethyl ketone
LaBelle, C.W.   and H.  Brieger.  1955.   Vapour  toxiclty  of  a  composite solvent
and Its principal  components.   Arch. Ind.  Health.   12:  623-627.

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.
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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.

Methyl Isobutyl ketone
Microbiological  Associates.   1986.   Subchronlc toxldty of  methyl  Isobutyl
ketone  In   Sprague-Dawley  rats.   Preliminary  report  for Research  Triangle
Institute,  RTP, NC.  Study No. 5221.04.  January.

Union  Carbide  Corp.  1983b.   Ninety-day Inhalation study  In rats  and  mice
sponsored by CMA.  U.S.  EPA/OTS public files 0750507469.

U.S.  EPA.   1986.   Integrated Risk Information  System  (IRIS):  Reference  Dose
(RfD)  for  oral  exposure for methyl  Isobutyl  ketone.   Online.  (Verification
date  05/30/86).    Office  of  Health  and  Environmental Assessment,  Environ-
mental Criteria and Assessment Office, Cincinnati, OH.

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.

Methyl Isocyanate
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 toxldty  of  monomerlc  ethyl acrylate  and  methyl methacrylate.
Toxlcol. Appl. Pharmacol.  6: 29-36.

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.
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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.  1986.  Integrated Risk  Information  System (IRIS).   Reference Dose
(RfD)  for  Oral  Exposure for Methyl  Parathlon.  Online.   (Verification date
12/09/86.)    Office   of  Health  and  Environmental  Assessment,  Environmental
Criteria and Assessment Office,  Cincinnati, OH.

Methyl styrene
MRI  (Midwest  Research Institute).   1984a.  Study of  the  Inhalation cardno-
genlclty (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.   lexicological
studies  of  certain  alkylated  benzenes and  benzene.   Arch.  Ind.  Health.  14:
387-398.

Mlrex
Shannon, V.C.   1976.  The  effects of mlrex  on  the reproductive  performance
and  behavioral  development  1n  the  prairie  vole  (Mlcrotus  ochroqaster).
Ph.D.  Dissertation,  Iowa State University,  Ames, IA.

U.S.  EPA.   1987a.   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.   1987b.   Integrated  Risk Information System (IRIS): Reference Dose
(RfD)  for  oral  exposure for mlrex.   Online.   (Verification  date 04/15/87.)
Office  of  Health  and Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

Hollnate
Stauffer Chemical Company.  1981.   MRID No. 00079209.  U.S.  EPA, Washington,
DC.

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.
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U.S. EPA.  1988.   Integrated  Risk  Information  System (IRIS).   Reference  Dose
(RfD)  for   Oral   Exposure   for   Mollnate.    Online.    (Verification   date
03/23/88.)   Office  of  Health  and  Environmental  Assessment,  Environmental
Criteria  and Assessment Office, Cincinnati, OH.

Honochlorobutane
NTP  (National   Toxicology  Program).   1986.   Toxicology  and  carclnogenesls
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,  3.R.  Borzelleca  and G.R.  Hennigar,  Jr.  1976.
Long-term toxicologic assessment of  nickel In  rats  and  dogs.  3.  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   1987    Integrated  Risk  Information System (IRIS): Reference Dose
 {RfD)  for oral  exposure for  nickel,  soluble   salts.  Online.   (Verification
date 07/16/87).   Office  of  Health  and  Environmental  Assessment,  Environ-
mental 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.

Nitrite
U.S. EPA.   1986.  Integrated Risk  Information System (IRIS).   Reference Dose
(RfD) for Oral  Exposure for  Nitrite.   Online.   (Verification  date 01/26/86.}
Office  of  Health and  Environmental Assessment,  Environmental Criteria  and
Assessment Office, Cincinnati,  OH.

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.

Walton,  G.  1951.  Survey of literature relating to Infant methemogloblnemla
due to nitrate-contaminated water.   Am. a. Pub.  Health.   41:  986-996.

N1troan1l1nes
U.S. EPA.   1985.  Health and Environmental  Effects  Profile for NHroanlllnes
(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  1n  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.   1985.  Integrated Risk   Information  System (IRIS):  Reference Dose
(RfD)  for  oral  exposure   for  nitrobenzene.   Online.   (Verification  date
07/08/85.)   Office   of  Health  and  Environmental  Assessment,  Environmental
Criteria and Assessment Office, Cincinnati,  OH.

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.

NUrofurantoln
SRI  (Southern   Research  Institute).   1980.   Subchronlc  Toxldty Report  on
NUrofurantoln  (C55196) In  Flscher-344 rats and  B6C3F1  mice  Tracor JU  CO,
Inc. Rockvllle,  MO contract  Nos N01-CP-43350 and 78-65-106002  U.S. EPA.

U.S. EPA.   1987.  Health and Environmental  Effects  Document  for  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.
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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.

NUromethane
U.S.  EPA.   1985.    Health   and   Environmental   Effects  Profile  for   NHro-
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 NHrophenols.   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  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.

Nltrotoluenes
Clss, M.,  N.  Huyen,  H.  Dutertre,  N. Phu-L1ch and R.  Truhaut.  1980.   Toxico-
loglcal  study  of  nitrotoluenes:  Long-term  toxldty.   Dakar Medical.   25:
293-302.

U.S. EPA.   1986.  Health  and Environmental  Effects  Profile for  Nltrotoluenes
(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  metaolism  1n rats by  bromi-
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.   1986.  Integrated Risk Information System  (IRIS).  Reference Dose
(RfD)  for  Oral Exposure for Octabromodlphenyl ether.  Online.  (Verification
date  05/15/86.)  Office  of  Health  and  Environmental  Assessment,  Environ-
mental Criteria and Assessment Office,  Cincinnati, OH.

Octamethylpyrophosphoramide
Rider, J.A.,  H.C. Moeller,  E.3.  Pulettl and J.I. Swader.  1969.   Toxldty of
parathlon,  systox,  octamethylpyrophosphoramlde and  methyl parathlon  1n man.
Toxlcol. Appl. Pharmacol.  14(3): 603-611.
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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.   A1r  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.

ParathIon
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.

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.  Confidential Business Information; unpub-
lished study.  MRID No. 0058657.

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.   1987.  Integrated Risk  Information  System  (IRIS).   Reference Dose
(RfD)  for  Oral  Exposure  for   Pendlmethalln.   Online.   {Verification   date
09/16/87.}    Office of  Health   and Environmental  Assessment,  Environmental
Criteria and  Assessment Office,  Cincinnati, OH.

Pentabromodlphenyl 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.


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U.S. EPA.  1986.   Integrated  Risk  Information  System (IRIS).   Reference  Dose
(RfD) for  Oral  Exposure  for  Pentabromodlphenyl  Ether.   Online.   (Verifica-
tion  date  05/15/86.)    Office   of   Health  and  Environmental   Assessment,
Environmental  Criteria and Assessment Office, Cincinnati, OH.

Pentachlorobenzene
Under,   R.,   T.   Scottl,  J.  Goldstein  and K.  McElroy.   1980.   Acute  and
subchronic  toxlclty  of  pentachlorobenzene.   J.  Environ.  Pathol.  Toxlcol.
4(5-6):  183-196.

U.S. EPA.  1985.   Integrated  Risk  Information  System (IRIS).   Reference  Dose
(RfD) for  Oral  Exposure  for  Pentachlorobenzene.  Online.  (Verification  date
10/09/85.)   Office  of  Health  and  Environmental Assessment,  Environmental
Criteria and Assessment Office, Cincinnati, OH.

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.

Pentachlorocyclopentad1ene
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 Haste and Emergency Response, Washington,  DC.

Pentachloronitrobenzene
Olln Corporation.  1968.   MRID NO. 000114201.  U.S. EPA, Washington,  DC.

U.S. EPA.   1986.   Health and Environmental  Effects  Profile for  Pentachloro-
nitrobenzene.    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.  1987.   Integrated  Risk  Information  System (IRIS).   Reference  Dose
(RfD) for  Oral  Exposure  for  Pentachloronitrobenzene.  Online.  (Verification
date  04/15/87.)   Office  of  Health   and  Environmental   Assessment,  Environ-
mental Criteria and Assessment Office, Cincinnati, OH.

Pentachlorophenol
Schwetz,  B.A.,  J.F.  Quast,  P.A.  Keeler  et al.   1978.   Results  of  two-year
toxldty  and  reproduction studies on  pentachlorophenol  in  rats,   in:  Penta-
chlorophenol:   Chemistry,  Pharmacology  and  Environmental  Toxicology,  K.R.
Rao, Ed.  Plenum Press, New York.  p.  301.   (Cited in 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.   1985.   Integrated Risk Information  System (IRIS):  Reference  Dose
(RfD) for  oral  exposure  for  pentachlorophenol.   Online.  (Verification  date
05/20/85).   Office  of  Health  and  Environmental Assessment,  Environmental
Criteria and Assessment Office, Cincinnati,  OH.
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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.

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.

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.   1988.   Integrated Risk  Information System  (IRIS):  Reference Dose
(RfD)  for   oral exposure for  phenol.   Online.   {Revised verification  date
11/16/88).   Office of  Health  and  Environmental Assessment,  Environmental
Criteria and Assessment  Office,  Cincinnati, OH.

Phenylenedlamlnes  (o-j  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-Pheny1ened1amine
Hofer,  H. and  R.  Hruby.   1982.   Ninety-day toxldty  study with  m-phenylene-
dlamlne on  rats.   Oestrr. Forschungszent.  Selbersdorf  {Ber.)   OEFZS  Ber.  No.
4155.  p. 50.
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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 Haste and Emergency Response, Washington,  DC.

U.S. EPA.  1986.   Integrated  Risk Information  System  (IRIS).   Reference  Dose
(RfD)  for  Oral  Exposure  for m-Phenylenediam1nes.   Online.   (Verification
date  02/26/86.)    Office  of  Health  and  Environmental  Assessment,  Environ-
mental 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.

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 acids
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-Phthalic acid
CUT (Chemical  Industry Institute  of  Technology).  1982.   A Ninety-Day Study
of  Terephthallc Add-Induced Urollthiasls  and  Reproductive  Performance in
Wlstar  and CD rats.  CUT,  Research Triangle Park, NC.

Gross   3.    1974.   The  Effects  of  Prolonged  Feeding  of  Terephthalic  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.


                      Institute).  1979.  Bloassay of phthallc anhydride for
possible  cardnogenldty.   NCI Cardnogenesis Tech.  Rep.  Ser. No. 159.   Nllb
PB293594.
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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 Haste and Emergency Response,  Washington, DC.

U.S. EPA.  1988.  Integrated Risk  Information System (IRIS).   Reference Dose
(RfO) for Oral Exposure for Phthallc Anhydride.   Online.   {Verification date
04/24/88.)    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.

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.

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.

Propachlor
Monsanto  Company.   1964.  Confidential   Business   Information;  unpublished
study.  MRID NO. 00094370.

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.  1986.  Integrated Risk  Information System (IRIS).   Reference Dose
(RfD)  for  Oral  Exposure  for  Propachlor.    Online.    (Verification   date
07/22/86.)    Office  of  Health  and  Environmental  Assessment,  Environmental
Criteria and Assessment Office,  Cincinnati, OH.

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.  1987.  Integrated Risk  Information  System (IRIS).   Reference Dose
(RfD)  for  Oral   Exposure   for   Propazlne.    Online.    (Verification   date
05/20/87.)   Office  of  Health  and Environmental  Assessment,  Environmental
Criteria and Assessment Office,  Cincinnati, OH.
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ProplonUrUe
U.S.  EPA.    1985.   Health  and  Environmental  Effects   Profile  for  Propio-
nltrile.    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.   1987a.  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 qlycol
Gaunt, I.F.,  R.M.B. Carpaninl,  P.  Grasso and  A.B.G. Lansdown.   1972.   Long-
terra  tox1c1ty  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 toxldty 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 qlycol monoethyl ether
Smyth, H.F.,  Jr.  and   C.P.   Carpenter.   1948.   Further  experience with  the
range  finding test In  the  Industrial  toxicology laboratory.   3.  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.

Propylene qlycol monomethyl ether
Miller,  R.R.,  E.A.  Herman,  J.T.  Young et  al.   1984.   Ethylene glycol mono-
methyl ether  and  propylene  glycol monomethyl ether: Metabolism, disposition,
and  subchronlc  Inhalation toxlclty studies.   Environ.  Health  Perspect.   57:
233-239.

Rowe,  V.K.,  D.D.  HcColllster,  H.C.   Spencer  et al.   1954.   Toxicology of
mono-, dl-, and trl-propylene glycol methyl  ethers.  Arch.  Ind.  Hyg. Occup.
Med.  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.


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 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.

 Pyrldlne
 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  subchronU  oral  toxldty In  rats.
 Sponsored by Office of Solid Waste. Washington. DC.

 U.S.  EPA.   1987.   Integrated  Risk  Information System (IRIS).  Reference Dose
 (RfD)   for   Oral   Exposure   for   Pyrldlne.    Online.    (Verification  date
 08/13/87.)   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   tox1c1ty/cardnogen1c1ty   study   of   hexahydro-1,3,5-
 tr1n1tro-l,3,5-tr1az1ne   (RDX)  1n   the  Fischer  344  rat.    NTIS  AD-A160774.
 Vol.  1.  347 p.

 U.S.  EPA.   1988.   Integrated  Risk  Information System (IRIS).  Reference Dose
 (RfD)  for  Oral  Exposure   for  Hexahydro-1,3,5-tr1n1tro-l,3,5-tr1az1ne  (RDX).
 Online.   (Verification  date  04/20/88.)   Office of  Health  and Environmental
 Assessment, Environmental  Criteria  and Assessment Office, Cincinnati,  OH.

 U.S.   EPA.    1989.    Health   and  Environmental   Effects  Document  for  RDX
 (CyclonHe).   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.

 Ronnel
 McColllster, D.D.,  F. Oyen and  V.K.  Rowe.   1959.   lexicological  studies  of
 0,0-d1methyl-o-(2,4,5-tr1chlorophenyl)phosphoth1oate  (ronnel)   In  laboratory
 animals.  3. AgrU. 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.

 Selenium
 U.S. EPA.  1985.   Integrated  Risk  Information System (IRIS).  Reference Dose
 {RfD)  for  Oral  Exposure   for  Selenlous  Add.   Online.   (Verification  date
 08/19/85.)    Office  of  Health  and  Environmental  Assessment,  Environmental
 Criteria and Assessment  Office,  Cincinnati, OH.
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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.

Yang, G., W. Shuzhen, R. Ahou  and  S.  Sun.   1983.  Endemic selenium Intoxica-
tion of humans 1n China.  Am. J. Clln. Nutr.  37: 872-888.

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.

Sodium cyanide
Howard,  J.W.  and  R.F.  Hanzal.   1955.   Chronic toxidty for  rats of  food
treated with hydrogen cyanide.  Agrlc. Food Chem.  3: 325-329.

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.   1985.  Integrated Risk Information System  (IRIS):  Reference  Dose
(RfD)  for  oral  exposure  for  sodium cyanide.   Online.   (Verification  date
08/05/85.)    Office  of  Health  and  Environmental Assessment,  Environmental
Criteria and Assessment Office, Cincinnati, OH.

Sodium diethyldithlocarbamate
Sunderman,   F.W., O.E. Paynter  and R.B. George.   1967.  The  effects  of the
protracted administration of  the  chelating agent, sodium diethyldithlocarba-
mate (dithlocarb).  Am. 3.  Med. Scl.   254:   46-56.

U.S.  EPA.   1985.  Integrated Risk Information System  (IRIS):  Reference  Dose
(RfD)   for   oral   exposure  for   sodium   dlethyldlthiocarbamate.    Online.
(Verification date  10/09/85.)  Office  of  Health and  Environmental  Assess-
ment, Environmental Criteria and Assessment Office, Cincinnati, OH.

U.S.  EPA.    1988.   Health  and  Environmental  Effects  Document   for  Sodium
Dlethyldlthiocarbamate.  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.

Sodium metavanadate
Domingo, J.L.,  J.L.  Llobet,  J.M.  Tomas and  J.  Corbella.   1985.   Short-term
toxicity studies  of vanadium  In rats.   J. Appl.  Toxicol.  5(6): 418-421.

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.
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Styrene
Quast,  J.F.,   C.6.  HumUton,  R.T.  Kalnlns,  et  al.   1979.   Results  of  a
Toxlclty Study  of  Monomerlc Administered  to  Beagle Dogs by  Oral  Intubation
for  19 Months.   Toxicology Research  Laboratory,  Health  and  Environmental
Sciences,  Dow Chemical Co., Midland, HI.   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.   1985.   Integrated Risk Information  System (IRIS).   Reference Dose
(RfD)   for   Oral   Exposure  for   Styrene.    Online.   (Verification   date
10/09/85.)   Office of  Health  and  Environmental   Assessment,  Environmental
Criteria and Assessment Office, Cincinnati, OH.

Succ1non1tr11e
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.

Sulfurlc acid
Carson,  8.L.,   B.L.  Herndon,   H.V.  Ellis  III, et  al.   1981.   Sulfurlc Add
Health Effects.   Prepared  under  Contract  68-03-2928  by Midwest  Research
Institute,  Kansas  City,   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.

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 add
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.
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Tetrachloroazobenzene (TCAB)
U.S. EPA.   1985.   Health and  Environmental  Effects  Profile for 1CAB,  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.

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.

Tetrachlorocyclopentadiene
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 (perchloroethylene)
Buben,  J.A.  and  E.J.  O'Flaherty.  1985.  Delineation  of  the  role  of metabo-
lism  In  the  hepatoxldty   of  trlchloroethylene and perchloroethylene:  A
dose-effect  study.  Toxlcol. Appl. Pharmacol.  78: 105-122.

U.S. EPA.   1987.   Integrated RUk  Information System (IRIS):  Reference Dose
(RfD)  for  oral   exposure  for  tetrachloroethylene.    Online.   (Verification
date  09/17/87.)    Office  of  Health  and  Environmental Assessment,  Environ-
mental Criteria and Assessment Office, Cincinnati, OH.

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.

Tetrachlorohydrazobenzene (TCHB)
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   Oral
Toxlcity Study in Rats Office  of  Solid Waste, Washington,  DC.

U.S. EPA.   1987a.  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    1987b.    Integrated  Risk  Information System  (IRIS).    Reference
Dose   (RfO)  for   oral   exposure  for  2,3,4,6-Tetrachlorophenol.   Online.
(Revised;  verification date  08/13/87).   Office  of  Health and Environmental
Assessment,  Environmental Criteria  and Assessment Office,  Cincinnati, OH.
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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   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.

Tetrachlorovlnphos (Stlrofos)
Shell  Chemical  Company.   1968.    Confidential  Business  Information;  unpub-
lished  study.  Accession No. 115684.

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.   1986.   Integrated Risk Information  System (IRIS).  Reference Dose
(RfD)   for   Oral   Exposure  for   Tetrachlorovlnphos   {Stlrofos).    Online.
(Verification date 09/02/86.)   Office of  Health and  Environmental  Assess-
ment, Environmental Criteria and  Assessment Office, Cincinnati, OH.

Thallium  and Compounds:
Thallium  (In salts).  ThalHum(I) oxide fThalllc oxldel. ThalHum(I) acetate.
Thalllum(I) carbonate.  Thalllum(I) chloride.  Thallium  (I)  nitrate. Thallium
selenlte  (T1?Se). Thalllum(I) sulfate
HRI  (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 1n U.S.  EPA, 1987a)

U.S.  EPA.   1986b.  Subchronlc (90-day) toxlclty  of  thalHum(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.   1988a.   Health and  Environmental  Effects  Document  for Thallium
and  Compounds.   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.   1988b.   Integrated  Risk Information System (IRIS): Reference Dose
(RfD)  for oral exposure  for thalllc  oxide,  thalllum(I) acetate. thallium(I)
carbonate,  thalHum(I)  chloride, thalllum(I)  nitrate,  thallium  selenlte and
thalllum(I)  sulfate.   [Separate  IRIS entry  for  each  compound.]  Online.
(Revised;  verification  date 04/21/88.)   Office  of  Health  and Environmental
Assessment, Environmental  Criteria  and Assessment  Office, Cincinnati, OH.

2-(Th1ocyanomethylth1o)benzothiazole  (TCHTB)
U.S.  EPA.    1984.   Health  and  Environmental  Effects  Profile   for  TCM1B.
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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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.  1987.   Integrated  Risk Information  System (IRIS).   Reference Dose
(RfD) for  Oral  Exposure  for  Thlram.   Online.  (Verification date 04/15/87.)
Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

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.

Tin and compounds
NTP   (National   Toxicology   Program).    1982.    Cardnogenesls  bioassay   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  1n  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.   1985a.   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.
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U.S. EPA.  1985b.  Integrated Risk  Information  System (IRIS):  Reference Dose
(RfD)  for   oral  exposure   for   toluene.    Online.    (Verification   date
05/20/85.)   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.  lexicological  studies
of  certain  alkylated  benzenes  and   benzene.   Arch.   Ind.  Health.  14:  387.
(Cited in U.S. EPA, 1985)

Toluenediamine (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 Haste, Washington, DC.

Toluene-2.5-d1amine
NCI  (National  Cancer  Institute).   1978.   Bloassay   of  Toluene-2,5-dlam1ne
Sulfate  for  Possible  Carclnogeniclty.   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.

Toluene-2.6-diainine
NCI  (National  Cancer  Institute).    1980.    Bloassay of  2,6-Toluenedlamlne
Dlhydrochlorlde  for  Possible  Carclnogeniclty.   NCI Carclnogenesls 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-Toluidine
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.

Triallate
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.  1986.   Integrated Risk Information  System  (IRIS).  Reference Dose
(RfD)   for   Oral  Exposure  for  Trlallate.    Online.   (Verification  date
12/16/86.)   Office  of  Health  and   Environmental  Assessment,  Environmental
Criteria and Assessment Office, Cincinnati,  OH.
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1,2.4-Tribromobenzene
Carlson,  G.P.  and  R.G.  Tardiff.   1977.  Effect  of  1,4-dlbromodibenzene  and
1,2,4-tMbromobenzene  on xenoblotic  metabolism.   Toxicol.  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.   1986.   Integrated  Risk  Information System (IRIS).  Reference Dose
(RfD)  for Oral  Exposure for  1,2,4-Tr1bromobenzene.   Online.   (Verification
date  05/15/86.)    Office of  Health   and  Environmental Assessment,  Environ-
mental Criteria and Assessment Office, Cincinnati, OH.

1,2,4-Trichlorobenzene
Carlson,  G.P.  and  R.G.  Tardiff.   1976.  Effect  of  chlorinated benzenes  on
the metabolism of  foreign organic  compounds.   Toxicol. Appl. Pharmacol.  36:
383-394.

U.S.  EPA.   1986.   Integrated  Risk Information System  (IRIS):  Reference Dose
(RfD)  for oral  exposure to 1,2,4-trlchlorobenzene.   Online.   (Verification
date  02/26/86.)    Office of  Health   and  Environmental Assessment,  Environ-
mental Criteria and Assessment Office, Cincinnati, OH.

U.S.  EPA.   1987.   Health  Effects   Assessment   for  1,2,4-Trichlorobenzene.
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.

Watanabe, P.G.,  R.O.  Kodba,  R.E.  Hefner et  al.   1978.   Subchronic  toxlcity
studies  of  1,2,4-trlchlorobenzene  in  experimental  animals.  Toxicol.  Appl.
Pharmacol.  45(1):  322-333.

Trlchlorocyclopentadiene
U.S.  EPA.   1988.   Health and  Environmental  Effects  Document for Chlorinated
Cyclopentadienes.   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-Trichloroethane
Torkelson, R.R., F. Oyen, D.D.  McCollister  and V.K.  Rowe.   1958. Toxlcity of
1,1,1-trichloroethane   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-Trichloroethane.
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):  Reference Dose
(RfD)  for oral  exposure for  1,1,1-trichloroethane.   Online.   (Verification
date  05/15/86.)    Office of  Health   and  Environmental Assessment,  Environ-
mental Criteria and Assessment Office, Cincinnati, OH.
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1tl ,2-TrIchloroethane
Sanders,  V.H.,   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-Tr1chloroethane.
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.   Integrated Risk  Information  System (IRIS):   Reference Dose
(RfD)   for  oral   exposure  for   1,1,2-trlchloroethane.    Online.   (Revised
verification  date  05/26/88.)   Office  of Health and  Environmental Assessment,
Environmental Criteria and Assessment Office, Cincinnati,  OH.
White,  K.L.  Jr.,  V.H.  Sanders,  V.W.  Barnes,  G.M.  Shopp  and
1985.   Toxicology   of   1,1,2   trlchloroethane   In  the  mouse.
Toxlcol.  8(5): 333-355.
                            A.E. Munson.
                              Drug  Chem
Trlchlorofluoromethane
Jenkins.  L.J., R.A.  Jones,  R.A.  Coon and  J.  Slegal.  1970.   Repeated  and
continuous   exposures  of   laboratory  animals   to   trlchlorofluoromethane.
Toxlcol. Appl. Pharmacol.  16: 133-142.
NCI  (National  Cancer Institute).   1978.   Bloassay
for  Possible Carclnogenldty.   NCI Cardnogenesls
(Also publ as DHEW  (NIH) 78-1356)
               of  Trlchlorofluoromethane
               Tech.  Rep.  Ser. No.  106.
 U.S.  EPA.   1985.  Integrated Risk  Information  System (IRIS):  Reference Dose
 {RfD)  for  oral  exposure  for  trlchlorofluoromethane.   Online.   (Verification
 date  05/31/85).   Office of  Health  and  Environmental  Assessment,  Environ-
 mental Criteria  and Assessment Office, Cincinnati, OH.

 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.

 2.4.4'-Tr1chloro-2'-hydroxydlphenyl 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-Trlchlorophenol
 McColllster,  D.D.,  D.T.  Lockwood and V.K. Rowe.  1961.  Toxlcologlc Informa-
 tion  on 2,4,5-trlchlorophenol.   Toxlcol.  Appl.  Pharmacol.  3: 63-70.

 U.S.   EPA.    1984.   Health  Effects  Assessment   for  2,4,5-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.
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U.S.  EPA.   1985.   Integrated Risk  Information  System  (IRIS):  Reference  Dose
(RfO)  for  Oral Exposure  for 2,4.5-Trlchlorophenol.   Online.   (Verification
date  05/20/85.)   Office  of  Health and  Environmental Assessment,  Environ-
mental Criteria and Assessment Office, Cincinnati, OH.
U.S.  EPA.   1987.   Health and Environmental  Effects  Document  for
Phenols.   Prepared by  the  Office  of  Health  and  Environmental
Environmental Criteria  and Assessment Office, Cincinnati, OH  for
of Solid Waste and Emergency Response, Washington, DC.
                              Chlorinated
                              Assessment,
                               the Office
Trichlorophenol. 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.

1.1.1- and 1,2.2-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-Trichloropropane
U.S.  EPA.   1987a.   Health and Environmental Effects  Document  for  Trichloro-
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.    1987b.   Integrated  Risk  Information  System  (IRIS):   Reference
Dose  (RfD)  for oral  exposure for  1,1,2-trichloropropane.  Online.   (Verifi-
cation  date  9/17/87.)   Office  of  Health  and  Environmental  Assessment,
Environmental Criteria and Assessment  Office, Cincinnati, OH.

VUlaneuve,  D.C.,  I.  Chu,  V.E. Secours,  M.G.   Cotie,  G.L.   Plaa  and  V.E.
Vain.  1985.   Results  of a 90-day  toxldty study on  1,2,3-  and  1,1,2-trl-
chloropropane administered via the drinking water.   Sci.  Total Environ.   47:
421-426.
1,2.3-Trlchloropropane
NTP  (National  Toxicology  Program).   1983a,
gavage  study  of  1,2,3-trlchloropropane  in
Hazelton Laboratories.
           Final  report 120-day  toxldty
        Fischer  344 rats.   Performed  by
U.S. EPA.   1986.   Integrated Risk Information  System  (IRIS):
(RfD) for  oral  exposure for  1,1,3-trlchloropropane.   Online.
date 9/02/86.)  Office  of  Health  and  Environmental  Assessment
Criteria and Assessment Office, Cincinnati, OH.
                           Reference  Dose
                            (Verification
                          ,  Environmental
U.S. EPA.   1987.   Health  and  Environmental  Effects Document  for  Irlchloro-
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.
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1,2.3-Tr1ch1oropropene
McKenna,  H.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.

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-Trlchlorotoluene
Chu,  I.,  S.Y.  Shen,  D.C. Vllleneuve,  V.E.  Secours  and V.E. Valli.   1984.
Toxlclty  of  trlchlorotoluene  Isomers: A  28-day  feeding study In  the  rat 3.
Environ.  Sc1.  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.

tt.2.6-Tr1ch1orotoluene
Chu,  I., S.Y.  Shen,  D.C.  Vllleneuve, V.E.  Secours  and V.E. Valll.   1984.
Toxlclty  of trlchlorotoluene   Isomers: A  28-day  feeding study 1n  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.
1.1.2-Tr1chloro-1.2.2-tr1fluoroethane
Imbus,  H.R.  and C.  Adkins.   1972.  Physical examination  of  workers
to trlchlorotrlfluoroethane.  Arch. Environ. Health.  24: 257-261.
                                  exposed
U.S.  EPA.   1983.  Health  Assessment  Document for 1,1,2-Tr1chloro-l,2,2-tr1-
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.   1985.  Integrated Risk  Information System (IRIS):  Reference Dose
(RfD)  for  Oral  Exposure  for  1,l,2-Tr1chloro-l,2,2-trlfluoroethane.  Online.
(Verification  date  07/08/85).   Office of  Health and Environmental  Assess-
ment, Environmental  Criteria and Assessment Office,  Cincinnati, OH.
Trlfluralln
Hoechst   Aktlengesellschaft.    1984.
unpublished study.  HR1D 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.
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U.S. EPA.  1989.   Integrated  Risk  Information  System  (IRIS).   Reference  Dose
(RfD)  for  Oral  Exposure  for  TMfluralin.   Online.    (Verification   date
04/20/89.)   Office  of  Health  and  Environmental  Assessment,  trwironmental
Criteria and Assessment Office, Cincinnati, OH.

Trlmethylbenzenes
U.S. EPA.  1987.   Health  Effects  Assessment for Trimethylbenzenes.   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-Tri nitrobenzene
Cody, I.E.,  S. WHherup,  L.  Hastings,  K.   Stemmer  and  R.T.  Chustion.   1981.
1 ,3-D1n1trobenzene:  Toxic  effects  in vitro.   3.  Toxicol.  Environ.  Health.
7:  829-847.

U.S. EPA.   1988.   Integrated Risk Information System (IRIS).  Reference Dose
 (RfO)  for Oral  Exposure  for  1 ,3,5-Trlnitrobenzene.   Online.   (Verification
date 05/26/88.)   Office  of  Health  and  Environmental  Assessment,  Environ-
mental  Criteria and  Assessment Office, Cincinnati, OH.

U S. EPA.  1989.   Health and Environmental  Effects  Document  for 1,3,5-Trl-
nitrobenzene.   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.

Tr1n1tropheno1s                                                 r    _ t  ,.
ITs  EPA    T984.   Health and Environmental  Effects  Profile  for Trinitro-
 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.


 Schroeder. 3. A..  M.  MHchener  and  A. P.   Nason.   1970.   Zirconium,  niobium,
 antlura. antimony,  vanadium and  lead  In  rats:  Life  term studTes.  3.  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
 CrHerU and  Assessment  Office,  Cincinnati,  OH  for  the  Office  of  Emergency
 and Remedial  Response, Washington, DC.  ECAO-CIN-H108.


                          Wagner,  3.T.  Hountaln  et  al.   1953.   Unpublished
                                ,    ..
           Div  Occup  Health. Cincinnati, OH.  (Cited in Stoklnger,  1981)

 U S   EPA    1986   Integrated Risk  Information System  (IRIS):  Reference  Dose
 (R?0) for oral  exposure9 for  vanadium pentoxide.   Online.   (Verification  date
 02/26/86 )   Office  of   Health  and  Environmental  Assessment,  Environmental
 Criteria and Assessment  Office, Cincinnati, OH.

 u s   EPA    1987     Health  Effects  Assessment  for  Vanadium  and  Compounds.
 Preoared I bv  the Office  of Health and Environmental Assessment, Environmental
 CrlteMa and Assessment  Office,  Cincinnati,  OH  for the  Office  of  Emergency
 and  Remedial Response, Washington,  DC.


                                      n 70                             01/11/90
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Vanadyl sulfate
Schroeder,  3.A.,  M.  Kitchener  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.

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.  1986.   Integrated Risk Information  System (IRIS).  Reference Dose
(RfD)   for   Oral   Exposure   for   Vernolate.    Online.    (Verification   date
09/29/86.)   Office  of  Health  and  Environmental   Assessment,  Environmental
Criteria  and Assessment Office, Cincinnati. OH.

4-V1nyl-1-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  Carclnogenesls  of Xylenes  (Mixed)  (60.2%  m-Xylene,  13.6%
p-Xylene, 17.0% Ethylbenzene and 9.IX 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.
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o-Xylene
NTP  (National   Toxicology  Program).   1986.   NTP  Technical   Report  on  the
Toxicology  and  Carcinogenesls  of  Xylenes  (mixed)  (60.2%  m-xylene,  13.6%
p-xylene,  17.0%  ethylbenzene  and  9.1%  o-xylene)  (CAS  No.  1330-20-7)  1n
F344/N  rats  and  B6C3F1  mice  (gavage  studies).   U.S.  OHHS.  PHS, NIH,  NTP,
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.  Xenoblotics,  Proc.  Int.
Conf.  p. 293-300.

Ungvary, G., 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
standard  for  the  Industrial  worker
XY-77-3.  NTIS PB82-152844.
al.  1981.   Development  of  a  biologic
by  breath  analysis.   NIOSH-MCOW-ENUM-
 U.S.  EPA.   1987.   Updated  Health Effects
 by  the Office of Health and Environmental
 and  Assessment  Office,  Cincinnati,   OH
 Remedial Response,  Washington,  DC.
     Assessment for Xylenes.   Prepared
     Assessment,  Environmental  Criteria
    for  the  Office  of  Emergency  and
 Xylenes. mixed                                                 t  ,    .   .
 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  *  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  Carcinogenesls  of  Xylenes  (Mixed)  (60.2%  m-Xylene, 13.6*
 P-Xylene?yi7.0% 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.
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NTP (National Toxicology Program).  1987a,b.
U.S. EPA.   1987.   Integrated Risk Information System  (IRIS):  Reference Dose
(RfD) for oral exposure  for  xylenes  (mixed  isomers).   Online.   (Verification
date  03/19/87.)    Office  of  Health  and  Environmental Assessment,  Environ-
mental Criteria and Assessment Office, Cincinnati, OH.

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.

Zinc
Pories, W.3.,  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.

Prasad,  A.S.,  E.B. Schoomaker,  J.  Ortega et al.   1975.   Zinc deficiency 1n
sickle  cell disease.  Clin.  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.

Zlneb
Blackwell-Smith,   R.J.,  Jr.   J.K.  Finnegan,   P.S.  Larson,   et  al.   1953.
Toxicologic  studies  on  zinc  and  dlsodlumethylenebisdithlocarbamates.   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.   1986.   Integrated Risk Information System  (IRIS).  Reference Dose
(RfD)  for  Oral Exposure  for  Zlneb.   Online.  (Verification  date 02/05/86.)
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.  MR10 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.   1988.   Integrated  Risk  Information System  (IRIS).   Carcinogen-
Iclty  Assessment  for Lifetime  Exposure  to Acephate.   Online.   {Verification
date  03/23/88.)   Office  of  Health  and  Environmental  Assessment,  Environ-
mental Criteria and Assessment Office, Cincinnati, OH.

Acrolein
U.S.  EPA.   1987a.   Health Effects Assessment  for  Acrolein.   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.   1987b.   Integrated  Risk Information System (IRIS).   Risk Estimate
for  Carc1nogen1c1ty  for  Acrolein.   Online.    (Verification  date  12/02/87).
Office  of  Health  and  Environmental  Assessment,   Environmental   Criteria  and
Assessment Office, Cincinnati,  OH.

Acrylamide
Johnson, K.,  S. Gorzlnski, K.M.  Bodner,  et  al.  1986.  Chronic toxiclty  and
oncogenidty   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.   1988.   Integrated  Risk  Information  System  (IRIS).  Carcinogen-
Iclty Assessment  for  Lifetime  Exposure  to  Acrylamlde.   Online.   (Verifica-
tion  date   03/23/88.)   Office  of  Health   and  Environmental  Assessment,
Environmental  Criteria  and Assessment Office,  Cincinnati,  OH.


Bio/dynamics,  Inc.   1980a.   A 24-month  oral  toxicity/carclnogenlcity 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  tox1c1ty/carc1nogen1cHy study
of  acrylonltrlle administered  in  drinking water  to Fischer 344 rats.  Final
Report   Vol.  1-4.   Prepared  by  B1o/dynamics, 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)
 0626h
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O'Berg, M.   1980.   Epldemlologlc  study  of workers exposed  to  acrylonHrlle.
J. Occup.  Hed.   22:  245-252.

Quast, J.F., C.E. Wade,  C.G. Humlston  et  al.   1980.  A 2-year  toxlclty  and
oncogenlclty study  with  acrylonltrlle  Incorporated 1n 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  AcrylonltrHe.   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.  1987a.   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.   1987b.   Integrated Risk  Information System (IRIS).   Risk  Estimate
for   Carclnogenlclty   for   Acrylonltrlle.    Online.    (Verification   date
02/11/87).   Office of Health  and  Environmental  Assessment,  Environmental
Criteria and Assessment Office,  Cincinnati, OH.

AldMn
Davis,  K.3.   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.   FHzhugh.   1962.   Tumorlgenlc  potential of aldrln  and
dleldrln for mice.  Toxlcol. Appl. Pharmacol.  4: 187-189.

Epstein, S.S.  1975.   The  cardnogenlclty of dleldrln.  Part  I.  Sd.  Total
Environ.  4: 1-52.

NCI  (National  Cancer  Institute).   1977.  Bloassays  of  aldrln  and  dleldrln
for  possible cardnogenlclty.  NCI  Carclnogenesls  Tech.  Rep.  Ser.  No.  21.
(Also published as  NTIS PB-275-666)

U.S.   EPA.    1986.   Cardnogenlclty Assessment   of  Aldrln   and  Dleldrln.
December 1986  Review  Draft.   Office of  Health and Environmental Assessment,
Carcinogen Assessment Group, Washington, DC.

U.S.  EPA.   1987a.  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.  1987b.   Integrated Risk  Information System (IRIS).   Risk  Estimate
for  Carclnogenlclty  for aldrln.    Online.    (Verification  date  03/22/87).
Office  of  Health and  Environmental Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

Aniline
CUT  (Chemical  Industry  Institute  of  Toxicology).   1982.   104-Week  chronic
toxlclty study In rats:  Aniline hydrochlorlde.  Final Report.


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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.   1987.   Integrated  Risk  Information  System  (IRIS).   Carclnogen-
Iclty  Assessment  for  Lifetime  Exposure  to  Aniline.   Online.   (Verification
date  06/03/87.)    Office  of  Health and  Environmental  Assessment,  Environ-
mental Criteria and Assessment Office, Cincinnati, OH.

Aramlte
Oser,  B.L.  and  M.  Oser.   1962.   2-(p-tert-Butylphenoxy)1sopropyl  2-chloro-
ethyl  sulfHe  (aramite).   II.  CardnogenlcHy.   Toxlcol. Appl.  Pharmacol.
4: 70-88.

Popper, H.,  S.S.  Steinberg,  B.L. Oser and M.  Oser.   1960.  The carcinogenic
effect of aramHe 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 epidemlologic  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.

Enterline,  P.E.  and  G.M.  Marsh.   1982.  Cancer  among  workers exposed  to
arsenic and  other  substances  In  a  copper  smelter.   Am.  J.  Epldemiol.   116:
895-911.

H1gg1ns,  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 rulemaking (Exhibit 203-5).

Lee-Feldste1n,  A.   1983.   Arsenic  and  respiratory cancer 1n  man:  Follow-up
of an  occupational study.  In.:  Arsenic:  Industrial,  Blomedical,  and  Environ-
mental  Perspectives,   W.  Lederer   and  R.   Fensterheim,   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.


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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.  1988.   Integrated  Risk Information System  (IRIS).   Risk estimate
for  carclnogenlclty  for  arsenic.    Online.   (Revised;   verification  date
01/13/88.)   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)  1n  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.   1987.   Integrated  Risk  Information  System (IRIS).   Cardnogen-
1c1ty  Assessment  for  Lifetime  Exposure  to Asbestos.   Online.   (Verification
date  12/02/87).    Office of  Health and  Environmental Assessment,  Environ-
mental  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.

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.   1988.   Integrated  Risk Information  System (IRIS).   Carclnogen-
lclty  Assessment  for   Lifetime  Exposure  to  Azobenzene.   Online.   (Verifica-
tion  date   02/03/88.)   Office  of Health  and   Environmental   Assessment,
Environmental Criteria and Assessment Office, Cincinnati,  OH.

Benzene
Ott, M.G., O.C.  Townsend.  W.A. Flshbeck and R.A.  Langner.   1978.  Mortality
among  workers occupatlonally  exposed   to benzene.  Arch.   Environ.  Health.
33: 3-10.

Rlnsky,  R.A.,  R.3.   Young  and  A.B.  Smith.   1981.   Leukemia  1n  benzene
workers.  Am. J.  Ind.  Med.   2:  217-245.
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U.S.  EPA.   1985.   Interim Quantitative  Cancer  Unit  Risk  Estimates Due  to
Inhalation  of  Benzene.   Prepared  by  the  Office of  Health  and Fnvlronmental
Assessment,  Carcinogen  Assessment  Group,  Washington,  DC  for the  Office  of
A1r Quality Planning and Standards, Washington, DC.

U.S. EPA.   1987a.   Memorandum  from 3.  Orme HE8,  CSD/ODW to C. Vogt, Criteria
and Standards Division, ODW, June, 1987.

U.S. EPA.   1987b.   Integrated  Risk Information System (IRIS).  Risk estimate
for  carclnogenlclty for  benzene.   Online.    (Verification  date  10/09/87.)
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.   1986a.  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.

U.S. EPA.   1986b.   Integrated  Risk Information System (IRIS).  Risk estimate
for carclnogenlclty  for  benzidine.  Online.   (Verification  date  12/17/86.)
Office  of   Health  and  Environmental  Assessment,  Environmental Criteria  and
Assessment  Office, Cincinnati, OH.

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.

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)pyrene
Neal, 0. and R.H.  Rlgdon.   1967.   Gastric  tumors  in mice fed benzo[a]pyrene:
A quantitative study.  Tex. Rep.  Biol. Med.  25: 553.

Thyssen, J., J.  Althoff, G. Kimmerle and  U.  Mohr.   1981.   Inhalation studies
with  benzo[a]pyrene  In  Syrian   golden  hamsters.    J.  Natl.  Cancer  Inst.
66(3): 575-577.
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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.   1987.   Integrated  Risk Information System  (IRIS).   Risk  estimate
for  carclnogenlclty   for  benzo[a]pyrene.    Online.    {Verification   date
01/07/87.)   Office of  Health  and  Environmental  Assessment,  Environmental
Criteria and Assessment Office, Cincinnati, OH.

Benzo(k)f1uoranthene
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.

Benzotrlchlorlde
Fukuda, K., H.  HetsushHa and  K.  Takemoto.   1978.   Carclnogenlclty  of benzo-
trlchloMde  by  the oral route  of administration (J-4774).  ln_:  Proc.  52nd
Ann.  Meet. Japanese  Industrial  Health Assoc.   TSCA  8E Submission  Document
No. 88-8000360, Flche 1204867.  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.

Yoshimura.   H.,  H.  Katayama,   K.   Takomoto  and  S.  Matsushita.    1979.
Experimental lung  tumors  Induced by  exposure to  benzotrlchlorlde.   [2] Proc.
of Japan  Assoc. of Ind. Health.  TSCA  8e  Submission Document No. 88-8000360,
Flche I 204867.  p. 332-333.

Benzyl Chloride
Lljinski,  W.   1986.  Chronic  bloassay of  benzyl  chloride  in  F344  rats  and
(C57BL/6J  x BALB/cJF! 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.   1989.   Integrated  Risk  Information  System  (IRIS).   Carclnogen-
lclty  Assessment   for   Lifetime  Exposure   to   Benzyl   chloride.    Online.
(Verification date 03/01/89.)   Office  of  Health  and  Environmental  Assess-
ment, Environmental Criteria and Assessment Office,  Cincinnati,  OH.
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Beryllium
Schroeder,  H.A.  and  M.   MHchener.    1975a.    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.   1988.   Integrated Risk Information System  (IRIS).   Risk  estimate
for  cardnogenlclty  for  beryllium.   Online.   (Verification  date  05/04/88.)
Office  of Health  and  Environmental   Assessment, Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

Wagoner,  O.K.,   P.P.  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.

B1s  (2-chloroethyl)ether
Innes,  J.R.M.,  B.M.  Ulland,  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.   1980a.   Ambient  Water 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 Water  Regulations and  Standards, Washington,  DC.   EPA-440/5-80-030.   NTIS
PB 81-117418.

U.S. EPA.   1986.   Integrated Risk Information System  (IRIS).   Risk  estimate
for  cardnogenlclty  for  b1s(chloroethyl)ether.   Online.   (Verification  date
07/23/86.)   Office  of  Health  and Environmental Assessment,  Environmental
Criteria and Assessment Office, Cincinnati, OH.

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, Washington, DC.

B1s(choromethy1)ether
Kuschner, M.,  S.  Laskln,  R.T.  Drew,  et  al.  1975.   Inhalation  cardnogen-
lclty  of alpha  halo  ethers:  III. Lifetime and  limited  period  Inhalation
studies  with  b1s(chloromethyl)  ether  at   0.1 ppm.   Arch. Environ.  Health.
30(2): 73-77.
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U.S. EPA.   1988.   Integrated  Risk Information System  (IRIS).   Risk  estimate
for carclnogeniclty for b1s(chloromethyl)ether.   Online.   (Verification date
05/04/88.)   Office of  Health  and  Environmental  Assessment,  Environmental
Criteria and Assessment Office,  Cincinnati,  OH.

B1s(2-chloro-l-methylethyl)ether
NTP  (National  Toxicology  Program).  1982.   Carcinogenic  Bloassay of  B1s(2-
Chloro-1-Hethylethyl)   Ether   (=70%)  Containing   2-Chloro-l-Ethylethyl-(2-
Chloropropyl)  Ether  (=30%)  In  B6C3F1  Mice  (Gavage Study).   NCI  Carcinogen.
Tech. Rep. Ser. No. 239.   105 p.  [Also pub!.  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 Waste
and Emergency Response, Washington, DC.

B1s(2-ethylhexy1) phthalate
NTP  (National  Toxicology  Program).   1982a.   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  Waste  and  Emergency  Response,
Washington,  DC.

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.   1988.   Integrated Risk  Information System  (IRIS).   Risk  estimate
for  carclnogeniclty   for   b1s(2-ethylhexyl)phthalate.    Online.    (Revised;
verification date  08/15/88.)  Office of  Health and Environmental  Assessment,
Environmental Criteria and Assessment Office,  Cincinnati,  OH.

Bromodlchloromethane
NTP  (National  Toxicology  Program).   1986a.   NTP  technical   report on  the
toxicology  and  cardnogenesls   studies  of  bromodlchloromethane  (CAS  No.
75-27-4)  1n  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  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.   ECAO-CIN-H083.

Bromoethene
Benya,  T.J., W.M.  Basey,  M.A.  Dorato  and  P.E.  Berteau.   1982.  Inhalation
cardnogenldty  bloassay   of   vinyl  bromide   In  rats.    Toxlcol.   Appl.
Pharmacol.  64:367-379.
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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  carcinogenesis  studies of trihalomethane (brorooform)  (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.

1.3-Butadiene
Hazleton  Laboratories.   1981.   The Toxlcity and Carcinogenicity 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)

U.S.  EPA.   1985.   Mutagenlclty and  Carcinogenicity  Assessment of 1,3-Buta-
dlene.   Office of Health  and  Environmental Assessment, Washington,  DC.  EPA
600/8-85-004F.  NTIS PB86-1 25507.

U S  EPA    1987.   Integrated  Risk  Information  System (IRIS).   Carcinogen-
 icity Assessment  for Lifetime  Exposure to  1 ,3-Butadiene.   Online.   (Verifi-
cation  date   01/07/87).    Office   of  Health  and  Environmental   Assessment,
 Environmental Criteria  and Assessment Office, Cincinnati,  OH.

 U S   EPA    1989     Health  and  Environmental  Effects  Document for  1,3-Buta-
 diene.   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.
       EPAZV  l°987a    Health  Effects  Assessment  for  Selected Phthalic  Acid
 Esters   'prepared   by  the  Office  of Health  and  Environmental  Assessment,
 Environment Criteria  and Assessment Office. Cincinnati, OH  for  the Office
 of Emergency and Remedial Response, Washington, DC.

 U S   EPA    1987b    Integrated  Risk Information System (IRIS).  Risk estimate
 for'ca rcinoge "city foAutyl  benzyl  phthalate.   Online.  (Verl  lea  or i  date
 08/26/88.)   Office  of   Health  and  Environmental   Assessment,  Environmental
 Criteria and Assessment  Office, Cincinnati, OH.
           .. l.H.  Schnorr,  A.B.  Smith and  W.E. Halperin.   1985.  Mortality
 among  a  cohort  of  U.S.  cadmium production workers:  An update.   3.  Natl.
 Cancer  Inst.  74(2):  325-333.

 U  S   EPA   1984    Health Effects  Assessment  for Cadmium.   Prepared  by the
 Qmce  of  Health  and  Environmental  Assessment, Environmental  Criteria and
 Assessment  Office, Cincinnati,  OH  for the Office of  Emergency and Remedial
 Response, Washington,  DC.


                                      n  qi                            12/29/89
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U.S.   EPA.   1985.   Updated mutagenlclty  and  CarclnogenlcHy  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.   1986.   Integrated  Risk  Information System  (IRIS).   Risk  estimate
for  carclnogenlclty  for  cadmium.   Online.   (Verification date  11/12/86.)
Office  of  Health  and  Environmental  Assessment,  Environmental Criteria  and
Assessment Office,  Cincinnati, OH.

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.

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.

Carbazole
Tsuda,  H.,  A. Hazlwara,  M.  Shlbata,  H. Ohslma and N.  Ito.   1982.   Carcino-
genic  effect  of carbazole In the  liver of  (C57BL/6N  x  C3H/HeN)F-j  mice.   0.
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  1n hamsters.   3.  Natl. Cancer
Inst.   26:  855-863.

Edwards,  0.,  W.E.  Heston and H.A.  Dalton.   1942.  Induction  of  the carbon
tetrachlorlde  hepatoma 1n 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  letrachlorlde.
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.   1986.  Integrated Risk Information  System  (IRIS).   Risk  estimate
for  carclnogenlclty for  carbon  tetrachlorlde.   Online.   (Verification date
12/04/86.)   Office  of  Health  and  Environmental  Assessment, Environmental
Criteria and  Assessment  Office,  Cincinnati,  OH.


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Chloranyl
BRL  (Blonetlcs  Research  Labs,  Inc.)-   1968.   Evaluation  of  carcinogenic,
teratogenlc and  mutagenic 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.

Chlordane
IRDC  (International  Research  and  Development  Corporation).    1973.   Unpub-
lished report to  Velsicol Chemical  Corporation,  Eighteen Month Oral  Carcino-
genic Study in Mice,  December 14, 1973.

NCI  (National  Cancer Institute).  1977.  Bloassay of  Chlordane for  Possible
Carclnogenlcity.   NCI  Carcinogenesis Tech.   Rep.  Ser.  No. 8.    Also  publ.  as
DHEW  Publ. No. (NIH)  77-808.

U.S.  EPA.   1986.  Carclnogenlcity Assessment  of Chlordane  and Heptachlor/
Heptachlor  Epoxide.    Prepared  by  the  Office  of Health and Environmental
Assessment,  Carcinogen  Assessment Group, Washington,  DC.  EPA-600/6-87-004.
Final Report.

U.S.  EPA.   1987.  Integrated  Risk  Information  System  (IRIS).  Risk  estimate
for  carclnogenicity  for  Chlordane.   Online.   (Verification  date 04/01/87.)
Office  of Health  and   Environmental  Assessment,   Environmental  Criteria  and
Assessment Office, Cincinnati,  OH.

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.

4-Chloroannine
NCI   (National  Cancer   Institute).   1979.    Bioassay  of  p-chloroan1Hne  for
possible carclnogenicity.  NCI  Carcinogenesis Tech Rep.  Ser. No.  189.  NTIS
PB295896.

U  S  EPA.   1987.   Health and  Environmental  Effects  Document  for  Chloro-
anllines.   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.

Chlorodibromomethane                                                       ,
NTP  (National  Toxicology  Program).   1985.   Toxicology  and  "rcinogenesls
studies   of  Chlorodibromomethane  (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.
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Chloroform
Jorgenson, T.A.,  E.F.  Melerhenry,  C.3.  Rushbrook et al.   1985.   Cardnogen-
IcHy 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).
of Chloroform.   NTIS PB264-018.
                 1976.   Report  on Cardnogenesls  Bloassay
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.

U.S.  EPA.   1987.   Integrated Risk Information  System  (IRIS).   Risk  estimate
for  carclnogenldty  for  chloroform.   Online.   (Verification  date  08/26/87).
Office  of  Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office, Cincinnati, OH.

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.

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
Carcinogenic  Risk
NTIS PB85-111623.
Institute  for
Assessment  for
Occupational
Occupational
 Safety  and
Exposure to
 Health).   1984.
Monohalomethanes.
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-methylanl1Ine
U.S. EPA.   1986.   Health  and  Environmental  Effects Profile for  4-Chloro-2-
methylanlllne  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  carclnogenldty.   J. Environ.  Pathol.  Toxlcol.   2:325-356.
0626h
                 D-94
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4-Chloro-2-methylan111ne hydrochlorIde
U.S. EPA.   1986.   Health  and  Environmental  Effects Profile  for  4-Chloro-2-
methylanlllne  and  4-Chloro-2-methylaniline  hydrochloride.   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
toxlcity 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.

U.S.  EPA.   1988.   Integrated  Risk  Information System (IRIS).  Risk estimate
for  carcinogenldty for  chloromethyl methyl  ether.   Online.  (Verification
date  05/04/88.)   Office  of  Health  and Environmental  Assessment,  Environ-
mental  Criteria and Assessment  Office, Cincinnati, OH.

o-Chloronltrobenzene
0~sEPA1985^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
toxlclty or  carcinogenldty.   J.  Environ.  Pathol.  Toxlcol.   2:325-356.

p-Chloronltrobenzene                                                    „»+„„
US—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
 toxlclty or  carcinogenldty.   3. Environ. Pathol.  Toxlcol.   2:325-356.


 £c?7LaUonna1  Cancer  Institute).   1978.   Bioassay  of  chlorothalonll  for
 possible  carcinogenldty.    DHEW   Publ.   NIH-78-841,   NCI-CG-TR-41.    Niib
 PB-286369.

              1984.   Health  and  Environmental Effects  Profile  for  Chlor-
 of Solid Waste, Washington. DC
           S^F    1975.   international  Conference  on  Heavy  Metals  in  the
 Environment; Toronto, Canada, Oct. 27-31.   (Cited  In  U.S. EPA, 1984)


                                        c                            12/29/89
                                       ~
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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   carc1nogen1c1ty   for    chromlum(VI).    Online.    (Verification   date
06/26/86.)    Office   of  Health  and  Environmental  Assessment,  Environmental
Criteria and Assessment Office, Cincinnati,  OH.

Coal   tars
Mazumdar, S.,  C.  Redmond,  W.  SollecHo and  N. Sussman.   1975.   An epldemlo-
loglcal  study  of  exposure  to   coal-tar-pitch   volatHes  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.  HSM-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.   1987.  Integrated  Risk  Information System  (IRIS).   Risk estimate
for  carclnogenlclty for  creosote.  Online.  (Verification  date 05/13/87.)
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.    1986a.    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.   19865.   Integrated Risk Information  System (IRIS).   Risk estimate
for  carclnogenlclty  for  DDT.   Online.  (Verification date 11/12/86.)  Office
of Health  and  Environmental  Assessment, Environmental  Criteria and Assess-
ment  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.
 0626h
D-96
                                                                     12/29/89

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U.S. EPA.   1987.   Health and Environmental  Effects  Profile  for  Decabromodi-
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.

Dlallate
BRL  (Blonetlcs  Research  Labs,  Inc.)   1968.   Evaluation  of  carcinogenic,
teratogenic, 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,  3.R.M.,  B.M.  Ulland,  M.G. Valerio, et  al.   1969.   Bioassay  of pesti-
cides and  industrial  chemicals  for  tumorlgenlclty  1n 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.

Dlbromochloromethane
NTP  (National   Toxicology   Program).   1985.   Toxicology  and  carcinogenesls
studies   of  chlorodlbromomethane  In  F344/N  rats  and  B6C3F1  mice.   NTP
Technical Report Series  No.  282.  NTIS/PB86-166675.

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.  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.

l.2-D1bromoethane
NCI  (National  Cancer  Institute).   1978.  Bioassay  of 1,2-dibromoethane  for
possible  carclnogenicity.    NCI  Carcinogenesls  Technical  Report  Series  No.
86.  PB-288-428  [Also  published as  CHHA (NIH) 78-1336].  p. 64.

NTP  (National   Toxicology  Program).   1982.   Carcinogenesls   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  1,2-01bromo-
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    1987a.    Health  Effects   Assessment   for  Ethylene  D1brom1de.
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.   1987b.   Integrated  Risk  Information System  (IRIS).   Carcinogen-
idty  Assessment  for  Lifetime   Exposure   to   1,2-D1bromoethane.    Online.
(Verification date  05/13/87.)  Office  of Health  and Environmental  Assess-
ment, Environmental  Criteria and Assessment  Office, Cincinnati,  OH.

1,4-Dlchlorobenzene
NTP  (National Toxicology  Program).   1986.   Toxicology  and  Carclnogenesls
Studies  of  1,4-Dlchlorobenzene  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'-D1chlorobenz1d1ne
Stula, E.F., H. Sherman, 3.A.  Zapp,  et  al.   1975.   Experimental  neoplasla In
rats  from  oral  administration  of  3,3'-d1chlorobenz1d1ne,  4,4'-methylene-
b1s(2-chloroan1!1ne)  and   4,4'-methylene-bls  (2-methylan1l1ne).   Toxlcol.
Appl. Pharmacol.  31: 159-175.

U.S.  EPA.   1988.   Health  and Environmental Effects Document   for  3,3'-01-
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.

1,4-01ch1oro-2-butene
E.I.  Dupont  de  Nemours  and  Co.  1986.   Long-term  Inhalation study  with
l,4-dlchlorobutene-2 (DCB)  1n  rats.  Final report OTS 8(e)  F1che 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.

U-Dlchloroethane
NCI  (National  Cancer  Institute).   1978.  Bloassay  of I,l-d1chloroethane  for
possible  carclnogenlclty.   NCI Carclnogenesls  Tech.  Rep.  Ser.   No.  66,  DHEW
Publ. No. (NIH) 78-1316.

U.S.   EPA.    1984.    Health   Effects   Assessment  for   1 ,l-D1chloroethane.
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  Dichloro-
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-Dlchloroethane
NCI  (National Cancer  Institute).   1978.  Bloassay  of 1,2-dichloroethane  for
possible  carclnogenlclty.    NCI Carclnogenesls  Tech.  Rep.  Ser.  No.  55,  DHEW
Publ. No. (NIH)  78-1361.
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U.S. EPA.   1985.
600/8-84-006F.
Health  Assessment  Document  for  1,2-D1chlcroethane.   EPA
U.S. EPA.   1986.   Integrated Risk Information  System  (IRIS).   Risk  estimate
for  carclnogenldty  for  1,2-dlchloroethane.   Online.   (Verification  date
12/04/86.)   Office  of   Health  and  Environmental  Assessment,  Environmental
Criteria and Assessment Office, Cincinnati, OH.
1,1-Dichloroethylene
Maltoni, C.,  G.  Lefemlne,  P. Chleco et  al.   1985.
vlnylldene chloride  carclnogenesls.   In: Archives
Carclnogenesls, Vol. 3, C. Maltoni  and  M.  Mehlman,
Publishers, Princeton,  NJ.
                                 Experimental research on
                                of  Research on Industrial
                                Ed.  Princeton Scientific
NTP  (National   Toxicology   Program).    1982.    Carclnogenesls
vlnylldene chloride  (CAS No. 75-35-4)  in  F344 rats and  B6C3F1
study).  NTP Tech. Rep. Ser. No. 228, DHHS No.  NIH 82-1784.
                                             bloassay  of
                                             mice (gavage
U.S.  EPA.   1985.   Health  Assessment  Document  for  Vlnylidene  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.   1987.   Integrated Risk  Information System  (IRIS).   Risk  estimate
for  carclnogenldty for  1 ,l-d1chloroethylene.   Online.   (Verification  date
01/07/87.)   Office  of  Health  and  Environmental  Assessment,  Environmental
Criteria and Assessment Office, Cincinnati, OH.

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.

1,2-D1ch1oropropane
NTP  (National   Toxicology Program).   1986.   NTP  Technical  Report  on  the
Carclnogenesls  Studies  of 1,2-D1chloropropane  (Propylene  Dichloride).   (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-D1chloropropane.
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-Dichloropropene
Lomax,  L.G.,  W.T.  Stott,  K.A.  Johnson,  L.L.  Calhoun,  B.L.  Yano
Quast.   1989.   The  chronic toxicity  and  oncogenlcity of  Inhaled
grade  1,3-dichloropropene  in   rats  and  mice.   Fund. Appl.
418-431.
                                                 and J.F.
                                                 technical
                                            Toxlcol.   12:
NTP  (National  Toxicology  Program).
studies of  telone II in  F344/N  rats
Human Services, Technical Report Ser
                    1985.   Toxicology  and  carclnogenesls
                  and B6C3F1 mice.  U.S.  Dept. Health and
                   No.  269.
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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
l,3-D1chloropropene.    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.

Helerhenrey,  E.F., B.H.  Reuber, M.E. Gershwin  et al.   1983.  D1eldr1n1nduced
mallory  bodies  1n 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  Pub!.   No.  (NIH)
78-882.]

Tennekes,  H.A.,  A.S.  Wright,  K.M. D1x  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,
phenobarbHone,  beta-BHC   and  gamma-BHC.   Food  Cosmet.  Toxlcol.   11(3):
433-443.

U.S.  EPA.   1987a.  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.

U.S.  EPA.   1987b.  Integrated Risk Information  System (IRIS).  Risk estimate
for carclnogenlclty  for dleldrln.  Online.   (Verification date  03/05/87.)
Office   of Health and  Environmental  Assessment, Environmental  Criteria and
Assessment Office,  Cincinnati,  OH.

Walker,  A.I.T..  E.  Thorpe and D.E.  Stevenson.   1972.   The  toxicology of
dleldrln  (HEOD): I.  Long-term  oral  toxlclty studies  In  mice.   Food Cosmet.
Toxlcol.  11:  415-432.

 3.3'-D1methoxybenz1d1ne
OSHA/NIOSH (Occupational Safety and Health Administration/National  Institute
 for Occupational Safety and Health).  1980.  Health hazard,  alert benzldlne,
 o-tolldlne and o-d1an1s1d1ne based dyes.  DHHS  (NIOSH)  Publ.  No.  81-106.

 Sellakumar.   A.R.,  R.  Hontesano  and  A.  Safflotl.  1969.   Aromatic  amines
 carclnogenlclty In hamsters.   Proc.  Am.  Assoc.  Cancer  Res.   10:78.
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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-D1methylan1l1ne
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,  E.K.,  A.B.  Russfield,  F.  Homburger,  et  al.  1978.   Testing  of
twenty-one   environmental   aromatic   amines  or   derivatives  for   long-term
toxldty or carclnogenlclty.  J. Environ. Pathol. Toxlcol.  2:325-356.

2.4-D1methylan111ne hydrochlorlde
U.S. EPA.  1987.   Health  and  Environmental  Effects Profile for 2,4-Dlmethyl-
anlHne  and  2,4-D1methylan1l1ne  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
toxldty or carclnogenlclty.  J. Environ. Pathol. Toxlcol.  2:325-356.

3.3'-D1methylbenz1d1ne
Grlswold,  D.P.,  Jr.,  A.E.  Casey,   E.K.   Welsburger  and   J.H.  Welsburger.
1968.   The carclnogenlclty  of  multiple  Intragastrlc  doses of aromatic  and
heterocycllc nltro or amlno derivatives  In  young female Sprague-Dawley rats.
Cancer Res.  28(5):924-933.

U.S.  EPA.    1987.   Health  and  Environmental  Effects  Profile for  3,3'-01-
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-Dlmethylhydrazlne
Toth,  B.   1972.   Comparative  studies  with  hydrazlne  derivatives.  Carclno-
genlclty  of  I,l-d1methylhydraz1ne,  unsymmetMcal  (1,1-DMH)   1n  the  blood
vessels,  lung,  kidneys  and liver  of  Swiss  mice.   Proc. Am.  Assoc.  Cancer
Res.  13:34.

Toth,  B.   1973.   1,1-Dlmethylhydrazlne  (unsymmetrlcal)  carclnogenesis  1n
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.
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l.2-D1methv1hvdraz1ne
Toth,  B.  and  R.B.  Wilson.   1971.   Blood  vessel  tumorlgenesls  by  1,2-di-
methylhydrazlne dlhydrochlorlde (symmetrical).   Am.  3.  Pathol.   64:  585.

U.S. EPA.  1984.  Health and  Environmental  Effects  Profile  for  1,2-D1methyl-
hydrazine.  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.  1987.   Integrated Risk  Information  System  (IRIS).   Cardnogen-
IcHy   Assessment   for   Lifetime  Exposure  to  Dimethyl  sulfate.   Online.
(Verification  date 05/13/87.)   Office of  Health  and  Environmental  Assess-
ment,  Environmental Criteria  and  Assessment Office, Cincinnati,  OH.
 2.4-D1n1trotoluene
 Ellis,  H.V., S.H.  Hageusen,  3.R.  Jodgson et  al
 of Munition  Compounds.   Phase III.  Effects  of
 2,4-D1n1trotoluene.  NTIS AD-A077692.   281 p.
            .   1979.
            Lifetime
Mammalian
Exposure.
loxlclty
 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.

 2.6-D1n1troto1uene
 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.
 l.2-D1phenv1hvdraz1ne
 NCI  (National   Cancer  Institute).   1978.   Bloassay of
 possible carclnogenlclty.   NCI  Cardnogenesls  Tech.  Rep.
 Publ. No. (NIH) 78-1342.
                      hydrazobenzene  for
                      Ser. No. 92.   DHEW
 U.S. EPA.   1980.   Ambient Water Quality Criteria Document  for  1,2-01phenyl-
 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.   1986.   Integrated Risk Information System  (IRIS).   Risk  estimate
 for carclnogenlclty  for 1,2-dlphenylhydrazlne.  Online.   (Verification  date
 10/29/86.)   Office of  Health  and  Environmental  Assessment,  Environmental
 Criteria and Assessment Office, Cincinnati, OH.
 0626h
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U.S.  EPA.   1987.   Health  Effects  Assessment  for  1,2-D1phenylhydrazine.
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-
phenylhydrazine.  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.

Direct Black 38
NCI  (National  Cancer  Institute).   1978.   13-Week subchronic toxlclty  studies
of  direct  blue 6, direct  black 38, and direct  brown  95  dyes.   NCI  Carcino-
genesls. Tech. Rep. Ser. No. 108.   p. 127.

U.S.  EPA.   1987.   Health and Environmental Effects  Profile  for  Direct  Black
38.   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.

Direct Blue 6
NCI  (National  Cancer  Institute).   1978.   13-Week subchronic toxicity  studies
of  direct  blue 6, direct  black 38, and direct  brown  95  dyes.   NCI  Carcino-
genesis. Tech. Rep. Ser. No. 108.   p. 127.

U.S.  EPA.   1987.   Health  and  Environmental Effects Profile  for  Direct Blue
b.   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.

Direct Brown  95
NCI  (National  Cancer  Institute).   1978.   13-Week subchronic toxiclty 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, Environ-
mental  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 6B    Prepared  by  the Office of  Health  and  Environmental Assessment,
Environmental  Criteria and  Assessment  Office,  Cincinnati,  OH for  the  Office
of  Solid  Waste, Washington, DC.


              ..  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.
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U.S.  EPA.   1985.  Health  and Environmental  Effects  Profile  for  Epichloro-
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.   1986.    Integrated   Risk   Information  System  (IRIS).   Cardno-
geniclty  Assessment   for  Lifetime  Exposure  to  EpIchlorohydMn.   Online.
(Verification date  10/29/86).   Office  of Health  and Environmental  Assess-
ment, Environmental  Criteria and Assessment Office, Cincinnati, OH.

Ethyl acrylate
NCI  (National  Toxicology Program).  1986.   Carclnogenesis 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
Shellings, W.M., C.S. Weil and  R.R. Moronpot.   1981.   Final  Report,  Ethylene
Oxide,  Two  Year Inhalation  Study.   Submitted  to   the U.S.  Environmental
Protection Agency by Bushey Run Research Center,  Pittsburgh,  PA.   (Cited  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 60Q/8-84-Q09F.  NTIS PB86-102597.

Ethylene thiourea
U.S.  EPA.   1984.    Health  and  Environmental  Effects  Profile  for  Ethylene
Thiourea.   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:
feeding  study  of pholton  technical  (SX-946;   folpet)
mice.  Cited 1n U.S. EPA, 1987.
                   Lifetime  oncogeniclty
                   in  CD-I  (ICR  derived)
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.  1987.   Integrated  Risk Information System  (IRIS).   Cardnogen-
icity  Assessment for  Lifetime  Exposure  to  Folpet.   Online.   (Verification
date  10/07/87.)   Office  of Health  and  Environmental   Assessment,  Environ-
mental Criteria and Assessment  Office, Cincinnati, OH.

Formaldehyde
U.S.  EPA.   1988.  CRAVE  verification  meeting notes  of  02/03/88.   Carcinogen
Risk  Assessment  Verification  Endeavor  (CRAVE)  Work  Group,  Office  of  Health
and Environmental Assessment,  Washington, DC.
0626h
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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.

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.   19765.   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  NHro-
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.

Furl urn
Cohen,  S.H.,  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
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.

Glycldaldehyde
U.S.  EPA.   1989.   Health and  Environmental  Effects Document  for Glycid-
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.


Davis,  K.   1965.  Pathology report  on mice fed  aldMn,  dleldrln, heptachlor
and heptachlor epoxlde  for  two  years.   Internal  FDA memorandum to Dr. A.O.
Lehman,  July 19.

Epstein,  S.S.    1976.   Carclnogenldty  of  heptachlor and  chlordane.   Sd.
Total Environ.   6:  103-154.
 NCI (National Cancer Institute).  1977.   Bloassay  of  HePtac*lonr
 Carclnogenldty.  NCI  Cardnogenesls  Tech.  Rep. Ser.  No.  9,  DHEW No.  (NIH)
 77-809.

 Reuber,   M.D.    1977.   Hlstopathology  of carcinomas  of  the  1Jcver1 ,_lnll.!;Ue
 Ingesting heptachlor or heptachlor epoxlde.   Exp. Cell. Blol.   45:  147-157.

 U S   EPA   1986    Carclnogenldty  Assessment  of  Chlordane and  Heptachlor/
 Heptachlor  Epoxlde.   Prepared  by  the  Office  of  Wealth  and  Environmental
 Assessment, Carcinogen Assessment Group, Washington, DC.  OHEA-C-204.
 0626h                               D-105

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U.S. EPA.   1987a.  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.  1987b.  Integrated Risk  Information  System (IRIS).   Risk estimate
for carclnogenlclty for  heptachlor.   Online.  (Verification  date 04/01/87.)
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
Koclba,  R.J., D.G. Keyes, G.C.  Jersey  et al.   1977a.  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.

Hexachlorocyclohexane-alpha
Ito,  N., H.  Nagasaki, M.  Aria, et al.   1973.   H1stolog1cal  and ultrastruc-
tural  studies on  the hepatocardnogenlcHy  of  benzene  hexachlorlde In mice.
J.  Natl. Cancer  Inst.  51:817-826.

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.    1986.   Integrated  Risk  Information  System (IRIS).   Carclnogen-
 lclty   Assessment  for  Lifetime  Exposure  to   alpha-Hexachlorocyclohexane.
Online.   (Verification  date  12/17/86.)   Office  of  Health  and  Environmental
Assessment,  Environmental  Criteria  and  Assessment Office, Cincinnati, OH.


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Hexachlorocyclohexane-beta
Thorpe.  E.   and  A.I.T.  Walker.    1973.   Toxicology  of  deldrm  (HEOD)   II.
Comparative  long-term  oral  toxldty  studies  in  mice  wHh  dieldrin,  DDT,
phenobarbitone, beta-HCH and gamma-HCH.  Food Cosmet. Toxicol.   11:  433-442.

U.S.  EPA.   1986.   Integrated  Risk  Information  System  (IRIS).   Carclnogen-
UHy   Assessment   for  Lifetime   Exposure   to  beta-Hexachlorocyclohexane.
Online.   (Verification date 12/17/86.)   Office of  Health  and  Environmental
Assessment, Environmental Criteria and Assessment Office, Cincinnati,  OH.

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.

Hexachlorocyclohexane-delta
Ho,  N., H.  Hagasakl,  M.  Aral, S.  Suglhara and S.  Makiura.   1973.   Hlsto-
loglc  and  ultrastructural  studies on  the  hepatocardnogenicity  of  benzene
hexachlorlde  In mice.   J. Natl. Cancer Inst.  51(3): 817-826.

Ho,  N., H.  Nagasaki,  H.  Aoe, et  al.   1975.  Brief communication: Develop-
ment   of  hepatocellular  carcinomas   1n  rats   treated  with  benzene  hexa-
chlorlde.   0.  Natl. Cancer  Inst.   54:  801-805.

Nagasaki,  H.,  S.  Tomil, T. Mega, H, Marugaml  and  N.  Ho.   1972.  Hepato-
carcinogenlc   effect   of  a-,  B-,  Y-.   4-1somers   of   benzene  hexachlorlde
In  mice.  Gann.  63(3):  393.

U S  EPA.   1986.   Integrated  Risk  Information  System  (IRIS).   Carcinogen-
iclty  Assessment   for   Lifetime   Exposure   to   delta-Hexachlorocyclohexanes.
Online.  {Verification  date 12/17/86.)   Office  of  Health  and Environmental
Assessment,  Environmental  Criteria and Assessment Office, Cincinnati, OH.

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.

Hexachlorocvclohexane. gamma (Lindane)                         ,  ,Ucnn,  TT
Thorpe, E.  and A.I.T. Walker.   19/3.  The  toxicology  of *l*™r™WW'"'
Comparative  long-term oral  toxlcHy studies   in  mice with  dieldnn   DDT,
phenobarbitone, beta-BHC and gamma-BHC.   Food Cosmet.  Toxicol.  11: 433-442.

U  S  EPA    1984    Health  Effects  Assessment for Lindane.   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 E/fects Profile for Hexachloro-
  yiohex'anes   Prepared  by the  Office   of  Health  and  EnvlroAmenta   Assess-
ment,  Environmental  Criteria  and  Assessment Off Ice  Cincinnati,  OH for the
 Office of Solid Waste and Emergency Response, Washington,  DC.

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U.S. EPA.   1986.   Integrated Risk Information System  (IRIS).   Risk  estimate
for  carclnogenlclty  for  hexachlorobutadlene.   Online.   (Verification  date
11/12/86.)   Office of  Health  and  Environmental  Assessment,  Environmental
Criteria and Assessment Office, Cincinnati, OH.

Hexachlorocyclohexane-epsllon
Goto, H.,  H.  Hattorl,  T. Mlyagawa  and M. Enomoto.   1972.   Ecological  chem-
istry. II.  Hepatoma formation  1n mice after  administration  of  high  doses  of
hexachlorocyclohexane  Isomers.   Chemosphere.   1:  279-282.

U.S.  EPA.   1986.  Integrated  Risk  Information  System  (IRIS).   Carclnogen-
lclty  Assessment  for  Lifetime  Exposure  to  epIsllon-Hexachlorocyclohexane.
Online.   (Verification  date 12/17/86.)   Office  of Health  and  Environmental
Assessment, Environmental Criteria and Assessment Office, Cincinnati, OH.

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.

Hexachlorocyclohexane-technlcal
Honlt, K.M..  C.S.  Soman  and V. Samatl.  1983.  Hexachlorocyclohexane-lnduced
tumor1gen1c1ty  In  mice under  different  experimental  conditions.   Tumorlgen-
IcHy.   69: 383-386.

U.S.  EPA.  1986.   Integrated   Risk  Information  System  (IRIS).   Carclnogen-
lclty  Assessment  for  Lifetime  Exposure  to   Technlcal-Hexachlorocyclohexane.
Online.   (Verification date 12/17/86.)   Office  of Health  and  Environmental
Assessment, Environmental Criteria and Assessment Office, Cincinnati, OH.

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.

Hexachloroethane
NCI  (National  Cancer  Institute).   1978.   Bloassay of  Hexachloroethane for
Possible Carclnogenlclty.   NCI  Cardnogenesls  Tech.  Rep.  Ser. No.  68, OHEW
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-4W5-80-029.  NTIS
PB  81-117400.

U.S.  EPA.  1986.  Integrated  Risk  Information System (IRIS).  Risk  estimate
for   carclnogenlclty   for   hexachloroethane.   Online.   (Verification  date
07/23/86.)  Office  of  Health  and  Environmental  Assessment,  Environmental
Criteria and  Assessment  Office,  Cincinnati, OH.

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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Hexachloroethane
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.

Hydrazlne/Hydrazlne sulfate
Blandfiori,  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  ToxIcHy  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.   1987.   Integrated  Risk Information System (IRIS).  Reference Dose
(RfD)  for  Oral  Exposure  for  Hydrazine/Hydrazine Sulfate.  Online.  (Verifi-
cation  date  06/03/87.)   Office  of  Health  and Environmental  Assessment,
Environmental Criteria and Assessment Office, Cincinnati, OH.

Isophorone
NTP  (National  Toxicology Program).   1986.   Toxicology and  carcinogenesls
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.   1986a.  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.


UTsT  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   1988   Integrated  Risk  Information System  (IRIS).  Risk estimate
for' carclnogenidty   for  lead.    Online.    (Verification   date   05/04/88.)
Office  of Health  and  Environmental  Assessment,  Environmental  Criteria and
Assessment  Office, Cincinnati,  OH.
 0626h
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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.    1987.   Integrated  Risk  Information  System (IRIS).   Cardnogen-
Iclty Assessment  for  Lifetime  Exposure  to  Hethoxychlor.  Online.   (Verifica-
tion  date   10/07/87.)   Office   of   Health  and   Environmental   Assessment,
Environmental Criteria and Assessment Office, Cincinnati, OH.

2-Methoxy-5-nUroan1l1ne
NCI  (National  Cancer  Institute).   1978.  Bloassay  of  5-n1tro-o-an1s1d1ne  for
possible  cardnogenlclty.    NCI   Carclnogenesls  Tech.  Rep.  Ser.  No. 127.
123 p.

U.S.  EPA.   1987.  Health and Environmental Effects Profile for  2-Methoxy-5-
nltroanlUne.   Prepared by  the  Office of Health  and Environmental  Assess-
ment,  Environmental  Criteria and  Assessment Office,  Cincinnati,  OH  for  the
Office of Solid Haste and Emergency Response, Washington, DC.

2-Hethylanlllne
Hecht,  S.S., A.  El-Boyoumy, A.  Rlvenson  and E.  F1ala.   1982.   Comparative
cardnogenlclty  of o-tolu1d1ne  hydrochlorlde  and o-n1trotoluene  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-Methylan111ne hydrochlorlde
Hecht,  S.S., A.  El-Boyoumy, A.  Rlvenson  and E.  Flala.   1982.   Comparative
cardnogenlclty  of o-tolu1d1ne  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-Hethylan1l1ne  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.

Methyl chloride
CUT  (Chemical  Industry Institute of Technology).   1983.   Final  Report  on
24-Month Inhalation Study on Methyl  Chloride.  Prepared  by  Battelle-Columbus
Laboratories, Columbus, OH.

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.
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4.4-Methylenebis benzelamine
NTP   (National   Toxicology  Program).    1983.    Cardnogenesls   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-Methylenebis.   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' -Hethylene-bis{N.N' -dimethyl )an1Hne
NCI (National  Cancer Institute).   1979.   Bloassay of 4,4'-methylenebis(N,N-
dimethyl)benzenam1ne  for  possible   carcinogenlclty.   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-bis(N,N'-dimethyl)an1l1ne.   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.  Integrated  Risk  Information System  (IRIS).   Carcinogen-
lclty Assessment  for  Lifetime  Exposure to  4,4-'Methylene-b1s(N,N'-dimethyl)-
anlllne.    Online.   (Verification  date  04/05/89.)   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  Vn mice.    Prepared  by  Hazelton Laboratories,
America Inc., Vienna, VA.  Unpublished.

NTP  (National  Toxicology  Program).   1986.   Toxicology  and  carclnogenesis
studies  of  dichloromethane (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.   1985b.  Addendum to  the  Health  Assessment  Document for  Dichloro-
methane  (methylene chloride).   Updated  Carcinogenlclty 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.   1986.   Integrated  Risk  Information  System  (IRIS).   Risk Estimate
for   Carcinogenicity   for   Dichloromethane.    Online.    (Verification   date
12/04/86.)   Office  of   Health and  Environmental  Assessment,  Environmental
Criteria  and Assessment Office, Cincinnati, OH.
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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 Maste and Emergency Response,  Washington, DC.

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.

Hethvlhvdrazlne
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-Heth¥l-5-nUroan1l1ne
NCI  (National Cancer  Institute).   1978.   Bloassay of  5-n1tro-o-tolu1d1ne for
possible carclnogenlcHy.  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.

M1rex
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, Environ-
mental  Criteria  and  Assessment  Office.  Cincinnati.   OH  for  the  Office  of
Solid Waste and Emergency Response. Washington, DC.

Nickel
Chovll, A., R.B.  Sutherland  and  H.  Halllday.   1981.   Respiratory cancer In  a
cohort  of sinter  plant workers.  Br. J. Ind.  Ned.  38:  327-333.

Enterllne,  P.E.  and 6.M. Marsh.  1982.   Mortality among workers 1n a nickel
refinery  and alloy  manufacturing  plant  1n  West  Virginia.    J.  Nat.  Cancer
Inst.   68:  925-933.
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Magnus,  K.,  A.  Andersen  and A.  Hogetvelt.    1982.   Cancer of  respiratory
organs  among  workers  at  a nickel  refinery  In Norway.  Int. J.  Cancer.  30:
681-685.

Peto, J., H. Cuckle,  R.  Doll, et al.  1984.  Respiratory cancer mortality of
Welsh  nickel  refinery  workers.    In:  Nickel  In  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.  1987a.   Integrated Risk Information System (IRIS).   Risk estimate
for  cardnogenldty for  nickel  refinery  dust.  Online.   (Verification  date
04/01/87.)   Office  of Health and  Environmental  Assessment,  Environmental
Criteria and Assessment Office, Cincinnati, OH.

U.S. EPA.  1987b.   Integrated Risk Information System (IRIS).   Risk estimate
for  cardnogenldty  for  nickel  subsulflde.  Online.   (Verification  date
04/01/87.)   Office  of Health and  Environmental  Assessment,  Environmental
Criteria and Assessment Office, Cincinnati, OH.

NUrofurazone
Erturk,  E.,  J.E.  Morris, S.M.  Cohen,  et al.   1970c.   Transplantable  rat
mammary  tumors  Induced by 5-n1tro-2-furaldehyde semlcarbazone  and  by  formic
acid   2-[4-(5-n1tro-2-furyl)-2-th1azolyl]hydrazide.    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-Nltropropane
Lewis,  T.R.,   C.E.  Ulrich and  W.M.  Busey.    1979.   Subchronic  inhalation
toxldty of  nltromethane  and 2-n1tropropane.  3.  Environ.  Pathol.  Toxicol.
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.

N-Nltrosodl-n-butvlamlne
Bertram, O.S.  and  A.W.  Craig.  1970.   Induction  of bladder tumors In  mice
with dlbutylnltrosamlnes.  Br. J. Cancer.  24: 352-359.
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U.S.  EPA.    1986a.   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.   1986b.  Integrated  Risk  Information System  (IRIS).   Cardnogen-
Iclty   Assessment  for   Lifetime   Exposure   to   N-N1troso-d1-n-butylam1ne.
Online.   (Verification  date 10/29/86.)  Office  of Health and  Environmental
Assessment, Environmental Criteria and  Assessment Office, Cincinnati,  OH.

N-N1trosodlethano1am1ne
Lljinsky. W.  and  R.M.  Kovatch.   1985.   Induction of liver tumors  In  rats  by
nltrosodlethanolamlne 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.   1987.    Integrated  Risk  Information  System  (IRIS).   Carclnogen-
1c1ty  Assessment  for  Lifetime  Exposure to  N-Nltrosod1ethanolam1ne.   Online.
(Verification date  01/28/87.)   Office  of  Health  and  Environmental  Assess-
ment, Environmental  Criteria and Assessment  Office, Cincinnati,  OH.

N-NUrosodlethylamlne
Peto,  R.,  R. Gray,  P.  Brantom and P.  Grasso.  1984.    Nltrosamlne cardno-
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  Sc1.  Publ.   57:
627-665.

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).   Carcinogen-
Idty  Assessment  for  Lifetime  Exposure  to N-NHrosodlethylamlne.   Online.
(Verification date  10/29/86.)   Office  of  Health  and  Environmental  Assess-
ment, Environmental  Criteria and Assessment  Office, Cincinnati,  OH.

N-N1trosod1methylam1ne
Peto, R.,  R.  Gray,  P.  Brantom and P.  Grasso.  1984.    Nltrosamlne 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.    1986a.   Health   and Environmental  Effects  Profile  for  Nltros-
amines.   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.   1986b.   Integrated  Risk  Information System  (IRIS).   Cardnogen-
iclty  Assessment  for  Lifetime  Exposure to  N-N1trosod1methylamine.   Online.
(Verification  date  10/29/86.)   Office  of  Health  and Environmental  Assess-
ment, Environmental Criteria and Assessment Office, Cincinnati,  OH.

N-Nltrosodiphenylamine
NCI  (National  Cancer  Institute).  1979.   Bioassay of N-nHrosodlphenylamine
(CAS No.  86-30-6)  for possible  carcinogenicity.   NCI  Carcinogenesls  Tech.
Rep. Ser. No. 164, NIH 79-1720.  NTIS PB298-275.

Peto,  R.,  R. Gray, P.  Brantom and  P.  Grasso.   1984.  NUrosoamine carcino-
genesis  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  Sci.  Publ.   57:  627-
665.

U.S. EPA.   1980.   Ambient Water  Quality  Criteria  Document  for  Nitrosamines.
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.   N1IS  PB
81-117756.

U.S.  EPA.   1986a.    Health  and  Environmental  Effects   Profile  for  Nitros-
amines.   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).  Carcinogen-
icity  Assessment  for  Lifetime Exposure  to N-N1trosod1methylamine.  Online.
(Verification date  10/29/86.)   Office of Health and Environmental  Assess-
ment,  Environmental  Criteria  and  Assessment Office,  Cincinnati, OH.

U  S   EPA    1987a.   Health   Effects Assessment  for  N-Nitrosodiphenylamine.
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   1987b   Integrated Risk  Information System (IRIS).  Risk  estimate
for'carcinogenldty for  N-nHrosodlphenylamine.   Online.  (Verification date
02/11/87.)    Office  of  Health  and   Environmental  Assessment,  Environmental
Criteria  and Assessment Office,  Cincinnati, OH.

N-NUrosod1-n-propy1am1ne                                                 T
Druckrey	H.  1967.Quantitative  aspects  in  chemical  carcinogens.    In:
Potential  Carcinogenic  Hazards  from  Drugs.   UICC  Monograph,  Series  7.
 Springer-Verlag,  Berlin,  p.  60-78.

 Oruckrey, H.,  R. Puressman,  S.  Ivankovic  and D.  Schmahl.   1967.  Organo-
 troplc carcinogenic  effect  of 65 different  N-nHroso compounds  on  BD  rats.
 Z. Krebsforsch.  69: 103-201.
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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.  1987.  Integrated  Risk  Information  System (IRIS).   Cardnogen-
Iclty   Assessment   for   Lifetime  Exposure   to   N-N1trosod1-n-propylam1ne.
Online.   (Verification  date 02/11/87.)  Office  of Health and  Environmental
Assessment, Environmental Criteria and  Assessment Office,  Cincinnati,  OH.

N-N1trosomethylethylaro1ne
Druckrey,  H.   1967.   Quantitative aspects  In chemical carclnogenesls.   In.:
Potential  Carcinogenic  Hazards  from   Drugs.   UICC   Monograph,   Series   7.
Springer-Verlag, Berlin,  p. 60-78.

Druckrey,  H.,  R.  Puressman,  S.  Ivankovlc  and D.  Schmahl.   1967.   Organo-
troplc  carcinogenic  effect  of 65  different  N-nltroso  compounds on BD  rats.
Z. Krebsforsch.  69:  103-201.

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.  1987.  Integrated  Risk  Information  System (IRIS).   Carclnogen-
IcHy  Assessment  for  Lifetime  Exposure   to  N-N1troso-N-methylethylam1ne.
Online.   (Verification  date 02/11/87.)  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  NUros-
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.

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.  1987b.  Integrated Risk Information System  (IRIS).   Risk estimate
for carclnogenldty for  parathlon.  Online.   (Verification  date  08/05/87.)
Office  of Health  and  Environmental  Assessment,  Environmental  Criteria  and
Assessment Office,  Cincinnati,  OH.

1.2.3.4.5-Pentabromo-6-chlorocyclohexane
Blair,  E.H.   1981.  TSCA sec  8(e)  submission 8EHQ-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.
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PentachloronUrobenzene
Innes, 3.R.M.,  B.M.  Ulland,  M.G. Valeria, et  al.   1969.   Bloassay  of  pesti-
cides  and  Industrial  chemicals  for  tumorlgenlclty  In  mice:  A  preliminary
note.  3. Natl. Cancer Inst.  41: 1101-1114.

U.S.  EPA.   1986.   Health and Environmental  Effects  Profile  for  Pentachloro-
nUrobenzene.   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-Phenylenedlamlne
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
toxlclty or  cardnogenlclty.  J.  Environ. Pathol. Toxlcol.  2(2): 325-256.

2-Phenylphenol
Hlraga  K.  and  T.  Fujll.   1981.   Induction  of  tumours  of the urinary system
In  F344  rats  by  dietary  administration  of sodium  o-phenylphenate.   Food
Cosmet.  Toxlcol.   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.

Polyaromatlc hydrocarbons  (PAH)
Neal, 3. and R.H.  Rlgdon.  1967.  Gastric tumors  In  mUe fed benzo[a]pyrene;
A quantitative study.  Tex.  Rep. Blol.  Med.   25:  553.

Thyssen, J., 3. Althoff. 6. Klmmerle and U.  Mohr.   1981.  Inhalation  studies
with  benzo[a]pyrene  In   Syrian  golden  hamsters.   3.   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.   NT1S PB  81-117806.

 U S  EPA    1984     Health Effects  Assessment for Polycycllc Aromatic Hydro-
 carbons (PAHs)    Prepared by  the Office of  Health  and  Environmental  Assess-
 ment, Environmental  Criteria   and  Assessment  OffIce  Cinclnnat1  OHfor  the
 Office  of  Emergency and  Remedial Response,  Washington, DC.   EPA  540/1-Bb-
 013.  NTIS PB86-34244/AS.

 n  s  FPA    1987    Integrated   Risk Information System (IRIS).   Risk  estimate
 for'  carclnogeniclty   for  benzo[a]pyrene.    Online.     (Verification   date
 01/07/87.)   Office  of  Health and  Environmental  Assessment,  Environmental
 Criteria and Assessment Office, Cincinnati, OH.
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Polybrominated biphenyls (PBBs)
NTP  (National  Toxicology Program).   1983.   Carclnogenesis studies  of  poly-
brominated blphenyl mixture  in  F344/N  rats  and  B6C3F1  mice (gavage studies).
Firemaster FF-1.  Case No. 67774-32-7.  NTP, Research Triangle Park, NC.

U.S.  EPA.   1989.  Health  and Environmental Effects Document  for  Polybromi-
nated  Biphenyls  {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.

Polychlorinated biphenyls (PCBs)
Norback,  D.H.  and R.H.  Ueltman.   1985.  Polychlorinated  blphenyl  induction
of  hepatocellular  carcinoma  in  the  Sprague-Dawley  rat.   Environ.  Health
Perspect.  60: 97-105.

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.  1987a.    Drinking  Water  Criteria   Document  for  Polychlorinated
Biphenyls  (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.  19875.  Integrated Risk  Information  System  (IRIS).   Risk estimate
for  carcinogenidty  for  polychlorinated  biphenyls.   Online.   (Verification
date  04/22/87.)   Office  of   Health  and  Environmental Assessment,  Environ-
mental Criteria and Assessment Office,  Cincinnati,  OH.

Propylene oxide
Dunkelberg, H.   1982.   Carcinogenidty of  ethylene oxide and 1,2-propylene
oxide upon Intragastric administration to rats.   Br. 3. Cancer.  46: 924-933.

NTP  (National  Toxicology  Program).   1985.  Toxicology   and  carcinogenesis
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.  Giddens,  G.A.  Boorman, R.  Kovatch,  J.E. Haseman and W.J.
Clarke.   1986.   Nasal cavity  neoplasia  in 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.   1989.   Integrated  Risk  Information  System (IRIS).   Carcinogen-
idty  Assessment  for  Lifetime  Exposure  to Propylene  Oxide.    Online:  Input
pending.   (Verification  date 05/30/89.)  Office of  Health and Environmental
Assessment, Environmental Criteria and Assessment Office,  Cincinnati, OH.
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Quinollne
Hirao, K.,  Y.  Shinohara, H.  Tsuda,  et al.   1976.   Carcinogenic  activity  of
qulnloine on rat liver.  Cancer Res.  36: 329-335.

U.S.  EPA.   1985.   Health  and  Environmental  Effects Profile  for  Quinollne.
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 (Cyclonlte)
Llsh,  P.M., B.S.  Levine,  E.M.  Furedl,  E.M. Sagartz  and  V.S.  Rac.   1984.
Determination  of the chronic mammalian  toxicologlcal effect  of RDX:  Twenty-
four  month chronic  tox1c1ty/cardnogen1c1ty  study  of hexahydra-1,3,5-trl-
n1tro-l,3r5-tr1az1ne  (RDX)  1n  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,   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.

Sodium dlethyldlthlocarbamate
BRL  (Blonetlcs Research Laboratories).   1968a.   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.  NT1S
PB223159.

U.S.  EPA.   1988.   Health  and  Environmental  Effects  Document   for  Sodium
diethyldlthiocarbamate.   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.

2.3.7.8-TCDD
Kociba,  R.J.,  D.G.  Keyes, 3.E.  Bower  et al.  1978.   Results of a  two-year
chronic  toxidty   and oncogenlclty  study  of 2,3,7,8-tetrachlorodibenzo-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.

U  S   EPA   1985a.   Drinking  Water Criteria  Document for  2,3,7,8-Tetrachloro-
dibenzo-p-dloxin.    Prepared  by  the  Office  of  Health   and Environmental
Assessment, Environmental Criteria and  Assessment  Office  Jlnclnnatl.  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 Polychlorinated D1benzo-p-
dioxin  '  Office   of   Health  and   Environmental   Assessment,  Environmental
Criteria and  Assessment  Office.  Cincinnati. OH.   EPA 600/8-84-014F.  NTIS
 PB86-122546.
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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, DHEH No. (NIH) 78-827.

U.S.  EPA.   1980.   Ambient  Hater 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 Hater  Regulations and  Standards, Hashlngton,  DC.   EPA-440/5-80-029.   NTIS
PB 81-117400.

U.S.  EPA.   1986.  Integrated Risk  Information System (IRIS).   Risk  estimate
for  carclnogenldty  for  1,1,2,2-tetrachloroethane.   Online.   (Verification
date  06/26/86.)    Office  of  Health  and Environmental  Assessment,  Environ-
mental 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, DHEU 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.   1985a.   Drinking  Hater 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
Hater, Hashlngton, DC.  Final Document.  NTIS PB 86-118114.

U.S.  EPA.   1986a.   Addendum to  the  Health  Assessment  Document  for  Tetra-
chloroethylene   (Perchloroethylene):   Updated   Carclnogenldty  Assessment.
Dfflce of  Health and Environmental  Assessment,  Carcinogen Assessment  Group,
Hashlngton, DC.  EPA/600/8-82/005FA.   External  Review Draft.

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,  Hashlngton, DC.   ECAO-CIN-H009a.

p.tt.a.a-Tetrachlorotoluene
Fukada,  K.S.,  HatsashHa  and  K.  Takemotol.   1979.    Carclnogenldty  of
p-chlorobenzotrlchlor1de.   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 Haste and Emergency Response, Hashlngton, DC.

Tetrachlorovlnphos (Stlrofos)
NCI  (National  Cancer Institute).  1978.   Bloassay of  Tetrachlorvlnphos  for
Possible  Carclnogenldty.   NCI  Carcinogen.  Tech.  Rep. Ser.  No.  33.   NTIS
PB278650.
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 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.

 2,4-Toluenedlamine
 NCI  (National  Cancer  Institute).   1979.   Bloassay of  2,4-d1am1notoluene 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-Tolu1d1ne
 Hecht,  S.S.,  K. El-Bayoum1,  A. Rlvenson  and  E.  Flnala.  1982.  A  Study of
 chemical  carclnogenldty of  o-tolu1d1ne  hydrochlorlde  and  o-nltrosotoluene
 1n rats.  Cancer Lett.  16: 103-108.

 U.S.  EPA.  1984.   Health  and  Environmental Effects  Profile  for  Tolu1d1nes.
 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-To!u1d1ne
 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.

 Welsburger, E.K., A.B.  Russfleld and  F. Homburger,  et al.  1978.   Testing of
 twenty-one  environmental  aromatic   amines  of   derivatives   for   long-term
 toxlclty  or carc1nogen1c1ty.  J. Environ. Pathol. Toxlcol.  2(2):  325-256.

 Toxaphene
 Litton Blonetlcs,  Inc.  1978.   Carcinogenic  evaluation  In  mice:  Toxaphene.
 Prepared  by  Litton  Blonetlcs,  Inc.,  Kensington,  MD   for  Hercules,  Inc.,
 Wilmington, DE.

 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.  1987a.  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.  1987b.   Integrated  Risk  Information System (IRIS).   Risk  estimate
 for carclnogenldty  for toxaphene.  Online.  (Verification date 03/06/87.)
Office of Health and Environmental  Assessment,  Environmental Criteria  and
Assessment Office,  Cincinnati,  OH.
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 2.4.6-Trlchloroanlllne and  2.4,6-tr1ch1oroan1line hydrochloride
 Welsburger,  E.L..  A.B.  Russfleld,  R. Homburger, et al.  1978.  Testing of 21
 environmental  aromatic  acmlnes  or  derivatives  for  long-term  toxlclty  or
 cardnogenlclty.   3.  Environ.  Pathol. Toxlcol.  2: 235-258.

 U.S.  EPA.   1987.   Health  and Environmental  Effects  Document for Trlchloro-
 anllines.   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.

 1.1,2-Trlchloroethane
 NCI  (National Cancer Institute).    1978.   Bloassay  of 1,1,2-trlchloroethane
 for  possible  cardnogenlclty.   NCI  Carclnogenesls  Tech.  Rep. Ser.  No.  74,
 DHEH No.  NIH 78-1324.

 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-Tr1chloroethane.
 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  carclnogenldty  for 1,1,2-trlchloroethane.   Online.   (Verification  date
 07/23/86.)   Office  of  Health and  Environmental Assessment,  Environmental
 Criteria  and Assessment Office, Cincinnati, OH.

 Trlchloroethylene
 Fukuda, K.,  K.  Takemoto,  H.  Tsuruta.   1983.   Inhalation  carclnogenlclty  of
 tMchloroethylene  1n  mice and  rats.   Ind. Health  21:  243-254.

 Maltonl,  C.,  6.  Lefemlne,   G.  Cottl.   1986.   Experimental   Research  on
 Trlchloroethylene  Carclnogenesls.   Archlv.  Res.  Industrial  Carclnogenesls
 Series.   Maltonl,   C.,  Mehlman,  H.A.,  Eds.,  Vol.  V.   Princeton Scientific
 Publishing Co., Inc., Princeton, NJ, p. 393.

 NCI   (National  Cancer  Institute).   1976.    Carclnogenesls   bloassay   of
 tMchloroethylene.   NCI  Carclnogenesls  Tech.  Rep. Ser.  No. 2, DHEW  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.
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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  carclnogenlcity.   NCI Carclnogenesls Tech.  Rep.  Ser.  No.  155,


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-Trichlorophenol.
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  carclnogenlcity for  2,4,6-trlchlorophenol.   Online.   (Verification  date
10/26/86.)    Office  of  Health  and  Environmental   Assessment,  Environmental
Criteria and Assessment Office, Cincinnati, OH.

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.

Trifluralin
Emmerson,  J.L.,  E.C.   Pierce,   J.P.  McGrath,  et  al.    1980.    The  Chronic
Toxlcity of Compound 36352  (1r1fluralln)  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 E11 Lilly and Co.,  Indianapolis, IN).

U.S.  EPA.   1984.  Health and Environmental  Effects Profile for Trifluralin.
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.   Integrated Risk  Information System  (IRIS).   Carclnogen-
lcity Assessment  for Lifetime Exposure  to  Trifluralin.   Online.   (Verifica-
tion  date  06/24/87.)   Office   of  Health  and  Environmental  Assessment,
Environmental  Criteria  and Assessment Office, Cincinnati, OH.

Trlmethyl phosphate
NCI (National  Cancer Institute).   1978.  Bloassay  of trlmethylphosphate  for
possible carclnogenlcity.  NCI Carcinogen. Tech. Rep.. Ser. No. 81.
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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  lexicological  Profile  for Vinyl Chloride.  U.S.
Public Health Service.  Public Comment Draft.

Feron,  V.3.,   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.

Haltonl,  C.,  6.  Lefemlne,  A.   ClUbertl   et  al.    1980.   Vinyl  chloride
cardnogenlclty  bloassays  (BT  project)  as  an experimental  model  for  risk
Identification  and assessment  1n  environmental  and  occupational  carclno-
genesls.   Epldemlol.  An1m.  Epidemic!. Hum: Cas  Chlorure  Vlnyle  Monomere,
(Reun Club Cancerog Ch1m),  20th,  Meeting Date 1979,  p. 11-112.   Pub! Essent,
Paris, France.

Maltonl,  C.,  G.  Lefemlne,  A.   ClUbertl   et  al.    1981.   Cardnogenlclty
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  for Vinyl  Chloride.
Office of Drinking Water, Washington, DC.  Final Draft.  NTIS PB86-118320.

U.S.  EPA.   1985b.   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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                                   *U.S. GOVERNMENT PRINTING OFFICE: 1990—720-623/D06653

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