U.S. EPA, Office of Toxic Substances Existing Chemicals Program, Question and Answer Summary, EPA Seminar on Industry Obligations Under TSCA (May 5, 1987) (ELR Order No. AD-484)

AuthorCarolyne R. Hathaway/William K. Rawson/Ann Claassen/Julia A. Hatcher
Pages607-613
Q&A Summary From EPA Seminar on Industry Obligations Under TSCA (May 5, 1987) Page 607
Question and Answer Summary From
EPA Seminar on Industry Obligations
Under TSCA (May 5, 1987)
EPA
undated
QUESTION A ND ANSWER SUM MARY EPA
SEMINA R ON INDUSTRY OBLIGATIONS
UNDER TSC A (MAY 5, 1987) OTS EXISTI NG
CHEMICA LS PROGRAM
I. CAIR
Q.1. At the Industry mee ting, a speaker stat ed
that the comment s received on the proposed CAI R
would be reviewed a fter the nal ru le is promul-
gated. Doesn’t thi s negate the extensive comment s
received?
A.1. e speaker actual ly said that the comments on
CAIR were bein g studied and serious consideration
would be given to them in preparin g the nal rule.
II. Chemical Testing
Q.2. What is E PA doing to prevent or lim it the
“unnecessa ry and cruel” use of a nimals in toxicity
testing prog rams?
A.2 EPA only requires testin g in cases that meet two
criteria: (1) existing data are ina dequate; and (2) test-
ing is necessar y to obtain the data. We do not use
direct anim al testing for all chemicals; we a lso use
other methods to evaluate a c hemical’s toxicity where
feasible. For example, the Age ncy uses a t ype of com-
puter modeling that employs data from chem icals that
are structu rally-related to certain classes of c hemicals
being investigated .
Computer modeling or computer simulation provides
a way to use all the dat a available on previous animal
tests. However, testing may sti ll be required to obtain
information not previously known a nd necessary for
evaluation of chemica l toxicity. Whenever possible,
EPA uses in vitro assays before requ iring whole animal
studies. Nevert heless, many e ects require the whole
organism to be stud ied.
EPA rmly supports the development of alternatives
to the use of anima ls in toxicity evaluation. Many of
these methods are s till in the early stages of develop-
ment. EPA has a research eort under way to develop
and validate a lternative test met hods that u se fewer
animals. e A gency is working on alternative tests for
mutagenicity, developmental and reproductive toxic-
ity, neurotoxicity, and dosimetry. ese tests could
reduce both the numbers of ani mals, as well as the
cost of toxicity testing a nd other research. e Oce
of Pesticides and Toxic Substances already u ses several
alternative test method s and will continue to incorpo-
rate new ones as they bec ome accepted by the scienti c
community.
Q.3. What did you mea n by a special consideration
for “chemicals found i n the Great Lakes” in ref er-
ence to the Expo sure Based Test Rule?
A.3. In evaluati ng candidates for its rst test rule bas ed
on environmental monitoring data to obta in data to
identify human hea lth and environmental hazards of
substances with k nown human or environmental expo-
sure, one of the principal groups of chemica ls EPA has
considered is a list of chemica ls reported to be found in
the Great Lakes. One or more of the Great L akes list
chemicals may be in t he rst environmental monitor-
ing based rule.
Q.4. Why are chem icals that have been produced or
imported for yea rs without any problems on the list
of 73 OSW chemica ls? Sodium Sacchar in is such a
chemical. W hy is it being tested for hydrolysi s?
A.4. In the example you cited, Sacc harin has been
listed as a carci nogen by the EPA Carcinogen A ssess-
ment Group (CAG) and other reviewers. e original
OSW hazardous w aste lists were compiled by com-
bining many list s (CAG, CWA “priority pollutants,”
RTECS, etc). All chemica ls listed in Appendix VIII of
40 CFR Part 261 are being looked at for “relisting”; the
same data set is needed for a ll chemicals. e data will
be used in the fate and t ransport model to determine
new “concentration-based” lis tings.
Q.5. What is the biodeg radation test that is bei ng
required of the 73 OS W Chemicals?
A.5. e proposed biodegradation procedure would
generate microbiological tra nsformation rate data for
organic chemica ls in saturated subsurface materia ls.
e data will be u sed as part of a chemical trans-
port and fate model for asse ssing the fate of organic
chemicals leach ing into ground water from waste
management facil ities. e anaerobic tra nsformation
of chemicals in selec ted subsurface samples will be
estimated from subsur face microcosm studies using
methods recently reported by Wi lson et al. (198 6). e
procedures will be u sed to determine the length of the
adaptation period before detect able degradation can be
observed and the ha lf-life of the compound following
the adaptation period. Supporti ng laboratory methods
will be applied to the mea surement of residual test
chemicals, level s of persistent intermediate s, biomass,
and other physical-chemic al parameters. A minimum
of six subsurface sa mpling sites will be identied on
the basis of two temperat ures and three pH values.

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