Document RJQw0Vgj0LEwYbkjRvwDpe1kk
AR226-2366
DRAFT
-^(--------^
Purpose: Scope:
Proposal to Conduct a Genera) Human Health and Envlronmenta! Effects
Risk Analysts on C-8
08 The piHpose of this
environment from
project
is
to
evaluate
the
risks
to
human
health
and
the
and
disposalof
exposure to C-8. The analysis
duringmanufacture,
will
transport,
product
use,
semi-quantitative
estimates
of
risks
be conducted in a fashion so that exposures yielding
that
wiB
provide
can be identified ami recommendations on reducing these the bfgftestrisks
developed.. Risks from a way (hat will facilitate
manufacture,
transport
and
nsks can be product use will developed
future comparisons of risks estimated for potential C-8
caoltnedrnuacttievdesin. TpahreaBpero!,jiencwt whilcl hbehucmonadnuhcteeadlthin (Nee parts. The first two will be
characterized.
The
final
part
wBdevsfcp
and ecological conclusions
nsks
will
be
contrifamaihetiigtiesrtisks strategies
so
that
s-sccminendaiions
on for
exposures risk
that-
and alternatives can be developed. months to complete from the
management' ^ The project is estimated to takal 3
betow
will
require
time collaboration
of
initiation.
The Exposure analyses fisted
----
presented assume a Feb. 1,199w7ithSaBpUpraoppprrioatvealpdlaantet .p)ersonnel. (The dates
1. Human Health Risk
A. Hazard Identification
Time Line 4/18/97
Est.Cost($) 8000
08 Hazards to human
critical toxicity
health
will
be
reviewed
and
summarized
in
this
endpoints
of
relevance
to
human
health
risk
will
be
section. identified
The
dpiostceunstisael dd.osTihmeetHearsskteollbteoxuisceitdy forinterspecies extrapolation of risk will be and
summary wit) be updated as part of this task.
B. Dose-Response Anatysis
cTohnedduocstien-gresponse characteristics of
9/307 wBl be evaluated. This
43,200
where
benchmark dose analyses necessaiy. Appropriate
to
identify no-observed
may adverse
include effect levels
developed be
based
on
the
likely
dosimeters for mode of action.
interspecies extrapolation The phaimacola'netics
will
also
be
reviewed. If possible, rudimentary physiologically-based
of C-8 will also
dapopseroraeclahteiosnwsihllibpsewdieltvbeelodpeevdetloopfaecdiliintattheisinptheraespeecies extrappohlaatrimonacoofkriinsekt.icRsisks vs.
C. Bcposure Analysis
Reasonable exposure airborne, drinking
scenarios
for
C-8
will
be
9/3W37 developed. This
are
16,000 likely to include
durations
of
water, dermal, and other exposure will be developed.
oral
ingesta'onpathways.
Intake rates and
from
the
plant
site
to
help
characterize
Haskell these
will
work
with
an
assigned
person
(s)
transport, product use, and waste disposal exposure pathways tor manufacturing,
Hastes!!wriih ua!a These data will
on
u,-iC5rm-a{fon3
of
C-S
operations. The business in ths affected media (air,
will
provide
be tabulated.
Monte
Cario
techniques
may
be
used
water, soil). to calculate
dexaptae.ctTehdeucpopsetracsosnofcidiaetnecdewliimthittshifsortathseksineceluxpdeossuornelsy, dependingthe availabilityof
HaskeB personnel time.
D, Risk Characterization
Risks
will
be
summarized
according
to
the
major
12/1S97 routes of
16.000
dennat,
other oral) for each ). The risks will
C-fl
application
(manufacture,
exposure transport,
(air, water, product
disposal
concentrations
to
the
be characterized dose-response
by
comparing
the
likely exposure
use.
to as a Margin of Exposure. The charraeclatetiroiznasthioipn. wTihllis method is generally referred
provide the risk manager with
^
EI0093162
EID093162
DRAFT
information that will help identify the operations and exposure pathways that present
the highest risk. The characterizations will also enable future comparisons to be
made of potential risks posed by 08 alternatives.
11 Ecological Effects
Time Line
EsLCost(S)
A. Hazard Identification Hazards to key environmental health indicator species wilt be reviewed and
summarized in this section. The critical toxicityendpotntswBI be identified. Based on the current literature search, chronic studies in aquatic species will need to be
undertaken. Avian reproduction and avian food-chain aecumulationwili need
assessment; however this may be extrapolated using mammalian toxicology and P&PK data and E Fate information. The Haskell toxfcitysummary wilt be updated as part of this task.
1.) Hazard Assessment
8/15/97
2.) Tssting (Fish B^ and Daphrsid Chronic) 8/15/97
(This is w8h stalk renewal and analytical)
$10,000 $80,000
3.) Avian fifneeded)
8/15/97
$80,000
B. Exposure Analysis
Reasonable exposure scenarios for C-8 will be developed for the higher environmental exposure areas at the three manufacturing sites. Includingtheir respective disposal sites and a customer site. Intake rates and durations of exposure wfll be developed. Haste)! will work with an assigned person(s) from the plant site to
help characterize these exposure pathways for manufacturing, transport, product use. and waste disposal operations. The business will provide Haskell with data on
08 concentrations of in the affected media (air, water, soil). These data wilt be
tabulated. Monte Carto techniques may be used to calculate expected upper confidence limits for these exposures, depending oh the availability of data. The cost associated with this task includes only Haskell personnel time.
1.) Exposure Assessment-Washington Works 6/15/97
2.) Exposure Assessment-Dordrecht
8/15/87
3.) Exposure Assessment-Shimizu
9/15/97
4.) Exposure Assessment-Customer
10/15/97
8.000 6,000 2,000 2,000
0. Risk Characterization Risks win be summarized according to the major media of environmental exposure
08 (water, soil, air) for each application (manufacture, transport, product use,
disposal). The risks will be characterized by comparing the likely Predicted
Environmental Concentrations (PEC) to the Predicted No Effect Concentrations
(PNEC). This method is generally referred to as Hazard Quotient. The characterization will provide the risk managerwith information mat will help identify
the operations and exposure pathways that present the highest risk. The
characterizations wili also enable future comparisons to be made of potential risks
posed bv 08 alternatives.
12/15/&7
16,000
III. Recommendations on Risk Management Strategies and Alternatives
12/1507
4800
This section win evaluate collectively the risks identified to human health and
ecological receptors. Based on these analyses, recommendations will be made as to
which operations could be targeted to ensure risks are appropriately managed in the most cost effective manner. This will be a very subjective exercise (narrative) and will
require some Mereactbn with the appropriate people from the business.
ETO093163
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4 1 A.EI......for,.C8 material is o.qima/cubic-msterI ..
. . t. ... ...,,....,,........................................I...................................
4 2 1 ft3 = 0.028 m3
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44 0.06 Ibs = 27,180 mg
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......!...................... 1j ........ ............i....................................
4.5 30M cfm s 30,000 X 60 X 24 = 43,200,000 ft3 = 1,209,600 |m3
46 2.2470238e-2|mg/m3
or 0.022S mg/m3 111^^1
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