Document ymb06M9ZL8nqnR1M2VyEp4z56
AR226-2840
EIOASSAY REPORT SUBMITTED TO
E. I. DUPONT DE NEMOURS & COMPANY
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A cute t o x i c i t y o f 8233 to rainbow
Bionom ics, In c , 790 Main S tr e e t Wareham, M a ssa ch u se tts Ju n e , 1973
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METHODS AND MATERIALS
This investigation was performed at the aquatic toxicology
laboratory of Bionomics, Inc., Wareham, Massachusetts. The
susceptibility of rainbow* trout (Salmo, gajrdneri) to 8233
(a light brown liquid tesjted as 100?S active) was measured in
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terms of the median tolerjance limit (TL^q ), the nominal
concentration of the chemical in water which causes 50 percent
response (death) under tha test conditions during a specified
time interval. The prediction of a T L ^ Value, and its 95#
confidence interval, was based on conversion of the concentrations
tested and the corresponding observed percent mortalities to
logs and probits respectively, and the subsequent mathematical
calculation of a linear
'' q t i a . The toxicity
of the chemical tested wajs evaluated under static bioassay conditions
for a 96-hour period.
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The test procedures for the static bioassays are in complete
accordance with the Pish ^ioassay procedure in the 1970
edition of Standard Methods (APHA) except for those conditions described below.
CBICompany Sanitized. Does not contain TSCA
Page two
The rainbow trout used jin these tests were obtained from a
commercial fish hatchery in Massachusetts and had a mean
weight of 1 .3 g and a mpan length of 58 mm. The test population
was held in the laboratpry hatchery facilities for at least
30 days prior to testing and during this period mortality was <2%. static bioassays Vere conducted in 5-gallon glass vessels
held in constant temperature water baths at 11c (- 1.0). The
vessels were not aerated, and there was a single introduction
of the test compound into the test, vessels. A solvent control,
utilizing the greatest amount of isopropyl alcohol contained
in any test vessel, was'conductid. fish were acclimated to the
test system containing reconstituted Water as the standard
diluent for at least 2h hours prior to testing. Ten fish
were exposed in each test vessel.
reconstituted water
used in the test system was jweparedj:% adding the following
chemicals to deionised viraten
Har dness 38 mg/l
mg of salt/llter wa ter_________
Na^COj
ca.SOjj; - MgSO^
KCT
48 30 30 2
The pH of the standard diluent was 7.1. and the methyl iI .
orange alkalinity was 3fj ppm as CaCQ^.. Dissolved oxygen
values for the various iest vessels ranged from 8.5
initially to 5.3 mg/l atj the end of the tests.
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The predicted TL^Q values;(95% confidence interval) are
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presented in Table 1. Tatjle 2 presents a summary of observed
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mortality for the bioassayf after and 96 hours of exposure.
Moribund fish generally beicame dark and lethaigic, lost
equilibrium, and expired.
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Company Sanitiz,ed. Does nof contain TSCACBll
SUBMITTED BY:
Bionomics, Inc. 790 Main Street Wareham, Massachusetts June, 1973
PREPARED BY:
Robert E. Bentley
APPROVED BY :
Kenneth J. Macek, ph.D. Director
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Table 1 -- Acute toxicijty of 8233 to rainbow trout (Salmo gairdneri).
These data ape based on results of bioassays conducted at
the aquatic jtoxicology laboratory of Bionomics, Inc., Wareham, Massachusetts.
Compound
8233
- milligran^/liter
iour
! 9b hour
8.63(6.94-10.90)b 5.64(4.14-7.69)
No Effect
Level
(mg/l)
4.20
Assay conducted at 11c (-1.0), mean weight of rainbow trout 1.3 g. 395% confidence intervaljs.
Company Sanitized. Does not contain TSCA CBi
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Table 2 -- Concentrations of 8233 tested and corresponding observed
percent mortality for rainbow trout (Salmo gairdneri) at
24 and 96 Hours during a static bioassay.
Compound 6233
Conce ntration (mg/1 )
18.0 j 14.0 i
10. 1
. .
7.5 5.6
4.2
3.2
contr Ol
,,
cntr ol (isopropyl alcohol)
...
4' hour
96 hour
100 100 100 100
4o 100 50 100
0 20 00 00
00
00
Company Sanitized. Does not contain T S C A CBI