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METHODS AND MATERIALS
This investigation was performed at the aquatic toxicology
laboratory if Bionomics, ^nc., Wareham, Massachusetts. The
susceptibility of rainbow trout (Salrno '.gaig4neri) to 8230
(a light brown liquid teslied as 100^ active.) was measured in terms of the median tolerance limi t (TI<rn) the nominal
concentration of the chemical in wat'er .which causes 50 percent
response (death) under the test; -condla^t^^-^uring a specified
time interval. The predicptiori of a 'ma^: value, and its 35%
";'""".:''-t^y^
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confidence interval, was qasec' on coTiye&si'an of the concentrations
tested and the correspondjing" observed ;]a^'ee|)t mortalities -to logs and probits respectivrely,-and thtes^sequent mathematical calculation of a 'linear''r^resa:<^'^r^-l'eg|%^m-Tj.he toxicity
of the chemical tested was evaluate^ und^r^static bioassay
conditions for a 96-hour period,
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The test procedures for thie static -bioa'sssiyA are in complete
accordance with the Fish Bioassay Procedure in the 1970
edition of Standard Methods (APHA) except for those conditions
described below,
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The rainbow trout used in these test? were obtained from a
commercial fish hatchery in Massachusetts and had a mean
weight of 1.3 g and a mear, length of 58 mm. The test
population was held in the laboratory hatchery facilities
for at least 30 days prior to testing and during this peiicd
mortality ';:as <2.%. Static bioassays were 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 isopropyi alcohol
contained in any test vessel, was conducted. Fish were
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acclimated to the test sy-stem containing reconstituted water
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as the standard dilusnt for at least 24 hours prior to testing.
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Ten fish were exposed in each test vessel. The reconstituted
water used in the test system was prepared by adding the following
chemicals to deionized water;
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Hardness 38 ,'ng/l
mg NaHCO-
of
salt/liter CaSO^
wMgaStOe^r____K_'"_l _
48
30
30
2
The pH of the standard diluent was 7.1, and t;.e methyl
orange alkalinity was 35 pom as CaCOn. Dissolved oxygen
values for the various test vessels ranged from 6.7
initially to 5.3 nig/I at the end of the tests.
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RE^LT^
The predicted TLcp values (95?S confidence interval) are
presented in lable 1. T^ble 2 presents a summary of observed
nior-taiity for the bioassay after 24 and 96 hours of exposure. A gela til-r-.-'UE suspension was formed imniediate-y after introduction of the chemical, and various methods of mechanical stirring would not alter the substance.
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r'ior.'c-irii i.K, ]nc.
790 yair: Stre'.-t
Warehafn, .''."a^sach'^se t t-s .Tune, 1973
PREPARED BY i APPROVED BY;
Robert L. Bent ley
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/li^C,.7..-.4
Aquqtic Biologist
Kenneth J. Macek, Ph.D.
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'iaL'le 1 -- A;.:i-,te toxicit.v of 8230 to rainbow trout (^aimo gairdh&rj )
""hese data are based on results '.'1' bioassays c.-oridL.cted at the aquatic toxicology laboratory of Bionomics, Inc.,
Wsreham, Massachusetts.
Corripound
8230
hour96 TL^ - milligram/liter
^vef"
24
hour(rng/1)
>1000
>1000
1000
^ssay conducted at lie (+ 1.0), mean weight of rainbow trout 1.3 g.
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.^';ib]e 2 -- 'oncentrations ol' 8230 tested and corresponding observed
percent mortality for rainbow trout (sa Irnq gairdr.eri) at '< and '-)6 hours du-ing a static hioassay.
C'o'npourid
8Z30
Concentration (nig/I)
1000
750
560
^90
370
280
210
100
-
control control (isopropyi alcohol)
hour96 ^ niortollty observed
24
hour
0
0
0
0
0
0
0 0 0
0
0
0
0
0
0
0
0
0
0
0
<"
Company Sanitized. Does not contain TSCA CBt