Document vBo7KoreqRE0L2r3O9DX20qBq
AR226-3340
o2 \ %
E.l. DUPONT DE NEMOUKb & COMPANY INC.
REPORT NO: /__GL-2001-42 j ____________
C0PY NO'
5
TITLE:
Anuatic Toxicity andjolubilitv off i j j B ^ F liio r o te .lo m e r Intermediate
1 AUTHOR: \ Roland C. Hall, Jr. J
L_
^
^__ >
CONTRIBUTORS: /Thomas V. Robertson, Olver Laboratoriesj
DISTRIBUTION:
ABSTRACT ONLY
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GL-2001-42
J
1
Report Num ber.
C TL-2001-42_j
Issued. December 5, 2001
Technical Report
Aquatic Toxicity and Solubility of.
)nrnfpinmer Intermediate
Report Written By Period Covered Research Notebooks Work Supervised By
n Roland C Hall, Jr
December 2000 to May 2001
NA F KmecT^
'
Abstract
, , , Hn-nphv Olver Labatones to determine the the aquatic
This report,d TM toxicity and solubility or
0Tie, study was conducted in
"component of the spin agent to be used
f the new spin agent in
" " ^ p l a n r w a s subsequently eancded. however,
f t e l l S n m this report was forwarded to the Lme 3 organ,satton to asstst m
meeting their environmental requirements ^
^
Olver Laboratones determined that the solubility S r a p p e a r e d ,0 be the order T^eir screening tests also indicated no acute toxicity at comentr
maximum solubility of 5 mg/L
nressure ^
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Th* report contains confident!,
rif th,
'.rhnipiil Manager.
may be reproduced withou, the approve,
TABLE OF CONTENTS
Introduction Objectives Summary and Conclusions
i Patent Situation Program Publication Status Acknowledgement Signature(s) Appendixes
1 1 1 2 ~i 2 *> 3 4
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G L - 2 0 0 1-42
INTRODUCTION
In
late
2000
addkeeccii,ssiioo. nn.
wwaass
made U
ct~nomevnaalup.anttetothbeespteisnteadgewnat.tob_e______
,
in t h e 0 A llOt Plant Th, P ! ^ n ich lo ro elh v len e Tn order to obtain
FluorSornenntermedi ate and tran
J ^ M ^ f c d o t plant, information w a s ^ --
environmental approval to run t e t e s J' 1 ..g e iu ^ ^ r e w a s noputtisRea^afa available
n eed ed on the a q u a d c t o j g j y ^
therefore a study was
on aquatic toxicity coZ.ss.oned ft ofterUboratonesto
rhe solubility m water and the ho,,ever. fte ~
aquaticto^toit)|fhe test in the pilo P
^ organization to assist m meeting
T ^ S m S i ^ d i i s report was forwarded to the Line i orca
their environmental requirements
OBJECTIVE
The purpose of this ot the study was to deterame Fluorotelomer Intermediate at a maximum cone Cenodaphnia and fathead minnows (Pimephales promel )
SUMMARY AND CONCLUSIONS
t0 near the
conducted ustng an expanded test solulion sen a P o u r e d j S ! l s tndtcated that
small amounts of methanol to .crease solubrl ty T
he
m a m ,,a s not acutely toxic to Cenodaphnia and fa head mmno ^
ha,K ^ 48. hour
at concentrations approaching met ano ai
, than 500 msA . The no
LCso values for Cenodaphnia
observed effect concentration (NOEC) tor th
Fathead Minnow
Reproduction chrome test was 100 m g ^ w htkthe NOECM b r f t e T C 5 ^ ^
S u m val and Growth chronic test w a s / " Z S Z e n c e ^ R n the maximum be no direct acute or chronic toxicity due to the presence o t ^ ^ T
armarent solubility m water of 6 mg/L
PATENT SITUATION
At the present time we have no plans to tile for a patent
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GL-2001-42
PROGRAM
No additional testing is planned at this time
PUBLICATION STATUS
At the present tinte e have no plans to pnbltsh the data conta,ned ,n th.s report
acknow ledgm ents
Thanks to Tom Robertson and Olver Labortones. Incorporated for then conmbonons ,0 this study and report.
1
SIGNATURE(S)
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Company
GL-2001-42
(>
APPENDIX
Appendix A Memo from R Lawrence Hoffman, V ic^ 'residenl, Olver Laboratories to
(Thomas V. Robertsonjdated May 4, 2001 subject p p P P Kr'o~l'u"b,~i'l,i`t"y and' Toxicity
Determination Program, Job Number 60175
'
Appendix B "Determination of solubility and aquatic toxicity of DuPont Product fi^^jpBFIuorotelomer Intermediate for E E DuPont De Nemours and Company by R
j^rwrcnce Hoffman dated May 3, 2001
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OLVER Consulting Engineers Environmental Laboratories
LABORATORIES 1116 South Mam Street Blacksburg, Virginia 24060 May 4, 2001
Mr Thomas V. Robertson) Development Associate Environmental Affairs E.l du Pont de Nemours and Company, Inc
P O Box 27001 Richmond, VA 23261
J ^ 0 R S o Iu b ility and Toxicity "Determination Program, Job
Dear Tom
Enclosed for your review and use are three (3jcopies of the report which describes the performance and results of th e g B B ^ o lu b ility and Toxicity Determination program performed by Olver Laboratories Incorporated for E I du on de Nemours and Company, Incorporated. This program was performed to support evaluations of the potential for the use of this product by examining its potential effects on wastewater toxicity The program, as described in our December 14, 2000 proposa , consisted of an initial determination of solubility in water and subsequent determinations of acute and chronic toxicity to two common freshwater test organisms As for the standard compliance monitoring performed by Olver Laboratories for DuPon , the toxicity testing component of this program is reported in a GLP format
As indicated on the Material Safety Data Sheet provided with the sample, the material appeared to be only slightly soluble in water As described in thajeport, the solubility of the material in water appeared to be in the order of 6 mg/L at standard temperature and pressure. The solubility in water appeared to in c re a ^^^je v e ls o 500 mg/L to 1000 mg/L by adding a small amount of methanol to t h e | l^ ^ | 3Jrninor itnto ,, addition to water For the reasons referenced in the report, the analysis of th
msolutions provided inconsistent results and could not be used to confirm the
concentrations used in the toxicity evaluation component of this program.
Blacksburg, VA (540) 552-6974
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Mr Thomas V. Robertson
"May 4, 2001
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The initial screening tests indicated no acute toxicity at concentration!near the apparent maximum solubility of 6 mg/L. In an effort to determine th e p B g p n c e n tra tions that results in acute and chronic toxicity, acute anachronic testing was conducte using an expanded test solution series prepared u s in g M p m e n d e d with smal amounts of methanol to increase solubility. The results of tfiese tests indicated that M L a s not acutely toxic to Ceriodaphma and fathead minnows (Pimephales J ^ rm la s ) at concentrations approaching methanol-aided solubility limits. The 48-hour l_r values for Ceriodaphnia and fathead minnows was greater than 500 mg/L. Tlne no observed effect concentration (NOEC) for the Three-Brood Ceriodaphnia Survival and Reproduction chronic test was 100 mg/L while the NOEC for the 7-Day Fathead Minnow Survival and Growth chronic test was 500 mg/L These results suggest tha there should be no direct acute or chronic toxicty due to the presence o f g p ^ a t the maximum apparent solubility in water of 6 mg/L
' I look forward to the opportunity to discuss this with you in more detail and to answer any questions that you may have As always, please do not hesitate to contact
me or David Griffiths
Sincerely,
R Lawrence Hoffman Vice President
RLH/egl
Enclosures
cc: David W Griffiths, Ph.D.. President, Olver Laboratories Incorporated
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STUDY TITLE DETERMINATION DFSOLUBIUTY AND AQUATIC TOXICITY OF DuPONT PRODUCT m fjK f^LU O R O T E LO M E R INTERMEDIATE
FOR F I DU PONT DE NEMOURS AND COMPANY
DATA REQUIREMENTS DuPONT CONTRACT ORDER NUMBEf
AUTHOR R. LAWRENCE HOFFMAN STUDY COMPLETED ON
May 3, 2001 PERFORMING LABORATORY OLVER LABORATORIES INCORPORATED ENVIRONMENTAL LABORATORIES
AND CONSULTANTS 1116 SOUTH MAIN STREET BLACKSBURG, VIRGINIA 24060
for '
OLVER LABORATORIES INCORPORATED JOB NUMBER 60175
Comnww
f*AAA AAl A*A<A!n
QgJ
OLVER
LABORATORIES
TABLE OF CONTENTS
REPORT APPROVAL RECORD
QUALITY ASSURANCE STATEMENT
GENERAL INFORMATION . . . .
PROJECT P E R S O N N E L.................
SUMMARY . . INTRODUCTION
METHODS AND MATERIALS
1-41 0 SOLUBILITY DETERMINATION...........
2 0 QUAT1C TOXICITY DETERMINATION
2.1 TEST ORGANISMS .
....................................
2.2 TEST SUBSTANCE . . . : ........................................
2.3 DILUTION WATER .................................................
2.4 TOXICITY TEST PROCEDURES.............................. 2.4.1 GENERAL PROCEDURES.............................. 2.4.2 TOXICITY RANGE-FINDING T E S T S ............. 2.4.3 ACUTE TOXICITY TESTING ....................... 2 4.4 CHRONIC TOXICITY T E S T IN G .....................
2.5 STATISTICAL ANALYSIS..........................................
RESULTS . .
1.0 SOLUBILITY DETERMINATION
2 0 M S h TOXICITY DETERMINATION . . 2.1 TOXICITY RANGE-FINDING . . 2 2 ACUTE TOXICITY TESTING . . . . 2.3 CHRONIC TOXICITY TESTING .
Page Number
h
1
2 3 4 4
4 4
.4 .5 .6
6 .6
8 8 9
10 11 11
12 12 12 14
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OLVER
LABORATORIES
Table 1 Table 2 Table 3
LIST OF TABLES Toxicity Range-Finding Data Summary Acute Toxicity Data Summary . . . .
................. -
13 15
Chronic Toxicity Data Summary - Companson to Standard
Controls . . .
................................................
. 16
Table 4
Chronic Toxicity Data Summary - Comparison to Methanol-
Spiked Controls .............
................................................ 17
APPENDICES
Appendix 1 Material Safety Data Sheet . . . ........................... 18
Appendix 2 P j ^ ^ o l u b i l i t y Determination - Test P r o t o c o l................. i
Appendix 3 ^ J J ^ o lu b ilit y Determination - Analytical D a ta ..................... .
25 27
Appendix 4 Toxicity Range-Finding Test Data . . .
- - . 32
Appendix 5 Acute Toxicity Test Data . . .
....................................... . . 39
Appendix 6 Chronic Toxicity Test Data - Pimephales promelas . . . . . 45
Appendix 7 Chronic Toxicity Test Data - Cenodaphnia dubia . . . . 67
Appendix 8 Acute Reference Toxicity Test D a t a ........................
. 93
Appendix 9 Chronic Reference Toxicity Test D a t a ................................... . 101
Appendix 10 Dilution W ater Quality Analyses D a ta ..................................... 113
Appendix 11 Chemical Analyses of Brine Shrimp and YCT Food Mixtures 122
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OLVER
LABORATORIES
Report Prepared by:
Susan Mirlohi
Date
Bioassay Laboratory Manager
Reviewed and Approved for Issue by
R Lawrence Hoffman Vice President and Study Director
5~j 3 Date
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OLVER
LABORATORIES
n i 1AI ITY ASSURANCE STATEMENT Quality Assurance Statement for final report entitled "Determination of Solubility and Aquatic Toxicity of DuPont P r o d u c t^ |^ B B ^ F lu o r o te lo m e r Intermediate for E I du Pont
de Nemours and Company
Audits for the study were conducted on the dates listed below:
Items Audited Sample Receipt Range-Finding Test Initiation Range-Finding Test Termination Acute Test Initiation Acute Test Termination Chronic Test Initiation Chhomc Test Renewal Chronic Test Termination
Audit Dates 1/ 11/01 1/25/01; 2/01/01 1/27/01; 2/03/01 2/14/01 2/16/01 2/13/01; 2/20/01 2/14/01; 2/21/01 2/20/01; 2/27/01
Date findings reported to management and study director -- 2/27/01-- . The information provided within this report was generated in accordance with Good Laboratory Practice Regulations and Protocols. A final review of all data and records indicate the report submitted is an accurate reflection of the study conducted:
Reported by:
Prian d. Bjoltinghouse
Date
(Duality Assurance Auditor, Olver Laboratories
ii
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OLVER
l a b o r a t o r ie s
Material Tested:
CFNFRAL INFORMATION
Olver Sample Designation:
Study Initiated; Completed:
Experimental Start; End: .
Location of Onginal Raw Data and Final Report:
1/12/01; 5/03/01
. 1/25/01,2/27/01
Olver Laboratones Incorporated 1116 South Main Street Blacksburg, Virginia 24060
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OLVER
LABORATORIES
PROJECT PERSONNEL
The study director of itus project for E. 1, du Pont de Nemours and Company was ^ R . Lawrence Hoffman.J
The following Olver Laboratories personnel assisted with the various phases of the aquatic toxicity determination study
NAME
TITLE
lNIT!ALS
Susan Mirlohi Stacey Boyles Sheryl Newton Laura Dunham Fran Boltinghouse
Bioassay Laboratory Manager Biological Technician Biological Technician Biological Technician Quality Assurance Officer
S.Q1-
5 PW Lml?
i
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OLVER
LABORATORIES
PRODUCT
DETERMINATION OF SOLUBILITY
IMP AQUATIC TOXICITY OF DuPONT P R u OROTELOMER INTERMEDIATE
SUMMARY
Solubilityandaguatic toxicity determination studies were performed for the DuPont
product,
facilitate projections and assessments of the potential for toxicity in
wastewater that'may contain this material. The solubility determination was performed
using a procedure developed by Olver Laboratories based on the substai^^tfprm ation
contained on the Matenal Safety Data Sheet (MSDS) provided by DuPont. Jp P jpo iu bility
in water wag estimated by establishing a calibration curve for GC/MS analysis. The
solubility of B a f f in water was determined to be on the order of 6 mg/L. However, when
introduced as a methanolic solution, it proved possible to produce wha^mpeared to be
homogenous aqueous solutions containing as much as 1,000 mg/L o f ^ is believed
that these are not true solutions, but rather dispersions or micellar solutions
The aiute and chronic toxicity of B H I to Cenodaphnia dubia and fathead minnows
(Pimephales promelas) was assessed utilizing EPA/600/4-90/027F and EPA/600/4-91/002 methods ^ Toj^city testing consisted of initial range-finding tests which included a wide
range o f B B p ncen^rat|ons to establish a general level of toxicity for acute and chronic testing using Cenodaphnia dubia and fathead minnows. Toxicity range-finding tests were followed by 48-hour static acute Cenodaphnia and fathead minnow tests, a three-brood chronic Cenodaphnia dubia test, and a 7-'day chronic static renewal fathead minnow test The concentration series used in the toxicity ram e^nding tests ranged from 0.01 to 1,000 mg/L o f F o r acute toxicity testing,ppjfconcentrations ranged from 5 to 200 mg/L, while chronic testing included concentrations which ranged from 5 to 500 mg/L
Estimated toxicity endpoints (LC5Dand NOEC values) were found to be as follows.
Toxicity Test Type
Toxicity End-points
Cenodaphnia Acute Test
Fathead Minnow Acute Test
Cenodaphnia Chronic Test - Survival Cenodaphnia Chronic Test - Reproduction Fathead Minnow Chronic Test - Survival Fathead Minnow Chronic Test - Growth
LC^ >500 mg/L (100% survival at 500 mg/L) LCjq>500 mg/L (100% survival at 500 mg/L) NOEC = 100 mg/L NOEC = 100 mg/L NOEC = 500 mg/L NOEC = 500 mg/L
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INTRODUCTION
Solubility determination and aquatic toxicity testing for the DuPont p ro d u c t------- ere ngrfnrmpd hv Qlver Laboratones Incorporated for the E.l. du Pont de [Nemours and C o m p a n y W B i l i B i r o m January 12*2001 to February 27, 2001. The5 pyuuirppuoosec of this study w is to detergiiml the solubility o f p m | n water and to determine thiee acute anI d chronic toxicity o f M p o representative freshwater organisms. The toxicity oc f^f lH n v ras assessed through determination of median lethal concentration (LC50) valueess'for acut te testing and no observed effect concentration (NOEC) values for chronic testing, using Ceriodaphnia and fathead minnows.
METHODS AND MATERIALS
1.0 olubiiity Determination
All testing was performed using a sample contained in a 3.63 kg/8 lb can bearing t h e T a b e f : | | ^ H H H H H H I ^ ^ H H j l P Solubility tests were performed according to the test protocol that is provided in Appendix 2.
M2.0 Aquatic Toxicity Determination
The toxicity tests were conducted according to "Methods for Measunng the Acute Toxicity of Effluents to Freshwater and Marine Organisms", EPA/600/4-90/027F and Short-Term Methods for Estimating the Chronic Toxicity of Effluents and Receiving Waters to Freshwater Organisms", EPA/600/4-91/002
The toxicity testing component of this study was conducted following Good Laboratory Practice general testing and reporting guidelines and the final report was reviewed by the , Olver Laboratories Quality Assurance Unit. Copies of the report and original raw data will be maintained by Olver Laboratories. The original signed report and raw data will be archived at Olver Laboratories Incorporated.
2.1 Test Organisms
Ceriodaphnia dubia and fathead minnows, originally obtained from the U.S. EPA and subsequently cultured at Olver Laboratories, were used for acute and chronic testing. Fathead minnow and Ceriodaphnia cultures were maintained in EPA moderately hard water and the culturing records indicated that the test organisms were in satisfactory health at test initiation. Ceriodaphnia cultures were fed a YCT (yeast-cerophyll-trout chow) and algae (Selanastrum capncomutum) food mixture prepared at Olver Laboratories. Fathead minnow cultures were fed brine shnmp nauplii (Artemia sp. eggs obtaineckfrom Ocean
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Star International Inc.", Snowville, VT, Lot No. 4400). Test organisms were fed for at least two hours prior to use in testing.
Larval fathead minnows used in the chronic testing (Olver Culture No. 1810) were 1-24 hours old at test initiation and the control organisms had an average dry weight of 0 429 mg at test completion. The biological loading factor in the controls was 0.02 g . Test organisms were fed 0.1 mL of a concentrated suspension of newly hatched (less than 24 hours old) bnne shrimp nauplii (approximately 700 to 1000 nauplii) 2-3 times daily during testing Larval fathead minnows used in the acute testing (Olver Culture No 180 ) were 3 days old at test initiation. The biological loading factor in the controls was 0 05 g/L with an average weight (not dried) of 2.4 mg at test completion.
The Ceriodaphnia dubia used in the chronic test were obtained from Olver Laboratories cultures produced from EPA-supplied stock. Cenodaphnia used in the chronic testing (Olver Culture Nos. 1-30) were less than 24 hours old, and all within 8 hours of the same age, at test initiation, and the control organisms had an average reproduction of 25.9 (per surviving female) at test completion. Test organisms were fed 0.1 mL of YCT and 0 1 mL of a cobcentrated suspension of algae (approximately 3.1 x 107 cells) once daily at test solution renewal time. Cenodaphnia used in acute toxicity testing were less than 24 hours old at test initiation and they were not fed dunng testing.
The brine shrimp and YCT used in feeding were tested to show that concentrations of metals, pesticides, and PCBs remained within acceptable limits No chemicals were present in the bnne shrimp that made them unsuitable for use as a food source in aquatic toxicity tests. Data for these analyses are included in Appendix 11
Monthly reference tests (Appendices 8 and 9) were performed to ensure that test organism sensitivities and health were within acceptable limits. A sodium chloride reference toxicant (EM Science; CAS #7647-14-5) was used and the results showed fathead minnow and Ceriodaphnia sensitivities to be comparable to ranges previously established at Olver Laboratories.
2.2 Test Substance
A concentrated sample f jjjH p ^ o n ta in e d in aon^gallonsealeqynetal container was provided to Olver LaboratonesTy the D u P o n t [ jH B H H 0 ^ ^ | a c il i t y The MSDS provided with the sample identified the material a ^ U ^ u o r o t e io m e r Intermediate with the following composition:
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Based on the results of th e (B (|s o lu b ility determination, various concentrations of were prepared for use in acute and chronic toxicity testing. The solubility l e v ^ ^ in water was estimated at 6 mg/L, therefore, the theoretical concentrations o f jp P u s e d in initial range-finding toxicity tests were selected at and below the 5 i n s o lu b i l i t y level Since no toxicity was observed at this level, higher concentrations of B d f v e r e prepared for use in the acute and chrome toxicity testing. These rangedfrom 5 to 500 mg/L To enhance the solubility o f p jj^ p in preparing test s o lu tio n s , ((^ v a s initially dissolved in methanol (Burdick & Jackson, High Purity Methanol, CAS #67-56-1) prior to being mixed in dilution water Test solution preparation for the range-finding, acute and chronic t ^ n u i is described in Section 2.4 2 through 2.4.4. In all cases, preparations of the H P standards and test solutions was performed in a manner to minimize loss by volatization to the xtent practical.
2.3 Dilution W ater
The dilution water used for culturing, toxicity testing, and f l t f e s t solution preparation was moderately-hard synthetic freshwater prepared using EPA guidelines (EPA/600/490/027F and EPA 600/4-91/002) This dilution water was aerated prior to testing with oilfree compressed air. pH ranged from 7.7 to 8.0, conductivity ranged from 300 336 /mhos/cm, alkalinity ranged from 60 to 64 mg/L, and hardness ranged from 84 to 100 mg/L. Annual dilution water quality analyses data are provided in Appendix 10.
2.4 Toxicity Test Procedures
2.4 1 General Procedures
The acute and chronic toxicity tests were performed at 25C 1C by placing the test chambers in a constant temperature water bath. Test organisms were exposed to ambient laboratory light (50-100 foot candles, measured at water surface) for a 16-hour day/8-hour night photoperiod. Transitional lighting (30 minutes, 30-40 foot candles) was included at the beginning and end of the 16-hour light period
For the Cenodaphnia dubia acute toxicity tests, plastic beakers filled with 25 mL of test solution were used. For the fathead minnow acute toxicity tests, 600^ mL glass beakers filled with 500 mL of test solution were used. Beaker positions were randomized in the water bath using random numbers. Test organisms were pooled
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and placed (five at a time) into each test solution in a random order. Test organisms were less than 24 hours old for the Ceriodaphnta acute tests and within 1 to 14 days old and within 24 hours of age for the fathead minnow acute tests.
Routine chemical analyses were cond^ted. Alkalinity and hardness were measured in the control and h ig h e s tU B p te s t concentrations at test initiation. Conductivity, was measured in all test concentrations at test initiation and termination. Dissolved oxygen, pH, and temperature were measured daily in one replicate per effluent concentration. All chemical analyses were conducted as per the EPA document "Methods for Chemical Analysis of Water and Wastes (EPA 600/4-79-020) or APHA, "Standard Methods for the Examination of Water and Wastewater", 18th Edition. Dissolved oxygen was determined by electrode EPA Method 360.1.
PARAMETER ` PH
Temperature Dissolved Oxygen
Conductivity Alkalinity Hardness
TEST METHOD EPA 1501 EPA 170 1 EPA 360 1 EPA 120 1 EPA 310 1 EPA 130 2
TEST SOLUTIONS ANALYZED
FREQUENCY
All Daily
All Daily
All Daily
All . Beginning/End
Control and Highest Concentration
Beginning
Control and Highest Concentration
Beginning
For the Ceriodaphnia chronic test, 30 mL plastic beakers filled with 15 mL of test solution were used. Beaker positions were randomized in a holding tray using random numbers. One Ceriodaphnia neonate (20-24 hours old) was placed in each of ten replicate test chambers per test solution using the assigned positions All test chambers, contained in their holding trays, were placed in the water bath. The number of surviving Cenodaphnia in each test concentration was determined prior to test solution renewal. Dead Cenodaphnia were discarded. Test solutions were renewed daily by transferring each of the original Cenodaphnia into freshly, prepared t Q d ^ t e s t solutions. The number of Ceriodaphnia neonates, reproduced by the adult female Ceriodaphnia in each replicate test chamber, was counted and recorded at each daily test solution renewal time
In the chronic test, Cenodaphnia were fed 0.1 mL of a concentrated suspension (approximately 3.1 x 107cells) of algae and 0.1 mLofYCT food mixturg daily, attest solution renewal time. Cenodaphnia were exposed to ambient laboratory light (50-
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100 foot candles, measured at water surface) for a 16-hour day/8` h ^ photoperiod with transitional lighting Transitional lighting (30 minutes, 30-40 foot candles) was Included at the beginning and end of the 16-hour hght pe^no _ Temperature was maintained at 25C 1C by placing the tes c
constant temperature water bath.
For the fathead minnow chronic test, beakers (glass; 600 m L )filled ^ 2| ^ ,f
test solution were used. Ten fathead minnow larvae, 1-20 hours old,
placed
in each of four replicate test chambers per test solution using random test chambers were positioned in the water bath using randomization techrnques The number of surviving larvae in each chamber was determined p n o jo test solution renewal. Dead larvae were discarded. Test solutions were renewed daily by siphoning approximately 80% of the test solution out o f t t e chamber lhe original test volume was restored by adding freshly p re p a re d ^ !s o lu tio n s to tne
test chambers.
2.4.2 Toxicity Ranae-Findina Tests
th e initial phase of testing consisjed o j a series of 48-hour range-finding tests to determine the general toxicity of f i ^ v e r a wide range of te s tc ^ e n tra tio n s Targeted test solutions ranged from 0.01 mg/L to 1,000 mg/L o f^ ^ H p
the results of t h e f jjf t o lu b ilit y determination, an initial concentration se oe^/as selected to perform the toxicity range-finding tests. Since the solubility water was estimated at 6 mg/L, the initial toxicity range-finding tests were performed using a dilution series consisting of control, 0.01 mg/L, 0.1 mg/L, 1 mg , an 5 mg/L of f M B Since no evidence of toxicity was observed at these levelM he dilution senes was expanded to include targetoilO O mg/L^^TPOO mg/ | concentrations. To enhance the solubility o f { 0 p f n water, p a u s e d to prepare test concentrations greater than 6 mg/L was initially mixed with 500 A. ot reagen grade methanol; this mixture was then added to moderately hard water to prepare
the test solutions.
2.4.3 Acute Toxicity Testing
The second phase of testing involved the performance of 48-hour static acute Cenodaphnia dubia and fathead minnow tests. Based on the results of the toxicity range-finding tests, a concentration serjgs consisting of control, 200 mg/U 300 mg/L, 400 mg/L, and 500 mg/L o 0 t N a s used. The highest t a r a e t e d f ^ ^ concentration used in testing was at 500rng/L since, above 500 m g /L ,^ |^ p ii no appear to remain in solution. At concentrations greater than 500 mg/L sma droplets o fJ M fc v e re observed adhenng to the glassware used to prepare the test solutions. Ar^dditional control solution consisting of 500 A. methanol/L of dilution water was included in testing to identify any potential toxicity associated with the presence of methanol in solution. Based on the available toxicity data on met ano
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(EPA documents: EPA-600/6-91/005 and EPA/600/6-91/003), the concentration of methanol in the test solutions (0 05%) was well below the expected toxic levels (i.e., 2% to 5% for acute toxicity and 0 3% to 0 5% for chronic toxicity)
B test solutions were prepared by first dissolving the pre-measured volume of concentrate in 500 u Lj A m&thanol pnor to mixing in the dilution water The measured concentrations o iQ ^ P jn test solutions were based on a specific gravity of 1.4 as noted on the m atenal^gM ^ data sheet provided with the sample The acute test dilution series and 9 N v est solution preparations are summarized below.
Test Solution (m g /lfp l
Control Control with Methanol
200 300 400 500
Volume o | J J /1 0 0 0 mL DilutSnWater None None 142 A213 L 284 fiL 355 A
2.4.4 Chronic Toxicity Testing
The third phase of testing involved the performance of the static renewal Ceriodaphnia dubia and fathead minnow tests. Based on the results of the acute toxicity tests, a dilution senes consisting o fc o n to l, 5 mg/L, 10 mg/L, 25 mg/L, 50
mg/L, 100 mg/L, and 500 mg/L of targeted5 ^P concen*:ra^Gns were used for the chronic testing An additional control solution consisting of 500 A- of methanol/L of dilution water was included in testing to serve as a second control for determinations of potential toxicity associated with the p re s e n c ^f methanol in test solutions Methanol was used as a solvent medium fo n B iB p n o r to mixing of S l V w i t h dilution water and preparation o f test solutions.
Test solutions were prepared at test initiation and daily chronic test solution
renewals. A 100 mg/L stock
usedto prepare the 5 mg/L,
10 mg/L, 25 mg/L, and 50 m g / L ^ U ^ e s t solutions, j p ^ f t t o c k solutions were
measured volumetrically, dissolved in 500 fA. of pure methanol, and added to
premeasured volumes of dilution water. The solutions were gently mixed in a
separatory funnel prior to use.
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Test Concentration Control
Control with Methanol 5 10 25 50
100 500
Volume o fl^ R lO O O mL dilution water None None
5 mL of 100 m g /U fc ^ o lu tio n 10 mL of 100 m gAJB B P solution 25 mL of 100 m g /L |s o lu tio n * 50 mL of 100 m g / L ^ d solution
71 p L 355 p L
2.5 Statistical Analysis
In light of the analytical difficulties p r e s e n te ^ D ^ B jJ I all statistical analyses of acute and chronic test data were based on ta rg e te d (U p te s t concentrations.
Insufficient mortalities occurred in the acute toxicity tests to calculate an LCX. Mortality per test concentration was reported, and the LC ^ values were approximated based on the highest test solution used.
Statistical analysis procedures described in EPA/600/4-91/002 were used with Toxstat Version 3.5 to perform statistical analyses for the Ceriodaphnia and fathead minnow chronic tests. For the Cenodaphnia chronic test, survival was analyzed first using Fisher's Exact Test. Normality of distnbution and homogeneity of vanance for the reproduction data were next checked with the Shapiro Wilk's or Chi-Square Tests and Bartlett's Test, respectively. ANOVA and Dunnett's Test or Steel's Many-One Rank Test were used to evaluate reproduction. Any Cenodaphnia test replicates identified as males were excluded from the reproduction data analyses as per EPA guidelines.
For the fathead minnow chronic test, data were transformed using the arc sine [square root
(y)] transformation. Survival was analyzed first. Normality of distnbution and homogeneity
of variance were next checked with Shapiro-Wilks and Bartlett's Test, respectively
ANOVA and Dunnett's Test or Steel's Many-One Rank Test were used to evaluate
mortality and growth. If any test concentrations showed statistically significant mortalities,
they were excluded from the growth data analyses For statistical analyses of growth data,
average growth of the organisms was based on the onginai number of larvae, as per EPA
method guidelines.
s-
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Two sets of data analyses were perform e^or the chronic toxicity tests. Test organism survival and reproduction or growth in th e M ((p e s t solutions were statistically compared to both the standard control group (with no added methanol) and the methanol control group.
RESULTS
Attempts to determine the water solubility o
approach given in the test
protocol that is included in Appendix 2. In t
as received from DuPont -
was equilibrated with deionized water in a separato^^anel. After phase separation, an
aliquot of the aqueous phase was analyzed for B P ^ c o n te n t by purge and trap gas
chromatographic/mass spectrometric (GC/MS) techniques.
The analytical system used for all determinations consisted of a Tekmar Model 3000 purge and trap concentrator interfaced to a Hewlett Packard Model 58^^G C , and a VG Trio I mass spectrometer Calibration ^ n d a rd s consisted of samples o f B H p in Moratory pure deionised water c o n ta in in g iB ^ concentrations of 80, 40, 20, 8.474 2, and 2.1 g/L. The standards were prepared by cauefullv adding to 25.0 mL of water appropriate quantities of a stock^solujjpn c o n ta in m g p B j^ t a concentration of 40 g/mL in methanol. To minimize loss o n p B R y evaporation, the standards were prepared in purge and trap test tubes which were secured to the Tekmar purge and trap unit immediately after
preparation.
Based on the chromatographic results obtained during calibration, H a p p e a re d to consist of a mixture of three poorly resolved constituents eluting witivci retention time of between 4.0 and 4.1 minutes. Mass spectra for each o f the constituents were virtually identical in that they exhibited prominent peaks, in decreasing order of intensity, at mass to charge ratios of 77 (100% intensity), 51 (26% intensity), and 69 (14% intensity) Raw data illustrating a typical chromatogram and mass spectrum are included in Appendix 3 Also included in Appendix 3 is the derived calibration curve, which proved to be linear with
a coefficient of determination of 0.991.
Samples of^ B J ^ a t u rated water were analyzed fo r^ P B ^ io n te n t on 11 separate occasions, over the course of three separate days. Eaclymn was preceded by the analysis of a mid-point calibration standard containing ( f l B at a concentration of 0.040 mg/L. Recoveries of the standard ranged from a low of 0.037 mg/L to a high of 0.052 mg/L, and averaged 0.046 mg/L (115% of theory).
For reason that are not immediately obvious, the results for thp^pBPsaturated water solutions proved to be poorly reproducible, ranging from a minimum value of 1.15 mg/L to a maximum of 16.7 mg/L. For the entire set of 11 determinations, the average was found
to be 6.14 mg/L, with a standard deviation of 5.33 mg/L.
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It is equally puzzling to note that the chromatogram obtained for th d jP js a iu ra te d water solutions was different from that obtained during the analysis of theTalibration standards Whereas th e J fc e a k had onginally appeared as a poorly resolved triplet the peak for the saturated water solutions took on the appearance of a well-resolved doublet, with one peak eluting at a retention time of approximately 3 6 minutes, and the second with a retention time of 4 1 minutes. Again, mass spectra for the peaks were virtually identical
Although it amounts to little more than speculation, possible explanations for the observed behav'ior of in water .in...c..l.u..d..e...t..h..e...f.o..l.lowing:
1. f l B r l a y possess sufficient surface activity to form micellar solutions If so,___ _ m a ^e n d to form monomolecular layers at the air/water interface and/or at the water/glass interface, making it difficult to withdraw representative samples from the bulk "solutions" for analysis.
2. _ nay be sufficiently reactive to undergo degradation (or polymenzation) in the Feafed inlet of the gas chromatograph. If this were the case, it would not be surprising to see multiple peaks of vanable intensity.
3 ' Focusing finally on the different peak patterns, and noting that the standards (which appeared as triplets) were analyzed immediately after preparation, whereas the
4B M 0saturated water samples (which appeared as well-res^/^Ldoublets) had ^ 2cTfor up to several days prior to analysis, it may be t h a t m ^ i s undergoing some unspecified sort of time dependent chemical transformation when allowed to equilibrate with water.
Despite the unusual properties exhibited b y H p n water, it can be concluded with a high degree of certainty that its solubility is extremely low, most likely on the order of 10 mg/L or less.,
2.0 i^ ^ ^ P 'o x ic ity Determination
2.1 Toxicity Range-Finding
All data generated for the toxicity range-finding tests are included in Appendix 4.
The results indicated no acute toxicity to fathead minnows and Cenodaphnia at
targeted
concentrations ranging from 10 mg/L to 1,000 mg/L ( ^ L ^ ^
concentration may be less than 1,000 mg/L due to apparent accumulation
on glassware) Toxicity data for these tests are summarized in Table 1
2.2 Acute Toxicity Testing
All data generated for the acute toxicity tests are included in Appendix 5 The results indicated no acute toxicity to fathead minnows and Cenodaphnia a1|
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TABLE 1 TOXICITY RANGE-FINDING DATA SUMMARY
Test Concentration*1'
(m g /L ^ H Control*2'
0 01 0.1 10 ........ 5 0 100 1,000*3> Toxicity End-Point*'1'
Percent Survival
Cenodaphnia
24-Hour
48-Hour
100 100
100 100
100 100
100 100
100 100
Fathead Minnow
24-Hour
48-Hour
100 100
100 TOO
100 100
100 100
100 100
100 100 100 100 100 100 100 100
LCkj >1,000 mg/L
LCso >1,000 mg/L
Notes
1 Targeted test concentrations.
2. Control consisted of EPA m oderately hard water and contained n o p | j |
3 Actual^BBPconcentration may be less than 1,000 mg/L based on appearance of
f-esidual on glassware used to prepare test solution.
.
4. LC50 values estim ated based on test organism response in highest targeted test solution.
Job Number 60175 April 20, 2001
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Q j r p>
laboratories
concentrations ranging from 200 mg/L to 500 mg/L. The sur/ival of Cenodaphnta in the methanoi co n tro ^'0% survival) was reduced relative to the standard control (100% survival) ^ndp^QJ^test solutions (90% - 100% survival). No reason for this reduction in survival was identified. The results are summarized in T a b le ^ ^ ^ ^ _ depicted, the LCH values for both tests were estimated based on the h i g h e s t f ^ ^ test solution used and are reported as greater than (>) 500 mg/L.
2.3 Chronic Toxicity Testing
^
All data generated for the chronic toxicity tests are included in Appendices 6 and 7 and the test results are summarized in Tables 3 and 4. Statisticall^^^^iead minnow survival and growth were not significantly reduced by exposure to ^ ^ B te s t concentrations ranging from 5 to 500 mg/L. This was consistent for comparisons to standard laboratory water (no methanol) controls as well as comparisons to control water spiked with 500 iA. methanol. The no observed effect concentration (NOEC) value for this test Was based on the highest test concentration used and is reported as NOEC = 500 mg/L. No unusual behavior was observed by control larvae in the dilution water controls and dilution water with methanol controls. i
jn t h ^Ceriodaphnia chronic test, survival was significantly reduced in the 500 mg/L J jjB s o n c e n tra tio n (40% survival) Ceriodaphnia survival and reproduction data were statistically analyzed by comparing the survival and reproduction in each test concentration to the standard control group (with no methanol added) (Table 3) and to the methanol control group (Table 4)^A^tetistically significant reduction in reproduction was observed at the 25 mg/LJ ^ J p e s t concentration when the data were compared to the standard control group, resulting in a non-continuous dosedependent toxicity response In accordance with standard EPA chronic test data evaluationprocedures, the NOEC value for this test may be defined as 10 mg/L, the h ig h e s ^jH c o n c e n tra tio n under the lowest statistically significant concentration (25 mg/L). Alternatively, test organism reproduction at the 25 mg/L concentration may be considered aberrant and the NOEC may be defined as 100 mg/L, based on improved reproduction (relative to the 25 mg/L concentration) in the 50 mg/L and 100 mg/L test concentrations The reproduction data analyses s t a j ^ n o statistically significant reduction in reproduction in the 100 mg/L and low ei^B JP est concentrations when the data were compared to the methanol-spiked control group (Table 4). The NOEC value for the test when compared to the methanol-spiked
control was 100 mg/L.
In light of test organism reproduction reproduction in the 5 mg/L, 10 mg/L, 50 mg/L, and 100 mg/L test concentrations, the NOEC for Ceriodaphnia is believed to be 100 mg/L.
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TABLE 2 ACUTE TOXICITY DATA SUMMARY
Test Concentrati^1
Control121 Control wtth MethanolP)
200
300
400 ______ __L------ -----
5,00 Toxicity End-
Point*41
Percent Survival
Cenodaphma
24-Hour
48-Hour
100 100
100 70
Fathead Minnow
24-Hour
48-Hour
95 95 100 100
100 100 100 100 LCjo >500 mg/L
95 100 90 95 LCm >500 mg/L
100 100 100 100 LC50 >500 mg/L
100 100 100 . 100 LC-*, >500 mg/L
Notes.
1. Targeted test concentrations.
2. Control consisted of EPA moderately hard water and contained n o p j j |
3. Control consisted of EPA moderately hard water and contained 500 (A. methanol/L and
4. LCsqvalues estimated based on test organism response in highest targeted test solution.
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la b o r a to r ie s
TABLE 3
Test C o n c e n ta to ^ 1'
(m g /L ^9
Control*2'
5
10
. 25 50
100 i
500
Toxicity End Points
CHRONIC TOXICITY DATA SUMMARY COMPARISON TO STANDARD CONTROLS
Toxicity Test Results
Cenodaphma
Fathead Minnow
Percent Survival 100
Average Reproduction 18 0
Percent Survival 98
Average Growth (mg)
0 420
100
16 6
98 0 468
90
17 1
95 0 416
90 13.9-P) 95 0.430
70 . 152
100 0.442
70 172 100 0.399-
40*ct
NAW
98 0.422
NOEC - Survival = 100 mg/L NOEC - Reproduction = 100 mg/L*5) IC2S- Reproduction >500 mg/L(6)
NOEC - Survival = 500 mg/L NOEC - Growth = 500 mg/L IC25- Growth >500 mg/L|5)
Notes-
1. Targeted test concentrations.
2. Control consisted of EPA moderately hard water and contained
3. Asterisks (*) indicates a statistically significant reduction in survival and/or reproduction
as compared to the control group.
4. Not Applicable. Since test organism survival at this concentration was significantly reduced relative to the control group, reproduction data was not included in the reproduction analysis.
5. Reduction test organism reproduction at the 25 mg/L concentration considered abberant. NOEC reproduction value based on test organism reproduction in 100 mg/L concentration.
6. IC25values estimated based on test organism response in highest targeted test solution.
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TABLE 4
CHRONIC TOXICITY DATA SUMMARY COMPARISON TO METHANOL-SPIKED CONTROLS
Toxicity Test Results
Test Concentetia^'
i m a* /1L W^ --Control with Methanol
5
10
25
Cenodaphnia
Percent Survival 90
Average Reproduction 14 3
100 16 6 90 17 1 90 13 9 70 15 2
oin
100 70 500 40*(3)
172 NAW
Toxicity End Points
NO EC - Survival = 100 mg/L NOEC - Reproduction = 100 mg/L IC,5- Reproduction >500 mg/Lt5>
Fathead t/linnow
Survival
Average Growth (mg)
95 0 407
98 0.468 95 0.416 95 0 430 100 0 442' 100 0 399 98 0 422
NOEC - Survival = 500 mg/L NOEC - Growth = 500 mg/L IC,5- Growth >500 mg/L
Notes:
1 . Targeted test concentrations.
2. Control i n sisted of EPA moderately hard water and contained 500 A. methanol/L and
nom m
'
Asterisks (*) indicates a statistically significant reduction in survival and/or reproduction as compared to the control group.
4. Not Applicable. Since test organism survival at this concentration was significantly reduced relative to the control group, reproduction data was not included in the reproduction analysis.
5. IC25values estimated based on test organism response in highest targeted test solution.
Job Number 60175 May 3, 2001
17 Company Sanitized. Does not contain TSCA CB1
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Ji
APPENDIX 1 MATERIAL SAFETY DATA SHEET
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T iie MSDS format adheres to the standards and regulatory r e q u i r e m e n t s * of the United States and may not meet regulatory requirements
in other countries.
DuPont Material Safety Data Sheet
Page 1
DU004S04
IFLUOROTELOMER INTERMEDIATE Ivisad 12-JAN-1999
CHEMICAL PRODUCT/COMPANY IDENTIFICATION
Material Identification M is a registered trademark of DuPont.
Company Identification
MANUFACTURER/DISTRIBUTOR
DuPont 1007 Market Street Wilmington, DE 19898
piONE NUMBERS , Product Information
Transport Emergency Medical Emergency
: 1-800-441-7515 : CHEMTREC 1-800-424-9300 : 1-B00-441-3637
HAZARDS IDENTIFICATION Potential Health Effects
Eye contact may cause eye irritation with discomfort, tearing or blurring of vision.
Based on related products, inhalation of spray or mist may cause ^ nasal, throat, or dung irritation. Inhalation of large amounts of respirable particles may be toxic to the lungs. Symptoms may be modest initially, followed in hours b y severe shortness of hreath requiring prompt medical attention. Carcinogenicity Information None of the components present in this material at concentrations ^ equal to or greater than 0 .1% are listed by IARC, NTP, OSKA or ASGIH as a carcinogen.
19
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DU004604
DuPont M a te r ia l S a fe ty D a ta S h e e t
Page
2
yyjtST AID MEASURES
First Aid
INHALATION
If inhaled, remove to fresh artificial respiration. If
air. If not breathing, breathing is difficult.
give give
oxygen
Call a physician.
SKIN CONTACT
Flush skin with water after contact. before reuse.
Wash contaminated clothing
EXE CONTACT
In case of contact, immediately flush^eyes with plenty of water for at least 15 minutes. Call a physician.
INGESTION
If of
swallowed, do water. Never
not induce vomiting. Immediately gave 2 give anything by mouth to an unconscious
glasses person.
Call a physician.
Notes to Physicians
Activated charcoal mixture may be administered. To prepare
,
activated charcoal mixture, suspend 50 grams activated charcoal m
400 mL water and mix thoroughly. Administer 5 mL/kg, or 3
for an average adult.
-Y33BHS" "FIGHTING M E A S U R E S
________
Flammable Properties
Flash Point Method
: Does not ignite = PMCC
Hazardous decomposition products including carbon dioxide, carbon monoxide, hydrogen fluoride, toxic gases or particles may be formed during combustion. These products may cause severe eye, nose, throat, and lung irritation or toxic effects.
Extinguishing Media Water Spray, Foam, Dry- Chemical, C 02.
Fire Fighting Instructions
Wear self-contained breathing apparatus. Wear full protective., equipment.
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DU004604
DuPont Material Safety Data Sheet
(FIRS FIGHTING MEASURES - Continued)
Avoid breathing decomposition products
Page
3
ACCIDENTAL RELEASE MEASURES
_ ______ ;________
S a f e g u a r d s (Personnel)
NOTE: Review FIRE FIGHTING MEASURES and HANDLING (PERSONNEL) sections before proceeding with, clean-up. Use approprxa e PERSONAL PROTECTIVE EQUIPMENT during clean-up.
Spill Clean Up SoaX up with sawdust, sand, oil dry or other absorbent material.. Shovel or sweep up.
Accidental Release Measures
Flush spill area with water.
_ _______________________________________________________
handling and storage
_ _ _ ________________
Handling (Personnel)
Avoid contact with eyes. Wash thoroughly after handling. Do not store or consume food, drink, or tobacco in areas where they may become contaminated with this material. Avoid circumstances a produce respirable particles unless suitable ventilation and respirator are used.
Storage
-"Keep container tightly closed.
Keep away from open flames and heated surfaces above 20 0 degrees C (392 deg F) .
e x p o s u r e c o n t r o l s /p e r s o n a l p r o t e c t i o n
____ ______
Engineering Controls
Keep container tightly closed. Use only with adequate ventilation Vent heated extruder or dryer fumes outside work area. Do not aerosolize. In spray applications, use airless type pressure spray equipment at less than SO psi, and exhaust ducts, drxp pans, m r other design features to minimize worker exposure to m a t s and overspray.
Keep away from open flames and heated surfaces above 20 0 degC (392 degF).
21 Company Sanitized. Does not contain TSCA CBI
DU0Q46Q4
DuPont M a te r ia l S a fe ty D a ta S heet
Page
(EXPOSURE CONTROLS/PERSONAE PROTECTION - Continued)
4
Personal Protective Equipment EYE/FACE PROTECTION Wear safety galsses or coverall chemical splash goggles.
RESPIRATORS Wear NIOSH approved respiratory protection as appropriate.
PROTECTIVE CLOTHING
Where there is potential for skin contact have available and wear: as appropriate, impervious gloves, apron, pants. and jachat -
Exposure Guidelines
Applicable Exposure Limits Perfluorobutyle thylene PEL (OSHA) TLV (ACGIH) kEL *(DuPont)
: None Established : None Established : 100 ppm, B Hr. TWA
* AEL is DuPont's Acceptable Exposure Limit. Where govemmentally imposed occupational exposure limits which are lower than the are in effect, such limits shall take precedence.
Exposure G u i d e l i n e Comm e n t s
No AEL has been established for this product. Other products with fluorinated material components have an AEL of 0.1 mg/3 to 1 mg/m3 (8 hour TWA) for respirable size
aerosol particles.
Air monitoring studies conducted at customer sites indicates tbat the use of the recommended low pressure (less than 60 psi) airless type, garden type or deck_ specific hand pump sprayer with spray tip orifice minimum of 0-031 inches in diameter does not produce respirable size aerosol particle concentrations near the AEL.
"
PHYSICAL AND CHEMICAL PROPERTIES
Physical Data
Boiling Point % Volatiles Solubility in Water Odor Form Color Specific Gravity
58 C (136 F) 0 7S O m m Hg
100 WT^s
Negligible Ethereal
Liquid, Clear Colorless
1.4
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DUO04604
DuPont M a te r ia l S a fe ty D a ta S h e e t
Page
5
STABILITY AND REACTIVITY
Chemical Stability
Stable at normal temperatures and storage conditions.
Incompatibility with Other Materials
None reasonably foreseeable.
Decomposition
Hazardous decomposition products including carbon dioxide, carbon monoxide, hydrogen fluoride, toxic gases or particles may be formed during combustion. These products may cause Bevere eye, nose, throat, and lung irritation or toxic effects.
Polymerization
Homopolymerizati'on will not occur. Copolymerization can occur in the presence of free radical sources, heat or UV light.
TOXICOLOGICAL INFORMATION
Animal Data
Inhalation 1 hour ALC: Oral LD5Q:
>7,178 ppm in mice >25,000 mg/kg in rats
The product is not a skin irritant, is a mild eye irritant, and is untested for skin sensitization in anima ls. Repeated exposure to high levels (5 vol^) produced blood changes (decreased -platelets and increased monocyte) . Tests in animals demonstrate no developmental toxicity. The product does not produce genetic damage in bacterial cell cultures but has not been tested in animals. Tests for carcinogenic and reproductive activity have not been performed.
DISPOSAL CONSIDERATIONS
Waste Disposal
"
Treatment, storage, transportation, and disposal must be in accordance with applicable Federal, State/Provincial, and Local regulations.
23
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DUO 04 604
D uP ont M a te r ia l S a fe ty D a ta S heet
Page
6
TRANSPORTATION INFORMATION
_
Shipping Information Not R e g u l a t e d as a hazardous m a t e r i a l by DOT, IMO, or IATA
REGULATORY INFORMATION
U .S . F e d e r a l R e g u l a t i o n s
TSCA Inventory Status : Reported/Included.
TITLE III HAZARD CLASSIFICATIONS SECTIONS 311, 312
Acute
: Yes
Chronic
: No
Fire
: No
Reactivity : No
Pressure : No
l ____ _______ _ ______________________
OTHER INFORMATION
NFPA, NPCA-HMIS
NFCA-HMIS Rating Health Flammability Reactivity
:1 :0 :0
Personal Protection rating to be supplied by user depending on use conditions.
The d a t a in this M a t e r i a l S a f e t y Data Sheet relates only to the^ specific material designated herein and does not relate to use in combination with any other material or in any process.
Responsibility for MSDS : MSDS Coordinator
_
Address
: DuPont Chemical Solutions Enterprise
' Wilmington, De. 19838
Telephone
: 800--441--7515
# Indicates updated section.
T h i s i n f o r m a t i o n is b a s e d u p o n t e c h n i c a l i n f o r m a t i o n b e l i e v e d to b e reliable. It is s u b j e c t to r e v i s i o n as a d d i t i o n a l k n o w l e d g e and. experience is gained.
End of MSDS
24 Company Sanitized. Does not contain TSCA CBI
APPENDIX 2
SOLUBILITY DETERMINATION M TEST PROTOCOL
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laboratories
Test Protocol for Determining, the Solubility of
in Water
1 Obtain sample of authentic product from DuPont. No more than 100 mL should be required
2 Calibrate the GC/MS system using samples of the authentic product. At the same time, determine a R R F J o n fliP n relation to an internal standard having a retention time similar to that o f H ^ s m c e f lM B is claimed to exhibit negligible solubility in water, prepare calibration standards b^nssolving carefully weighed quantities of the product as received in a suitable solvent Methanol is suggested. The calibration curve should be constructed using a minimum of four, and preferably five, calibration standards
3 Equilibrate] with laboratory pure water as follows
a Place approximately 25 mL of the product as received in a clean 2L separatory funnel.
Add 1L of laboratory pure water
c Shake vigorously to intimately mix the two phases, venting to atmosphere as needed to relieve pressure Allow the phases to separate, then repeat both steps a minimum of five (5) times
d After mixing, allow the funnel and its contents to stand undisturbed overnight (to ensure complete phase separation)
e Remove a portion of the aqueous phase (upper phase) using a clean transfer pipet Place the sample in a 40 mL VOA vna^^iuipped with a Teflon-lined cap Makeihe transfer quickly to avoid loss o tflH ^ to the atmosphere When full, seal the vial with its cap such that zero haraspace exists after the cap is secured
Prepare three such vials for subsequent analysis
f After removing analytical samples, measure and record, i) temperature of the aqueous phase, and n) atmospheric pressure
4 Analyze all three samples for the presence
Quantify concentration in units of
mg/L relative to the calibration curve and RRF, as determined in Step 2
Safety Considerations
The toxicity o f ^ J H although not believed to be high, has not been well-defined All prepara tive steps should tKe place in a hood Standard and customary measures should be taken to guard against skin and eye contact. Should contact occur, follow the procedures outlined in the attached MSDS
?c C o m p a n y Sanitized. D o e s not contain TSCA C B
APPENDIX 3
SOLUBILITY DETERMINATION ANALYTICAL DATA
27 Company Sanitized. Does not contain TSCA CB1
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LABORATORIES
File
. c \V 012 201 ',700122 02
Operator Acauired
: BP : 22 JAN 1 9 .02
Instrument
Trio-1
Sample Namme: 1000 NG STD
Mise Info : 25mls
Vial Number : 0
D
using
Abundance
110000
TIC V 0012202.D
C u r A i o&?a h
/CETUt r"
(jT riP K iT Y J
ov
Tim e-> 3 00
3 20
P
3 40
II --
3 6 0 3 BO
............1' I '----!,T-.-TTT| I n i -r
4 00 4 20 4 40 4 60 4 80 5 00
r-r-i-- -i--1I 111r 1' ` ' I
5 20 5 40 5 60
5 80 6 00
4,bun0ance
Scan 49 0 (4 083 min) V0012202 0
77
25000
20000
15000
10000
50001
69
t i/z - >
44 :
o ' l ' : i I i ' 30 40 50
57 100
. I ,108
, : i'l 'l - r - l - M-p ----- ,-------1 i----- 1 * j-i 6 0 70 BO 9 0 10 0 11 0
157 __
181
207
I_, I,119 127
145 I !6 3
i--,*----r-4,------ n ----- r - 1, . j I . | .`i-nj - ----- T ----- I- ' P r P ~
120 130 140 150 160 170 180 190-- 200-- 210_
28 Company Sanitized. Does not contain TSCA CBi
Response Rateo 14-
12-
10-J
J
6-
/
~' " I
'
2 Amount Ratio
Resp Ratio = 3.49e+000 * Amt + 1.33e+000 Coef of Det (r*2) = 0.991 Curve Fit: Linear
Method Name: C :\V012 5 0 1 ^ ^ B 2 .M
"
Calibration Table Last Updated: Wed Jan 24 07:52:06 2
Company Sanitized. Does not contain TSCA CBI
29
Fils Operator Acquired Instrument Sample Name Misc Info Vial Number
C : \ HFCKEM\1 \DATA\VO 119 C1 \VO C119 0 3 . D
BP 1.9 JAN 1 1 3 :4 5
u s in g AcqMethcd
TriQ25 ML 2 5m ls 0
H20 EXTRACT
^ oloV ^ O f
30 Company Sanitized. Does not contain TSCA CB1
File Operator Acquired Instrument Sample Name Mise Info Vial Number
C .\H?CHEM\1\DATA\VO 1 1 901\VO 0119 Q8.D
EP 19 JAN 1 13:45
using AcqMethod
Tr 25 ML
H20 EXTRACT
25mls 0
Scan 498 (4 15 0 min) V 0 0 1 1908 D
fjh iS n e u H oF 1
m /z- >
CD O O
207
108 131
157 181
93 t ,
145
U'' I " " l .... 1 " ' I` 1A'-''T11 "I" ''' ,- r - 4' IT-'X' ' I . ' " I'1--I-P'P'" ' , I 1-6'I9' '
227
1' 8` 8I 1191'5
219
` JU 1' :
30 40 5 0 60 70 80 90 1C0 110 120 130 140 150 160 170 18 0 190 2 0 0 210 220 2 j 0
31 Company Sanitized. Does not contain TSCA CBI
I
APPENDIX 4 TOXICITY RANGE-FINDING TEST DATA
32
Company Sanitized. Does not contain TSCA CB1
OLVER
LABORATORIES
I K
Company Sanitized. Does not contain TSCA CB!
OLVER LABORATORIES INCORPORATED ENVIRONMENTAL BIOLOGY LABORATORY
TEST SUMMARY SHEET
CLIENT TOXICANT/EFFLUENT
JOB NO
on S
PERMIT NO
v/A
PAGE I OF l
TP C T DATC"^
ACUTE TOXICITY TEST RESULTS Cenodaphma l/z5 - | / z . l) o 1
Fathead Minnow
1/2._
Id
CHRONIC IO X IC IIY T EST RESULTS Cenodaphma
Fathead Minnow
TFRT CONDITIONS TEST ORGANISM AGE DILUTION WATER SOURCE AERATION
aJ
TEST ACCEPTABILITY CONTROL SURVIVAL (a90%)
F P A -M H W
OLVER LABS conlinuous
loo/.
2. J ams EPA-MHW Ol VER LABS conlinuous
Io n /
TEST ORGANISM AGE DILUTION WATER
SOURCE AERATION
CONTROL SURVIVAL (80%) NO OF CONTROL FEMALES
% CONTROL FEMALES WITH 3 BROODS (60%)
EPA-MHW OLVER LABS
continuous
EPA-MHW Ol VER LABS
continuous
AVE NO YOUNG/SURVIVING FEMALES (15)
STATISTICAL RESULTS SURVIVAL IN 100%
L C 50
95% C I METHOD
.
loo/
>5 m3 h .
fJD * MD
AVE W T/SURV CONTROL (0 25 mg)
1O/.
> 6 mA/t-
MD ND
SURVIVAL IN HIGHEST (
) CONC
NUMBER OF REPLICATES NUMBER OF ORGANISM/REPLICATE
NORMAL DISTRIBUTION?
HOMOGENEOUS VARIANCE?
NOEC METHOD
NOEC SURVIVAL NOEC REPRODUCTION/GROWTH
SG SG SG
COMMENTS f ivlDa. NrvF
(_ vu. -`ro |n.So.fKQ<jrV
Il UEMPLATErDIODENCIMlIOADMIMTESTSUM WPD
Revised March 21. 2001
\
Company Sanitized. Does not contain TSCA CB1
OLVER LABORATORIES INCORPORATED ENVIRONMENTAL BIOLOGY LABORATORY
CLIENT I W c u f t * TOXICANT/EFFLUENT
TEST SUMMARY SHEET
JOB NO
Io l~l5____________ PAGE
O F ... L
PERMIT NO
M/A _____________________ __ ______
ACUTE TOXICITY TEST RESULTS Cenodaphnia Falhead Minnow
CHRONIC TOXICITY TEST RESULTS Cenodaphnia
TFST DATFfS^
z/i -T -I'slo l
4 /l-W lo l
TEST CONDITIONS TEST ORGANISM AGE DILUTION WATER SOURCE AERATION
U3
TEST ACCEPTABILITY CONTROL SURVIVAL (>90%)
/. ^ 4 VOouvs EPA-MI-IW OLVER LABS conlinuous
1n i l / .
1 EPA-MHW OLVER LABS conlinuous
-
In n '/
TEST ORGANISM AGE DILUTION WATER
SOURCE AERATION
CONTROL SURVIVAL (*80%) NO OF CONTROL FEMALES
% CONTROL FEMALES WITH 3 BROODS (*60%)
EPA-MHW OLVER LABS
conlinuous
Falhead Minnow
EPA-MHW Ol VER LABS
conlinuous
STATISTICAL RESULTS SURVIVAL IN 100% C H ^Vve v t C v i c } 1r
qs% n i METHOD
`
lo o -/. > loo
N)t rD-v "fc ro D
AVE NO YOUNG/SURVIVING FEMALES (*15)
AVE W T/SURV CONTROL (*0 25 mg)
Ion/.
> InTM mpi/L.
MD MD
SURVIVAL IN HIGHEST (
) CONC
NUMBER OF REPLICATES
NUMBER OF ORGANISM/REPLICATE
NORMAL DISTRIBUTION?
HOMOGENEOUS VARIANCE?
NOEC METHOD
NOEC SURVIVAL
NOEC REPRODUCTION/GROWTH
SG SG SG
COMMENTS -fr
MirE &*rkxrr.^<xU<L 7 V
morkV-K^)
I! rtEM I' LATE\UIOBEIICHWOADMIN\TESTSUMWPD
R e vise d M arch 21, 2001
S a m p le In form alion
C lie n t
P la ^ o T :
P erm it N o
N/ '
T o xica n l/E fflu en t
5 m-jjL.I *
S a m p le Typ e
r3 7 a
G r a b C o ll e c t e d __________A M / P M
//
C o m p o s ite C o llec te d F r o m ________ A M / P M
(D ate)
_J l_____ ______ ( D a t e )
T o ___________ A M / P M
//
(D ale)
Job No
(a o /~~75
S a m p le N o __
TR C
ro /A
m q /L
In itial p H Initial D 0
N /A
n /A
m q /L
A d ju s t m e n t s _______________ _
^ TR3 I 4 .r
. ACUTE TOXICITY TEST
T e s t In fo rm atio n
A n a ly s l( s ) S r r > ( J|?, rvj
T e s t S p e c ie s P- rvom< tos
C u ltu re N o
_______ ___
A g e Z. d . ^ $
Length (s S D ) a h ~ 1 o . Q 5
W e ig h t ( r S D )
a.Mt o -3^
T est M ode S 'R h 'c .
D ilu tio n W a te r
& PA im u J
Start of T e s t
1E n d o f e s t
AM^
/ l z 5/ of (D ate)
L7r3^> A M aP m 1 foT) & 1 ( D a t e )
T e s t C o n ta in e r S iz e T e s t S o lu tio n V o lu m e
< * 0 m u ____________
'loo m e
c M D is so lv e d O x y g e n (T im e /T e s t S o ln /C o n c )
A eratio n
I L L J. L/ _____ _____ -------- -------- -- -------tJ/ A
B eg in n in g D a te /T im e /R a le
P h o lo p erio d 1 6 -h o u r day/O -h o u r night
Cone or %
5 .0 n \ V c
Rep
A
N u m b e r o f Live O rg an ism s
0 24
48
ID /C
fO
% S urvival
D is so lv e d O x y g e n (m g /L )
0 24
48
pH
0 24
48
JO o/ 7 -B
7P 7 7 i l - 7 , 7
T e m p e ra tu re (C )
0 24
48
5 85*
37
In itial A lk alin ity (m g /L as C a C O J
In itial H a id n e s s ( m g /L a s C a C 0 3)
C o n d u ctivity L im h o s /c m ) In itia l/F in al
50
IO 0
3 )7
AI .0 Or\a)) L
10 / / o l o o ' / . 7 .? ?
l.o T 7 n - 7 7 Z 5 2 5 3 5
rA T E
Company Sanitized. Does not contain TSCA CBI
0 ' " W l_
A
10 /
/O
0 6 / 7 -X
-70 i . i 1 1
87
37
3/
A 10o o \ h /,
i a/ o
fo
| /( 7 ,5 ?
7 ,o
7 -8
1----- "------------------ --
i n z 85~
\C a a - \ - r o
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7 ^) o I 0 0 / 7 i t ,
7 - 5 7 .7 - i n Z 5 f l S l .
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A n a ly s t's Im li a ls /T im e
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310
80
2^ Sj ; J_- l / . | j o |
Condition o(Organisms atTest Imtialion/End H<ftV\VvM , Oorrocx) J \-l Q I }-h -- fl.Q_Cjarl.iL
N \Tcmplales\UioDefich\acule\rOXTEST WPD
OLVER
LABORATORIES
S a m p le In form atio n
C ile n i
rJn .iP r.n ~ t
P erm it No
N /.~
T o xican l/E tflu en l
IS a m p le T y p e __
M
G ra b C o llected
C o m p o site C o llec te d
F r o m ________ A M / P M
T o ________ A M / P M
A M /P M
/__L
(D ate) /______ ( D a l e ) /______ ( D a l e )
Job No ,
,
S a m p le N o
_____________ .
TRC
N /A
m q /L
In itial p H
n / A ____________
In itial D O aj/ a
m q /L
A d ju s t m e n t s ___________
4 ^ __________ CA I o -f'
ACUTE TOXICITY TEST
T e s t In fo rm a tio n
liA n a ly s l( s ) 5<~n ; $ r J _______
C ic.T e s t S p e c ie s
c A A a ________
C u ltu re N o Age
z-\ W >
Length (s S D )
N /A
W e i g h t ( x S D ) ___ N / A
Jest M ode 5 - H h c D ilu tio n W a te r & PA m H ixJ
Q 0S ta rt o f T e s t _
-7
A M /)
/ /Z 5 / cl
7 / 5 ..E n d o t T e s t --------_ _
T e s t C o n ta in e r S ize
^ ) /9 7 l bl >0 i*nl'2-S m L.
T e s t S olu tio n V o lu m e
(D a le ) (D ale)
D isso lve d O xygen (T im e /T e sl S o ln /C o n c)
//
7 /______ L__ L
A eratio n
B e g in n in g D a le /T im e /R a le P h o lo p e rio d 1G -hour day/O -hour n iy h l
Company Sanitized. Does not contain TSCA CBS
C one or % 5 .0 rr'.S//
Rep
A
p>
N u m b e r o( Live O rganism s
0 24 48
5h cA 7 f
%
S urvival
D is so lv e d O x y g e n (m g /L )
0 24 48
pH 0 24
/ O / T 7-8)
7 . 7 _lL_ n
coT e m p e r a lu r e
48 0 24 48
1-3 75 2$
In itial A lk alin ity ( m g /L a s C a C 0 3)
Initial H a rd n e s s ( m g /L a s C a C 0 3)
C o n d u c tiv ity (/m ih o s /c m ) In itia l/F m al
( ? o
/0 O
3 i2
S 3 / f /'"
I1 .0v m i7WViL ' A
5 5
A t m.V,
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7 P q-h 7 7 7 .7
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1 $ 2 5 OS 3 5
7 ? 1-3 2 S i S
75
31 s " X
0 O'
A
------- ------- J-- &
5
I b b /' 7 .8 7 -u 7 7 7-8 5 s)
7 % 25 os 5 5
" UI A
6
A n a ly s t's Im i a ls /T im e
5 # 5 5 ? fo O '/ 7-8 7'U
5 o ^V
5HmIPch^ / ,,' T S I I n) Sffl
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7-0 Srr)
fl m S) S'
2 5 0-5 S/n S.I
C o m m e n t s ~X A & . 9 'M L / 5 P ..A L
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N \Templ3 t05\BioOencH\arute\TOXTEST WPD
OLVER.
l a b o r a t o r ie s
Company Sanitized. Does not contain TSCA CB1
S a m p le In fo rm atio n
C lien t
'D 'a P
P e r m i t N o _____ T o xica n l/E fflu en l
S a m p l e T y p e ___ G r a b C o lle c t e d _________ A M / P M
C o m p o s ite C o llec te d
F r o m ________ A M / P M
To A M /P M
//
(D ate)
J ______ ( D a l e )
J ______ ( D a l e )
Job No
(ooHS
S a m p le N o
TR C
N /A
m g /L
Initial pH
N /A
Initial D 0
n /a
m g /L
A d ju stm en ts
m /A
p*> I o f \----------------
ACUTE TOXICITY TEST
T e s t In fo rm a tio n
A n a ly s l(s ) s m . S P iY
o l IQ\S t a r t o f T e s t . S ' - o o A M / 6 0 )
/
0T e s t S p e c ie s
3 3 P iiA ________ E n d o f T e s t _. ____ ________ A M f r t v P
C u ltu re N o
J Lt o A i . , . U . u A C . i t W ^ T e s l C o n t a in e r S i z e _ 3
-------------l-Y-- ll
(D ate ) (D a le )
Age
. T e s t S o lu tio n V o lu m e
Length (x S D ) W e ig h t (x S D ) Test Mode
xi/A WA
D isso lved O x y g e n (T im e /T e s l S o ln /C o n c )
//
/ / _ _ J ___L
W t LA e r a tio n
D ilu tio n W a te r
B eg in n in g D a le /T im e /R a te .. /V /A
P h o lo p e rio d 1 6 -h o u r d a y /8 -h o u r night
Cone or % lo o o fm /
Rep
A
&
N u m b e r o f Live O rganism s
0 24 40
% S urvival
D is so lv e d O x y g e n (m g /L )
0 24 48
5 5 5 7 lo o / 7 -p i 7 - * 7 . ?
5 5 5^
pH 0 24 48
7 ? " 7.7 I S
T e m p e ra tu re (C ) 0 24 48
In itial A lkalin ity ( m g /L a s C a C 0 3)
a5
_S S l
G>H
Initial H a rd n e s s ( m g /L a s C a C 0 3)
C o n d u c liv ity (n m h o s/cm ) in itia l/F m al
I OO
539
\UU n / L
A-
E
5 5
5 it
/Q 0 '/
7 , I S 7 -t
7 .7
35
A
b
------------ 1--
^7
5
57 l o o / 7 8
7J
1?
5 5 IT
I
7 . 7 1, (d zS 3 5 - 5 . 5
cL-J
tZ _
5 3 L -t 7 i
s'
A n a ly s t's Im li a ls /T im e
rJ / T
3 D3Pd
^
P
a t**
5 /r\
&rr\
S/n
C om m ents
------------------------------------------------------------ --------------------------------------------_ _ _ _ _ ---------------- ------------------------------------------
C o n d itio n ol O rg a n ism s at T e s t Im liatio n /E n d
I Q, O o r m u l
.H C H ~ ^ Y ,
Q- l .
N \fenipldlbf5\iuenc.lAdCulc\TOXTEST WPD
N otes
#3
V 2 i/oJ
OLVER
LABORATORIES
Sample Information
Cileni
'D ^P o rA -.
Permil No ' ___ Toxicanl/Effluenl
Sample Type ;_
Grab Collected ____
Composite Collected
From ______ AM/PM
To A M /P M
A M /P M
/
//
(D ate)
/____ (Dale)
/ . (Date)
Job No
Loo /lS
S a m p le N o
TRC.
N/A
m q /L
Initial p H
N /A
Initial D O
n /A
m a/L
A d ju s tm e n t
n /A
T e s t In fo rm a tio n '
Analyst(s) s tn . S jL r i Tasi Spadas p . p a m A t
C u ltu re N o P i a n
Age
e < x > \V
L e n g th ( R S D ) ________
W e i g h t ( x S D ) _______
Test Mode
Dilution Water EPr
_.
ACUTE TOXICITY TEST
.Start of Tesi -3 IT O AM/@ ? -I I ! \ (Dale)
End of Test 3 5 j 3 --
T e s t C o n ta in e r S ize
to
/ 0 _L (Date)
nr\L
T e a l S n ln lio n V o lu m e
S?*5
r *N U ------------ -
D is so lv e d O x y g e n (T im e T ie s t S o in /C o n c )
' / I______!__1______I--- L
A e r a t io n _________ _____________________________ -- B eg in n in g D a le /T im e /R a le
Pholoperiod 16-hour day/8-hour night
Cone or %
Rep
loop tng/. A
Number of Live Organisms
24 40
ID to I
% Survival
Dissolved Oxygen (mg/L)
24 40
pH 24
/oO/- 1 & iS L k l l f - 7 z l
Temperature ("C)
48
1 5 25
24 40
35 7 5
Initial Alkalinity (mg/L as C a C 03)
(a t-\
Initial Hardness (mg/L as C a C 03)
Conductivity
(imhos/cm)
In itia l/F in a t
539
\0O
lOo mc^/L__A
LCl lo O
I 0 0 Y. 7 f t T O M 9 - 1 7 J
^5 3 5 R 5
Crsn-Vr-a| A
lo IV l o l b '/ M
7,0 7 &
7 1 5 2.5 3 ^ 3 5 "
331/
ompany Sanitized. Does not contain TSCA CBf
Comments
Z'-TQprr, Jrn
Condition ol Organisms at Test Imliation/End
5 EfJ 5rn sp7
VNgaVfti^ , n o r m a l -- i -- H C Q /
N ITpmplatesIBioDendAaculetTOXI EST WPD
Sv(J Sm lS.rO S'2 rV Notes Cr>j # 3 ' / z6/t>l
LC-5r> > loop
O t , n?--l(I
OLVER
LABORATORIES
APPENDIX 5 ACUTE TOXICITY TEST DATA
Company Sanitized. Does not contain TSCACBI
OLVER
la b o r a to r ies
Company SanHzed. Does not contain TSCA CB1
OLVER LABORATORIES INCORPORATED ENVIRONMENTAL BIOLOGY LABORATORY
TEST SUMMARY SHEET
CLIENT Dufcnt _
TOXICANT/EFFLUENT
JOB NO PERMIT NO
Acu,-K TjXxc-i~Tj T id in g
ACUTE TOXICITY TEST RESULTS
( c n l l 6 ___________ PAGE __ !__ O F ___/ N /A ______________________________
CHRONIC TOXICITY T EST RESULTS
Ceriodaphnia Fathead Minnow
Ceriodaphnia
TEST DATEfSl
Z j IM -Z./lCe/ol z/ h - Z / Jfa/o/
TEST CONDITIONS TEST ORGANISM AGE DILUTION WATER SOURCE AERATION
A hour* EPA-MHW OLVER LABS continuous
3 .vjs
EPA-MHW OI.VFR LABS
continuous
TEST ORGANISM AGE DILUTION WATER
SOURCE AERATION
EPA-MHW OLVER LABS
continuous
Fathead Minnow
EPA-MHW OI.VFR LABS
continuous
o
TEST ACCEPTABILITY
CONTROL SURVIVAL {z 90%)
loo/
CONTROL SURVIVAL (*00%) NO OF CONTROL FEMALES
% CONTROL FEMALES WITH 3 BROODS (60%)
AVE NO YOUNG/SURVIVING FEMALES (15)
STATISTICAL RESULTS SURVIVAL IN 100%
LCW
95% C I METHOD
35/
>5<30 "Yj/l
ND* wr>
AVE W T/SURV CONTROL (0 25 mg)
/mi/. > 5 oo m 5 /L
N fc> WO
SURVIVAL IN HIGHEST (
) CONC
NUMBER OF REPLICATES
NUMBER OF ORGANISM/REPLICATE
NORMAL DISTRIBUTION?
HOMOGENEOUS VARIANCE?
NOEC METHOD
NOEC SURVIVAL
NOEC REPRODUCTION/GROWTH
SG SG SG
iniCMPLATEUlOQGNCinmOAUMJimeSTSUM WTD
R e vise d M arch 21, 2001
Sample Iniormaiio
Client'
-
Permit No n /A
Toxicant/Effluuent
Sample Type3 s1i
Grab Collected ______ AM/PM
Composite Collected
F r o m ________ A M / P M
To _______ AM/PM
/
/
//
(Dale) J ____ (Date) _____(Dale)
Job No /7 T Sample No wM
T RC Initial dH Initial D 0 Adiustments N/
ma/L ma/L
P3 i f 7. ...Z ACUTE TOXICITY TEST
Test Inlormation
3,^0 / )fa/oTAnalyst(s) s iA i 1 f. n>
Start of Test / 30
Test Species C`.enn'baniu<L ctubia. End of Test I
AM/@ 2. / I H I o l (Dale)
AM/ggft A
(Date)
Culture No ,'n d m t/u o l
Test Container Size 3p m I
Age c ?<-/ h r s
___ Test Solution Volume 2s .t
Length (r SD) Weight (x SD)
Ja
LL
Dissolved Oxygen (Time/Test Soln/Conc)
/ /______/ /
//
Test Mode ifc.h c.
Aeration j / A
Dilution Water EPA /nr/uu
Beginning Date/Time/Rate
Pholoperiod 16-hour day/8-houi night
Company Sanitized. Does not contain TSCA CB1
Cone or %
Rep
--f*D-k:O----fcro* m-------
A & c
D
Number of Live Organisms
0 24 40
% Survival
Dissolved Oxygerl (mg/L)
0 24 40
55
1 s 7O
S5
`V 9 5 / -
S?
5
5 57
pH 0 24. 48 1 ? I S 7 .2
Temperature (C) 0 24 40 3b
Initial Alkalinity Initial Hardness (mg/L as CaCO-,) (mg/L as CaCOj)
Conductivity (imhos/cm) Initial/Fmal
3 0 A-
S S
S'
--a1/-o--O----jp~fp--m------
A 6 c.
C 5 ?
08
f sf
R) / 5r
55
R/
'
1 . 0 T f 1 8 7 9 Sb 2 b
^> 335
T-o--o----f B^U-M5--
A fi
5 S'
1s
5 5 5 / |O0 /
7.0
7 8 7 f7
7`S'
3 pT'' S S >^
(1 5 S
) s ' f
Analyst's Inili iIs/Time T T Comments
5J 5 jJ
Condition of Organisms at Test Imliation/End f) (W7/u
.<-6
L 6U>
iliS .01
Notes l'o r b a i
d " T- i j s 'foi 5oa " '`Ml.
ftoCM0-/ /o n R
U n try I $ h /-A,i/T f.-ne-Z/iQno i a p o m re d he aldhu / napyci |
N \Templaies\8ioOonch\acul0\TOXTE5T WPD
OLVER
LABORATORIES
Company Sanitized. Does not contain TSCA CBt
N \T enpIdlos'DtoDunciAocutc\TOXT EST WPD
LABORATORIES
I
Company Sanitized. Does not contain TSCA CB!
Sample Information
Client
Permit No ___
Toxicanl/Effluenl
Sample Type _
Grab Collected
AM/PM / /
Composite Collected
(Date)
From _____AM/PM
J ___ (Date)
To ______ AM/PM
J ___ (Dale)
Job No (p u ) 1 5
Sample No AJA
TRC
mq/L
Initial oH
Initial D0
rrm/L
Adiustmenls J
ACUTE TOXICITY TEST
iTest Information
Analysl(s) s / n Line1
Test Species
Culture No Jiig .fi
Age ______ --30---------
I n n n lh (< S D
0,0^
W e ig h t (>< S D ) a H a 1
c
Start End Test Test
o( Test ol Test.
1a5-0op
AM/Pt^t g V/1 l o i 'M W 1 / Ih l T
(Dale) (Date)
Container Size ___(_p_o_o__m_I_--______
Solution Volume `-to o mL______ L
Dissolved Oxygen (Time/Tesl Soln/Conc)
//
//
//
Test Mode 5-kh'C______ Aeration _----------------
Dilution Water
mH<~j Beginning Dale/Time/Rale
Pholopenod 16-hour day/8-hour night
Cone or % Rep
Number of Live Organisms
0 2d 40
% Survival
Dissolved Oxygen (mg/L)
0 24 48
0
pH 24 48
Temperature (C) 0 24 48
Initial Alkalinity Initial Hardness (mg/L as CaCOJ (mg/L as CaC03)
Conductivity 0/mhos/cm) Imtial/Final
5dC Pfm A
I n / 1 0 / OO /' 7.B 7 0
78 7 5 7 7 25
25
(eXL
s i n I a lb / 00 /
3o2L /T o g
A 1 0 1 0 (0 00 t "7 A 7 -0 U A 7 P) 7 . 5 " 7 7 7 5 2 5 2 5 8 t o 10 1 1 o o i -
3 ? /5 /n < 5 5^ 3i f
3oO PprTi A R
fZ 0 0 f p m
A 6
1 0 0 to I O \6 10
1 0 t o I 1D to lo
/oo 7. 7 - 8 U too t.
(o-(p 7 .& 7 5 7 7
160 7 ' P) 1 . 0 A 1?! 7 - 8 7 5 7 7 loo '
2 5 ,,7 5 ... 2 5
3(7/0 25 5 5 _
2 -/ T T c fi
3e3r^c) 7z/ 14/
Co,vR> I
A 6
I Analyst's liutials/Time Comments
10 , 0
t o /o
m th
5 to
Condition of Organisms at Test Imlialion/End
t o >
60 /' uW O
7 l x /p b 7 - 8 Vi t-fhD VJAV) S s fi
1.5 7 7 25 25 V i LmT> V\ffxO )0>rr lwD LimP
(e O
Noies C /L r L u $ Ll ^ S l o 0 5 00 m \ J ----------------- ----
, norm g I/ H<aI/K] HirCeroat
N \Templaies\BioBench\aculeYl OXTEST YVPD
OLVER
LABORATORIES
m.
W
W
Sample Information
Cileni ___ LA-
Permit Ho
N
Toxicant/Eftluenl
Sample Type _
Grab Collecled _____ _AM/PM
Composite Collected
From ______AM/PM To AM/PM
/ /
//
(Date)
J ____ (Dale) J ____ (Date)
Job No feoH E
Sample No A)/A_______
T R C ________ m a /l
Initial pH __ Initial D O
mq/L
. Adjustments
_______ P. 7- O'f 2. ... ACUTE TOXICITY TEST
Test Information
Analyst(s) "Zm / l~mt>
Start of Test 2 -nn AMlfu)
^ I (Date)
Test Species P fV*.^ faC End of Test, i 5 0 _Atv#M
/ i W p f (Dale)
Culture No Age -3
. 5
Test Container Size _ Lo o p / n L
Test Solution V_o_lu_m_e
H<Pi. rn t~_____
I ennlh fx SDt n H tT t o o<- cm
Dissolved Oxygen (Time/Test Soln/Conc)
Weight (x SD) -I
0-21 mtj
___ I------/------ ----- L------L------ ------L------L
Test Mode S-ki-fi?. Dilution Waler Erf1A / n u n
Aeration
Beginning Date/Time/Rate Photopenod 16-hour day/B-hour night
Cone or % Rep
Number ol Live Organisms
0 24 -to
% Survival
Dissolved Oxygerl (mg/L)
0 24 40
0
pH 24 40
Temperature (C) 0 24 40
Initial Alkalinity Initial Hardness (mg/L as CpC03) (mg/L as CaC03)
Conductivity
(f<mhos/cm) Imlial/Final
A 1 0 1 |0 loo 1 7 - 8 l x
7-
75 I f -
3 D2 ^ /
( m i dH ) y~t>n J*
rz
) n I 10 1 0 6 (
/ l\X
Company Sanitized. Does not contain TSCA CB1
* 1
Analyst's Imti als/Time MfcH Comments
imp
1
Condition of Organisms at Test Iniliation/End
Sn-| LWt Srr) UpoO U vtT) z>sn U^O \tfAQ Notes
Hec-lFN-j , v-i a r m r j /
. Oorrfic'
N \T6mplals\BtoGanch\acuIe\TOXTEST WPO
4X R ' P/ls'/o f
OLVER
LABORATORIES
APPENDIX 6
CHRONIC TOXICITY TEST DATA Pimephales prometas
45 Company Sanitized. Does not contain TSCA CBI
OLVER
la b o r a to r ies
I
t
Company Sanitized. Does not contain TSCA CBi
TEST SUMMARY SHEET
OLVER LABORATORIES INCORPORATED ENVIRONMENTAL BIOLOGY LABORATORY
CLIENT TOXICANT/EFFLUENT.'
JOB NO _ G>on 5
PERMIT NO
N/A
PAGE
OF
ACUTE TOXICITY TEST RESULTS
Ceriodaphnia Falhead Minnow
CHRONIC TOXICITY TEST RESULTS Ceriodaphma
TEST DATE(S)
TFST CONDITIONS TEST ORGANISM AGE DILUTION WATER SOURCE AERATION
EPA-MHW OLVER LABS
continuous
EPA-MHW Ol VFR I ABS
continuous
TEST ORGANISM AGE DILUTION WATER
SOURCE AERATION
EPA-MHW OLVER LABS
continuous
TFST ACCEPTABILITY CONTROL SURVIVAL (90%)
CONTROL SURVIVAL (80%) NO OF CONTROL FEMALES
% CONTROL FEMALES WITH 3 BROODS (60%)
Falhead Minnow
zj ^--xlzolol
i -ZH ho.
EPA-MHW OLVER LABL
continuous
STATISTICAL RESULTS SURVIVAL IN 100% l c 50 95% C I METHOD
COMMENTS
AVE NO YOUNG/SURVIVING FEMALES (15)
AVE WT/SURV CONTROL (0 25 mg)
SURVIVAL IN HIGHEST f 5oo "\3/o) CONC NUMBER OF REPLICATES NUMBER OF ORGANISM/REPLICATE NORMAL DISTRIBUTION? HOMOGENEOUS VARIANCE? NOEC METHOD NOEC SURVIVAL NOEC REPRODUCTION/GROWTH
qzR
R/
IO S ND G V;s R No G S i i S tdtd'SG IXiM.-H!)
5oo r^a/t--
Soo
>gaO "'S/l.
li \ 1EMPLATP'DtOBMCH\8 tOADWlM\TESTSUM WPD
Revised March 2 \ , 2001
Company Sanitized. Does not contain TSCA CBI
TEST SUMMARY SHEET
OLVER LABORATORIES INCORPORATED ENVIRONMENTAL BIOLOGY LABORATORY
CLIENT D iaPartiTOXICANT/EFFLUENT
JOB NO
U ol~~i5__________ PAGE ___ L . O F -- L
PERMIT NO
m )A____________________________
ACUTE TOXICITY TEST RESULTS Cenodaphnia . Fathead Minnow
CHRONIC TOXICITY TEST RESULTS Cenodaphnia
t1ctoc t1 UnAnT1Fu/lQO\i
TEST CONDITIONS TEST ORGANISM AGE DILUTION WATER SOURCE AERATION
TEST ACCEPTABILITY CONTROL SURVIVAL (90%)
FPA-MHW Ol VER LABS
continuous
FPA-MHW OI VER LABS
continuous
TEST ORGANISM AGE DILUTION WATER
SOURCE AERATION
#CONTROL SURVIVAL (60%)
NO OF CONTROL FEMALES
% CONTROL FEMALES WITH 3 BROODS (60%)
FPA-MHW Ol VER LABS
continuous
Fathead Minnow z //3 -z /z //
/ - Z>4 hrs FPA-MHW Ol VER LABS continuous
^57.
STATISTICAL RESULTS SURVIVAL IN 100%
l c 5q
95% C I METHOD
f
COMMENTS
C oaLvO
oortV,
AVE NO YOUNG/SURVIVING FEMALES (15)
AVE W T/SURV CONTROL (0 25 mg)
SURVIVAL IN HIGHEST ( 5oo ^ 3/0 CONC NUMBER OF REPLICATES NUMBER OF ORGANISM/REPLICATE NORMAL DISTRIBUTION? HOMOGENEOUS VARIANCE? NOEC METHOD NOEC SURVIVAL NOEC RfPRODUCTION/GROWTH
(.So o
o f w *-W ~ o \ PSr-- ' L,`wr
o Hzfi
R ft'/ H IO
S N n G Vci R NO G Vcs S SAm I'$ G
5 oo <r >\/i 5 qo ^ / l __ > 5 DO m j/,
N\TGMPLATE'B1086NCH\BI0A0MIHMFSTSUMWPD
Revised March 21, 200i
Company Sanitized. Does not contain TSCA CB1
>
\
is
OLVER
LABORATORIES
AQUATIC TOXICITY T E S T S A M P L E U S E S H E E T FO R STA N D A RD SYNTHETIC DILUTION W A TER
Client' 0 3 f ^ o -v
Effluent/Toxicant Synthetic Dilution Wa`
Job Number Cp o )~7 *5_______
Permit No
_________ _
oderatelv Hard Water (MBW1
Page_L_ofJ--
Testing Requirements
48-Hour Acute Cenodaphma Test
48-Hour Acute Fathead Minnow Test 96-Hour Acute Fathead Minnow Test
7-Day Chronic Fathead Minnow Test _____ 3-Brood Chronic Cenodaphma Test _____ Other_____________________________
j-
TFRT HAY
1
23
Carboy No /Identiricalion
tf i
Pieparaliori Dale
j./2/ol
Alsh)
< ?/(3 /o I
Time & Day of Use
19j Hdt | a 0 m <&>2i N p \ l'iDamr@i}& J5 / I
Age of Dilution Water1' '
3D Alkalinity (mg/L)
(Acceptable Range 60-70 mg/L)
j-7 rJ dot 5
Po
..............(..0..--c| oici 5
Po
p
Hardness (mg/L) (Acceptable Range 80-
dH
n n (mn/\ )
Aeraiion
3 00
- -- 7f . ?u ..........
ND-
n$
Continuous
2V
3 00 1 .
ND
7J
Conlinuous
7P
307 in
ND
1?
Continuous
4 #3
2 / 1? h i
3 days
5 16 1 7 LEV
2 ^am^ S / ' 7 / 0 |
Q /lp /o l
5?,/ H / D 1
* am/^fj R / I ^ / / A 3 m / 0 > / / 7 /
1 4 ay
)
(oO <b 0 Loo
(p H
%
3 7 7 .? ND
1 .
Continuous
7 ^ _____ ND
1,9
Continuous
313
S .O ND
7 ..g _______ Continuous
lo b
in
17
ND
7.8
Continuous
COMMENTS m Svnlhelic dilution water is prepared wilh laboratory deionized waler and leagsnl grade chemicals (EPA/600/4-9,1/0021
(2) Each balch of diluhfen waer is no! used tor more than 14 days following .the preparation datg------------------------ -- ------------------------
ND = Nol Deleclable-------------------------------------- ----- ----------------------- -- ------------------------------------------------- -- -- ---------------------
OLVER
LABORATORIES
O LVER
laboratories
LARVAL FATHEAD MINNOW SURVIVAL and GROWTH TEST
SURVIVAL DATA SHEET
CLIENT X l 4 2 a 2 PERMIT NO _________ EFFLUENT/TOXICANTO__s .
DILUTION WATER f Q PHOTOPERIOD 16 nr Day/8 hr Night
CONC "5
REP A B C D
A
B C D
START 10 10 10 ' 10
10
10 10 10
1 10 ( 0 6
lo 10 lo 6
2 10
IO IO l
10 io IO IO
JOB NO ( t OI 7 s _______ PAGE / . o f
TEST ORGANISM AGE . `I H J u ' i (
START of TEST
A M p U \J L J J 3 J O
END of TEST l 1^ A
! V I Oj
NUMBER SURVIVING PER DAY
3 456
6
1O to
)
If)
l o le
IO
|(1 I O O 9
( 1 0 lo I o
7 io I 9 io
(o I O \ i o t 0
IO " 9 9
77
Io I O (o !0 10
10 l o l o l o l o
COMMENTS TEST SOLUTION VOLUME 250 mi TEST CONTAINER SIZE 600 ml
FEEDING 0 1 ml BRINE SHRIMP NAUPLII 2-3 TIMES PER DAY
-
16 M jjL
A B C O
10
l o 1 0 10
l o \ o /O
0
10 ( I O
IO
lo
i o i
I
10 l O 13 [ 0
l o i o I O 13
10 I O (.0
~ T 9 9 fi
y^ I l
A 10 i o
B 10 1 0
C`
10
(0
D 10 0
: f) l 6 IO I \ 0
( 0 |0
v, Y*) \l_
A 8 C D
10 l 1 0 0
10 l o
[ 0 IO
10 I O \ l o
10 I O
1 io
lo 0 7 ? i o 1o / o IO
10 1o I O q
l a lo
/o i
/ O lo Io
Iff
i o io i o
( o lo
,0
10 lo
1 o J
(c> I O
1OlY^ji analyst
A B C D
COM M ENTS
10 / a 10 / o
io IO
10 l o
IO
10 O l
im T)
f i f l-Hi n i 1 I 1 d
IO 1o 1 IO io lo
16 l o
/A V fitsl
1&P
Q i'if
Orejan i sms
\o IO / o
10 IO
IO
10 /> O
lo J0 IO U" D
CLP/ V q r h a l-th - u
r / -its 0 m Orr>plrftoo
___
N 'Templatcs\BioBench\clvc>mcviFHMSl,'RV W ?D
49
Revised November I ?Q0Q
Company Sanitized. Does not contain TSCA CBI
O LVER
LABORATORIES
r.\ IF N T D u f n n t -
PERM 1T NO E F F L U E N T /T O X IC A N T .
DILUTION WATER B?f> m H uJ PHOTOPERIOD 16 hr Day/8 hr Night
CONC 5 oo
REP A B C D
STA R T 10 10 10 10
A 10
- / &iS u
B Ci
D -----------
A
B
C D
10 10 10
10 10 10 10
12
lo }
IO lo t o lo I D [O
/
lo
to
iO
lo (0
7 --l o--
3 /d > 1 IO 10
!o in
0
LARVAL FATHEAD MINNOW SURVIVAL and GROWTH TEST
SURVIVAL DATA SHEET
JOB NO /yW?S~ _ PAGE _ Z _ o f ^ _
TEST ORGANISM AGE. -ZM
( i-ZU VwsA
START of TEST 3 ;6> A M & _ 2 J J J 0 L
END of TEST 7 ^ AM/ !
XTZoi a I
45 R lo /o 9 iO lo / o /o
I D lo J O lo 9
67
COMM ENTS
lo /0
TE S T SO LUTIO N VOLUM E. 250 ml
T~
TE S T C O N TA IN E R SIZE. 600 ml
9
1 0 /< ?
l o />
FE E D IN G 0 1 m l BRINE SHRIMP N AUPU I l o } 0 2-3 TIM ES PER DAY
/ o 10
? ?.
A 10 B 10 C 10 D 10
A 10 B 10 C 10 D 10
A 3 C D
a n a ly s t
COMMENTS
10
10
10
10
MGH
5 id 7~o
U rV 2 *p
5 (lb J
Co.V+orJ_# I &/0 '0 f f t a h '.i rr\S A p p e a r
p 4 l- t f y Cf-t -fe V-f- I n r h - h o / ) * C o m p Ic T ?
N 'Tctnplatcs\iocnch\chroi\ic\FHMSUl\V V/?D
50
Company Sanitized. Does not contain TSCA CBI
Revised November I 2000
O LVER
LABORATORIES
LARVAL FATHEAD MINNOW SURVIVAL and GROWTH TEST
GROWTH DATA SHEET
CLIENT _ Q u OQi } l PERMIT NO
JOB NO V 01?*? ANALYST L r ^
Deciea vveigiuI N IT IA L B A L A N U f c U A U D K . H 1 1>JJN U n t U i N e x
CONC
REP
F O IL W E IG H T (m g )
F O IL W E IG H T
+F IS H
W E IG H T of F IS H
NO of S U R V IV IN G FIS H
CoYY
. A 10(p 0 (p
B
C n2 70 0 ? i oL,
110 H i III 7<j
l/5~ U
7 5 HO
V 12
3 11 7 72 H o7
0 7
i0
Q)n\ro l
A 77.79
B 90 3 9 C 90.07 D i /o3\ 0 2
10? a
7 3 ?2 19 7 7
i Gb 72
5 i7 3 .5 0 3 s.V 1,0
to 16
f 7
10 "S/l
A / 03 7(a B 09 n
C r / oo
D ?o s7
A ?5o2
B > f 5?
C , b<?. o7 D 77 00
0<k 7 (j
20 9 2 ?9 75
27 50
12 2 3
72 HS 21 0 7
5 00 7.30 5 71 9 7\
M S7 3 7io 7 71 3 93
o 7 to 0
to
6 /0
?
A ?0 00
93 ??
3 92
?
75
B 7777 C ? 7 r>7
lo2 7 7 75 2%
5 0.3
H 17
0 7-
D 79.10 02- 27 9 - i 7
10
5o ^ 1^
A B C D
77. SI
92 27 97 !<? T V 7-0
To. 9 5
$0 3 7
72 7b 7VSV
7 97 9 /o
3.71
9 37
0
/> /O 0
PAGE I of 2 7
, -'-Ht _J---- __________
AVERAGE
*
PERCENT
W E IG H T P E R F IS H
S U R V IV A L
.972
- 511_____ 312 709
/oo / 0 0 '/
9o Y '
/00 0
S l7 350
?>S3___ *9/o
/o o /.
00 /___ 7 6 '/,
36 /
.576 970 577 v,z/
ton / 9o /
..... 0 6 ' /
loo 7
9sH .
. H7LU Y Y / ........ ...
. 373
too V loo /
to o './ :- _______ 70 /
332 . 563 9 ) 7 w _
7 73 .9 / 0
33? v?y
Ho /-
O o '.L ______ %7
00 7
00 V '
/o o 3.. _______ too V 'oo >'
N \Tcmplaics'>BioEcnch\chronic\FKMGRWTH WPD
^^
Revised November 1 2000
Company Sanitized. Does not contain TSCA CBi
3o r 5 >
_
O LVER
LAB ORATO RiE S
LARVAL FATHEAD MINNOW SURVIVAL and GROWTH TEST
GROWTH DATA SHEET
CLIENT "P u -P o ^ PERMIT NO ______
JOB NO ( i 0 / 7 5
ANALYST
Im D
PAGE 7 of 2
INITIAL BALAN CE CALIBRATICDN CHECK Excected weiqnt
CONC
REP FOIL WEIGHT FOIL WEIGHT WEIGHT of
(mg)
+ FISH
FISH
"31/ UU UIL) /
NO of
AVERAGE *
SURVIVING FISH WEIGHT PER FISH
PERCENT SURVIVAL
A 76 7 7
9/ 77
B Lt 7 7 7 o rt?
C 7 7 /5
7 /T -
0
9 5 75"
?9 35
Lrrc
h :? 3 l 3 .7 3
3 3/
to > '0 to /o
.9 7 7
i q .o I l - ____
- .3?. 3 ________ / d V -
_
5 9 6 _______ _ / M 7 _____
-3 3 /
/O 0 /-
.
500
A /P P /,7 B 5 7 <?7C 7 7 /> D l ? 9 5-7
/ 0 5 * <55 H 0Z 7 3 7V 77. ? 0
H 93 7 17 7 77 7 7J!
/o 1
/0 10
993 . 7 /7 9 7 % ______
i3 ~ t
/ o o ' / ____
t o o /-. lo o '/
A B C D
A B C D
A B C D
A
B
C
D
h l N A L d A L A N U t O A L i o r w i h- ' in
COMMENTS r li I F t
iJu\^~
Qr\ "Un ^r-jvVieJ n a r n k r ^
, ,/ .
'Lia u
N 'Templaies\Bio3cnch\chromc\fKMGRWTH W?D
^^
Rcvibcd November i 2000
Company Sanitized. Does not contain TSCA CBI
CHRONIC TO XIC ITY TEST
V CHEMICAL ANALYSIS DATA SHEET
-. Page >f y
OLVER
L A B O R A T O R IE S
c lie n t T ) i <n n n f ~ JOB NO U O rtS
Pr cErRu vMi iI Ti N O
-
E F F L U E N T /T O X IC A N T
_
D IL U T IO N W A T E R EPQ 7*1 HW
TEST IN IT IA T IO N D A T E
X l 0 j o \ ------------------
TEST C O M P L E T IO N D A T E
A - / P I------------------
T E S T O R G A N IS M P 0 re A c la. S______
P H O T O P E R IO D
81 6 - H o u r D a v / - H o i j r N ig h t,
L I G H T IN T E N S IT Y _5P-1,,QQUrS-- -----------------------------
IN IT IA L
pH D .O (m g /L ) T e m p e ra tu re (C ) C o n d u c tiv ity (u m h o s /c m ) H a r d n e s s ( m g /L a s C a C 0 3)
DAY
1 1 ft 7-8
3oO
DAY
2
75
19
35
3oo
DAY 3
73 7S
7 ,7
,577
DAY 4
7?
7?
35
3o 7
DAY 5
7 -5
7-? 73 315
AY
6
DAY 7
0 .0 7 3
7S7 7 ?
3 .3 i 5 _
3 5 3/3
A l k a l i n i t y ( m g /L a s C a C 0 3) A n a ly s t's In itials
5m
5 (1 i\J L m D (JriD 5iM
unP
F IN A L pH D .O . (m g /L ) T e m p e ra tu re (C ) C o n d u c tiv ity (^ m h o s /c m ) A n a ly s t's In itials
____________________________
75 7 5 7 % io,0 3 . l 3 ?
73 55
7 -7 3 -3
73
73
----------
17
5 ds lb
00
3^
S0 u n D
313 3 3 7 2 9 6 L W twoLtnO S R pJ / * /
CO M M ENTS
L l'n .n a
u
----------
C. roi TntcieAnb, 'anf.rc/1.
1
1Jlp\
J
IN IT IA L
DAY
1
DAY
2
DAY 3
DAY 4
DAY 5
DAY
6
DAY 7
CO M M EN TS
pH 7 . ?
D .O . (m g /L ) T e m p e ra tu re (C ) C o n d u c tiv ity (u rn h o s /c m )
I7
15
300
H a r d n e s s ( m g /L a s C a C 0 3)
A l k a l i n i t y ( m g /L a s C a C 0 3)
7O
A n a ly s t's In itials
U ^D
75
75
25
77
7
7 ,5
300 27
G ?o
303
76 60
S rJ U n o
75
3 -7
75
7 .?
,3n 7
25
35
72
G o
urn w
_Z 7
75
77
75
35
3 ) 3 31H
7 2 Ctfpio:
(ztfbH * * - 5 2 LpO
i7 ^ / o ( ^ 7 :
(ACCmT'
F IN A L pH D 0 (m g /L ) T e m p e ra tu re (C )
.
75
(o.O
55
77
50 IKS'
77
5X
35
C o n d u c tiv ity (jim h o s /c m ) A n a ly s t's In itials
316
J P
330 ^ 0 LfflQ Y T )
N \TEMPLATP.BIOBENCH\CHRON|C\CHRONCHE W P0
75 31
35
272
W
7-7 75 7 5
7 - 2 (? 0 6 O So 7 5
333 375
0A i m O
Revise November 1 2000
53
Company Sanitized. Does not contain TSCA CBI
54 Company Sanitized. Does not contain TSCA CB1
CHRONIC TOXICITY TEST CHEMICAL ANALYSIS DATA SHEET
Pag 2, of _h_
O LV E R
L A B O R A T O R IE S
CLIENT JOB NO /gO l f O . PERMIT NO EFFLUENT/TOXICAN' DILUTION WATER. E R
INITIAL
T E S T IN IT IA T IO N D A i E
^ I l l / o i . -----------------
T E S T C O M P L E T IO N D A T E . # 7 7 <3 / ------------------
T E S T O R G A N IS M PH O TO PER 1C D
P Q r c r i t la ^ ffi-H nur D a v /3 -H o u r N ichj
L I G H T IN T E N S I T Y _ 5 Q - 1 Q.Q ft-C---------------------------
CLUONNDCCE NN T R A T IO N
SO ? p K
DAY 1
DAY 2
DAY 3
DAY 4
DAY 5
DAY 6
DAY 7
COMMENTS
pH D O. (mgIL)
.
Y -.r 1-5? T-.r I S
Temperature (C)
9.5 7 5
Conductivity (umhos/cm) 7)60
Hardness (mg/L- as CaC03)
7 .7 9 -f
75 7? as
307
1 ) 3 0 i l _ 75 YJ 73
7 5 73 75
3 W 3 /3 3 i-
Alkalinity {mg/L- as CaCOJ Analyst's Initials
FINAL pH D.O. (mg/L) Temperature (C) Conductivity (mhos/cm) Analyst's Initials
UTiO S lO / JrO L M D
JN T O
7 r5 7 3 7 7
O jo
7?
7 5 :*5 7 5
B n 3 i3 7 /5 J lc J UrLO U m
7 7 7 -5 7 7 7 5.0 3 - 7 K L -
75 15_ 3 3 | 33 6
J w t o ImD
____ 1 ----------- ------ A.-_- .
INITIAL
CONCENTRATION
7 S ' 7Q pn
DAY 1
DAY 2
DAY 3
DAY DAY 4, 5
DAY DAY 7 6
COMMENTS
pH D.O. (mg/L) Temperature (C) Conductivity Lumhos/cm) Tlardness (mg/L as CaCOJ
7? 7^ 75 3oo
77 7J 75 3^0
77 3 ?
77 7 * 7 5 15 397 Tv?
7 7 _o_ 1 9
1-s 7 ^ 7 Y b 7S
3 1 V 7 /3 3l4
Alkalinity (mg/L as 0aCO3)
Analyst's Initials
LmO
i m o U n j) < 7 7 35(3 LmO
FINAL
pH D O. (mg/L)
7- 7 3 7 7 GO 5 0 3 7
Temperature (C)
7 5 975 75
Conductivity (unhos/cm) 3 03 3I j ]|
Analyst's Initials
T O LmO UyP
N \T=MPLAoBBIOBENCH\a-iRONiaCHRONCHE WPO
7 3 7-55 .0 3 -9
05 5 7 /p 371
T O ftA
j-j-
73 70
K
Jri/7
3.7
35
370 5^?
R ev ise NGvemer 1. 200
Company Sanitized. Does not contain TSCA CBt
CHRONIC TO XIC ITY TEST
CHEMICAL ANALYSIS DATA SHEET
A
~"
Page H of 9
OLVER
L A B O R A T O R IE S g *
^
c l ie n t _ D i) , p n n h P B m L
JOB NO
( 3pjl T 5 ~
------------------
P E R M IT N O __________ EFFLU EN T/TO X 1C A N T
_
D ILU TIO N W A T E R : r J A PI /H J
ZU/Z/olT E S T IN IT IA T IO N D A T E
/ - ..____
l X l i o UT E S T C O M P L E T IO N D A T E X l M l O t
TE S T O R G A N IS M P 0rc,r\<~ltxs________
PHO TG PERIO O
1 6 -H o u r D a v /8 -H o u r N ight
L IG H T IN T E N S IT Y J 5 Q-.1QP ft-C.
IN IT IA L
1D A Y
C O N C E N T R A T IO N S O Pi?TM
2D A Y
DAY 3
DAY 4
DAY 5
6D A Y
DAY 7
COMMENTS
pH D.O (m g/L) T e m p e ra tu re (C) C o n d u c tiv ity (p im h a s/cm ) H ardness (m g/L as C aC O J A lk a lin ity (m g/L as C aC O J A n a ly s t' s In itia ls
72 7t V5 3oo
QP Uv)0
1 -9 1 -5 7 ? 1 1 2,o 7^ 1 1 1% I t l i 13 3 3
75 2 5 %5
25 i5
3 oo ,30> 3oT- 3J9 3)3 3 t L <a )0 7 l oV 91 I1 IO
(d3- (oT- (pQ (p0
i M LxrD LW SW Sp IM )
FIN A L pH D .O (m g /L ) T e m p e ra tu re (C) C o n d u c tiv ity (u m h o s/cm ) A n a ly s t's In itia ls
7 .5 1 3 7.3 v 3 7 3 1 -5
(p .O 3 5 U
3.2 3 A 7 7
1 5 1 5 2 5 ' l l 7 7 75
3)1 ?)I3. 315 331 3 7 I P 3x) LmO two S tl M LmO UnD
IN IT IA L
C O N C E N T R A T IO N
[ O V P!Y>
DAY
1
DAY
2
DAY 3
DAY 4
DAY 5
DAY
6
DAY 7
COMMENTS
pH D .O (m g/L) T e m p e ra tu re (C)
7r 15 21
C o n d u c tiv ity tim h o s /c m )
3 0
H a r d n e s s ( m g /L a s C a C D 3)
7 8 771 7 * ?3
7 7 I t l i 7-9 25 25 7 3
3 00 301 3 o l 3 )3
7.0 7 .9
73 7 * 75 35
3)3 3 W
Alkalinity (m g /L as C a C O J A n a ly s t's In itia ls
LM0 $7 N Lm o Lm D 5 ^ 7 T p " LlYlO
FIN A L
pH / . $ 7 3 . 7 3
D O (m g/L)
Cp o .3 7 . 7 3
T e m p e ra tu re (C)
35 35~
0
(Y ),
C o n d u c tiv ity p jm h o s /c m )
3S3 303
A n a ly s t's In itia ls
57/9 uvn Urrsf)
n \tem platbbiobENch \ch r o n !C',ch ronch e w fo
73 -7.3 3 0 3- ^ 7 5 xb 3 3 ? 311
Sfi
73 7 9
7 7 9-7 35
,923 377L/d D Lm o
Company Sanitized. Does not contain TSCA C tt
R evise N ovem ber 1. 2000
A. TEST FOR NORMALITY OF SURVIVAL DATA
T itle F ile
prom elas S u r v iv a l-2 /1 3 /0 1
T ransform
ARC S IN E (S Q U A R E R O O T ( Y i)
S h a p iro - W ilk 's T est f o r N o rm a lity
D= W=
0 1560 0 8233
C r i t i c a l W = 0 8 9 6 0 (a lp h a = 0 01 , N = 29) W = 0 9240 (alph a = 0 05 , N = 28)
Data FA IL n o r m a lity t e s t (alph a = 0 .0 1) T ry a n o th e r tr a n s fo r m a tio n .
W arning
1
The f i r s t th re e h o m o geneity te s ts are s e n s itiv e to n o n -n o rm a lity
and s h o u ld n o t be o e rfo rm e d w it h t h i s d a ta as i s
B. TEST FOR HOMOGENEITY OF VARIANCE
T itle
-File.
D u p o n t|H B H T o x ic ity -P
pro m e la s S u rv iv a l-2 /1 3 /0 1
~ T ransform
ARC S IN E ( S Q U A R E R O O T ( Y ) }
H a r tle y 's T e s t f o r H om ogeneity o f V a ria n c e B a r t l e t t 's T e s t f o r H om ogeneity o f V a ria n c e
These two te s ts can n o t be p e rfo rm e d because a t le a s t one g ro u p has zero v a ria n c e
D ata FAIL to m eet h o m o g e n e ity o f v a ria n c e a ssu m p tio n A d d itio n a l tra n s fo rm a tio n s are u se le ss
Olver Laboratories Incorporatrd
V 1J.16 South M ain Street
Blacksburg, V irginia 24060
Phone (540) 552-5548 FAX (540) 552-1715
q7
Company S a n itiz e d . D o e s not contain TSCA CBI
AryaAuS'S- C p m w i s . m 4 p S-VlrvW d GirA-g>\ S J
C. STEEL'S MANY-ONE RANK TEST
T itle F ile
GROUP
Dupont jB H jp T o x ic itv - P '
p ro m e la s S u r v iv a l - 2/13 / 0 1
T ransform
ARC S I N E (SQ UAR E ROOT (V) )
S t e e l's Manv-One Rank T e s t
IDENTIFICATIO N
TRANSFORMED
MEAN
Ho C o n t r o l- c T r e a t m e n t
RANK
SUM
C R IT . VALUE
SIG
DF 0 . 0 5
1
C e n tra l
1 3713
2
5 m g/L
1 3713
18 00
10 00
4 00
3
10 m g/L
1 3358
17 50
10 00
4 00
4
25 m g/L
1 3303
16 00
10 00
4 00
5
50 m g/L
1 4120
20 00
10 00
4 00
. 100 m g/L
1 4120
20 00
10 00
4 .0 0
7
500 m g/L
1 3713
18.00
10 . 00
4 00
C r it ic a l va lu e s a re 1 t a ile d ( k = S )
Olver Laboratories Incorporated 1116 South M am Street
sS Blacksburg, Virginia 2406
Phone 15401 552-5548 F-VX 15401 552-1715
58
Company Sanitized. Does not contain TSCA CB!
t^o-W ^.no.\u--?,i's ComoftivS.-'.n
Cqq-WoIS
A. TEST FOR NORMALITY OF GROWTH DATA
T itle F ile
Dupo:
o x ic ity -P
p ro m e la s G r o w t h - 2 / 1 3 / 01 T ransform -
S h a p iro - W ilk 's T est fo r N o rm a lity
NO T RANSFO RM ATIO N
D= W=
0 0809 0 9114
C r i t i c a l W = 0 8960 (a lp h a = 0 01 , N = 28) W = 0 9 2 4 0 ( a lp h a = 0 05 , N = 28)
D a ta PASS n o r m a l i t y t e s t ( a l p h a = 0 01) C o n t in u e a n a l y s i s
B. TEST FOR HOMOGENEITY OF VARIANCE
T itle F ile
D u p o n t, '
T o x ic itv -P
p rom elas G ro w th -2 /1 3 /0 1 T ransform
NO T RANSF O RM AT IO N
B a r t l e t t 1s T e s t f o r H o m o g e n e i t y o f V a r i a n c e
C a l c u l a t e d B1 s t a t i s t i c = 1 2700
(p -v a lu e - 0 9
D a ta PASS B1 h o m o g e n e it y t e s t a t 0 01 l e v e l . C o n t in u e a n a l y s i s
C r i t i c a l 3 = 16 8119 = 12 ,591c
(alph a = 0 01, d f (a lp h a = 0 05, d f
6) 6)
Olver Laboratories Incorporated I11S South Mam Street
si Blacksburg, Virginia 24060
Phone (540) SS2-BSAS FA X (540) 552-1715
59
Company Sanitized. Does not contain TSC CBS
|\riciAuS'5>- Cdrr\e>c^-( '.SnA ~T~o 'SA-ty-iAo./.d--
c. a n a l y sis of variance of dry w eight data
T itle F ile
Dupont
o ;tic ity -P
pro m e la s G ro w th -2 /1 3 /0 1 T ransform
ANOVA T a b le
NO TRANSFORMATION
SOURCE B e tw e e n W ith in (E rro r) T o ta l
DF 6
21 27
SS 0 0117 0 0809 0 0926
MS 0 0020 0 0039
F 0 5065
(p -v a lu e = 0. 7965)
C r i t i c a l F = 3 B117 *, = 2 5 7 2 7
(a lp h a = 0 01, d f = 6,21) (a lp h a = 0 05, d f = 6,21)
'S in c e F < C r i t l e a l F F A I L TO REJECT Ho A l l e q u a l ( a l p h a = 0 . 0 5 )
D. DUNNETT'S TEST
T itle F ile
Dupont
p ro m e la s G r o w th - 2 /1 3 /01 T ra n s fo rm
NO TRANSFORM AT ION
D u n n e tt' s Test
1
-
GROUP
ID E N T IF IC A T IO N
TABLE 1 OF 2
TRANSFORMED MEAN
Ho C o n t r o l T r e a tm e n t
MEAN CALCULATED I N ORIGINAL UNITS
T STAT
SIG 0 05
1
C o n tro l
0 .4 1 9 8
0 4198
2
5 m g/L
0 .4 6 B 3
'
0 .4 6 8 3
-1 1053
3
10 m g/L
0 .4 1 6 0
0 .4 1 6 0
0 0855
4
25 m g/L
0 4295
0 `4295
-0 .2222
5
50 m g/L
0 4415
0 4415
-0 4957
6
100 m g/L
0 3985
0 3985
0 4 B43
7
500 m g/L
0 4217
0 .4 2 1 7
-0 04 56
D unnett c r i t i c a l va lu e = 2 4600
(1 T a ile d , a lp h a = 0 05, d f [u se d ] = 6 ,2 0 )
(A c tu a l d f = 6,21)
Olvcr Laboratories Incorporated
V 1116 South Mam Street is Blacksburg, V irginia 24060
Phone (540) 552-554S FAX (5401 552-1715
C mPani'
60
D o noi c o n u m y o ,, - ,
Qo-Vo, ^oaW S'S- irT\-)Q<{
Gcu->~Y>o\ S
T itle F ile
D u p o n t - f g & r o *x i c i t y - P
'
D rom elas G ro w th -2 /1 3 /0 1 ' T ra n s fo rm
NO TR AN SFO R M ATIO N
Dunnett's Test
T A B L E 2 OF 2
Ho C o n t r c l c T r e a t m e n t
GROUP
ID E N T IF IC A T IO N
NITM OF REPS
MIN SIG DIFF (IN ORIG UNITS)
% OF CONTROL
DIFFERENCE FROM CONTROL
C o n tro l 5 m g/L
10 m g /L 25 m g /L 50 m g /L 100 m g /L 500 mg/ L
4 4 4 a
4 4 4
0 1079 0 1079 0 1079 0 . 1079 0 1079 0 1079
25 7 25 7 25 . 7 25 7 25 7 25 7
-0 .0 4 8 5 0 0038
-0 0097 -0 0217
0 0213 -0 0020
l
INHIBITION CONCENTRATION (IC25) ESTIMATE
T itle F ile
Dupont
ic ity -P
GRP
ID E N T IF IC A T IO N
1 C o n tro l T 5 m g/L
3 10 m g /L 4 25 m g/L 5 50 m g /L 6 100 m g/L 7 500 m g/L
prom elas G ro w th -2 /1 3 /0 1 T ransform
NO TRANSFORMATIO N
MEAN
SMOOTHED MEAN
CONCENTRATION
0 4198 0 4583 0 4160 0 4295 0 4415 0 39B5 0 .4 2 1 7
0 .4 4 4 0 0 .4 4 4 0 0 4290 0 4290 0 .4 2 9 0 0 4101 0 4101
0 0000 5 0000 10 0000 25 0000 5 0 .0 0 0 0 1 0 0 .0 0 0 0 500 0000
IC p e s tim a te w itn p =
25 i s >
500 0000
O lvcr Laboratories Incorporated
V 1116 South Mam Street
Blacksburg, Virginia 24060 Phone 1540J 552-5548 F \ X (540) 552-1715
61
Company Sanitized. Does not contain T 5CACBV
QoVc kncc\TuJc/.s - Caom o a . f \ e. ,>n ~Vt! fsOlg.~Wia.no\ C-C.o'VvpIs A. TEST FOR NORMALITY OF SURVIVAL DATA
T itle F ile
E u p o n ti
T o x ic ity -P
prom elas S u r v iv a l-2 /1 3 / 0 1
T ransform
ARC S IN E (S Q U A R E RO O T ( / ) )
S h a p iro - W ilk 's T e st fo r N o rm a lity
D= W=
0 1627 0 B62 5
C r i t i c a l W = 0 3960 (a lp h a = 0 01 , N = 28} W = 0 9240 ( a lp h a = 0 05 , N = 28)
D ata FA IL n o r m a lity t e s t (a lp h a = 0 01) T ry a n o th e r tr a n s fo r m a tio n .
W arning l
- The f i r s t th re e h o m o g e n e ity te s ts a re s e n s itiv e to n o n -n o rm a lity and sh o u ld n o t be p e rfo rm e d w ith t h is d a ta as is
B. TEST FOR HOMOGENEITY OF VARIANCE
T itle F ile
Dupont
T o x ic it'.
p rom elas S u r v iv a l-2 /1 3 /0 1
T ransform
ARC SINE(SQ UARE R O O T(Y ))
H a r tle y 's T e s t f o r H o m ogeneity o f V a ria n c e B a r t l e t t 's T e s t f o r H om ogeneity o f V a ria n c e
These tw o t e s t s can n o t oe p e rfo rm e d because a t le a s t one g ro u p has
zero v a ria n c e
.
D a ta FA.IL t o m eet h o m o g e n e ity o f v a r ia n c e a s s u m p tio n A d d itio n a l tra n s fo rm a tio n s a re u se le s s .
Olvcr Laboratories Incorporated 1116 SoutU M a m Street Blacksburg, V irginia 24060 Phone (540) 552-5548 FAX (540) 552-1715
62
Company Sanitized. Does not contain TSCA CB1
C. S T E E L 'S MANY-ONE RANK TEST
T itle F ile
D upont^^j^N ^ci
p rom elas S u r v iv a l-2 /1 3 /01
T ransform
ARC S I N E [ S Q U A R E R O O T I Y ) )
S t e e l 's M any-One Rank T e s t
- Ho C o n t r o l T r e a t m e n t
GROUP
ID E N T IF IC A T IO N
TRANSFORMED MEAN
RANK SUM
CRIT VALUE
DF
1 C o n t r o l w / MeOH 1 3 3 0 5
2
5 m g/L
1 3713
20 00
10 00
4 00
3
10 m g /L
1 3358
19 00
10 00
4 00
4
25 m g/L
1 3305
13 00
10 00
4 00
5
50 m g /L
1 4120
22 00
10 00
4 00
6
100 m g/L
1 .4120
22 00
10 00
4 . 00
7
500 m g/L
1 3713
20 00
10 00
4 00
C r it ic a l v a lu e s are 1 ta ile d ( k = 6 )
i
Olver Laboratorios Incorporated
V y 1116 South Mam Street
Blacksburg, V irginia 24060 Phone (540) 552-5543 FAX (540) 552-1715
63
Company Sanitized. Does not contain TSCA CB1
A . TES T FOR N O R M A L IT Y OF GROWTH D ATA
T id e F ile
Dupont
H
T o x ic i t y -?
p rom elas G ro w th -2 /1 2 /0 1 T ransform
P!
S h a p iro - W ilk 's T est f o r N o rm a lity
NO TRANSFORM AT ION
D= W=
0 0799 0 9735
.
C r i t i c a l W = 0 .8 96 0 (a lp h a = 0 01 , N = 28) W = 0 .9 2 4 C ( a l p h a = 0 05 , N = 28)
D a t a PASS n o r m a l i t y t e s t ( a l p h a = 0 0 1 ) C o n t i n u e a n a l y s i s i
B. TEST FOR HOMOGENEITY OF VARIANCE
T itle F ile
Dupont
T o x ic ity -P
prom elas G ro w tn -2 /1 3 /01 T ransform
NO TRAN SF ORMAT ION
B a r t l e t t 's T e s t f o r H om ogeneity o f V a ria n c e
C a lc u la te d B1 s t a t i s t i c = 1 1848
(p -v a lu e = 0 9776)
D a t a P.ASS B 1 h o m o g e n e i t y t e s t a t 0 01 l e v e l C o n t i n u e a n a l y s i s
C r i t i c a l B = 16 8 1 1 9 = 12 5 9 1 6
(a lp h a = 0 01, d f = 6) ( a lp h a = 0 05, d f = 6)
Olver Laboratories Incorporated 1116 South M am Street
CS Blacksburg, V irginia 24060 Phone (540) 552-5548 FA X (540) 552-1715
Company Sanitized. Does not contain TSCA CBI
fr.nc-\uS'S- Coro-QC-.rX'vOri -Vo yog.TVxQ.n\ Cco~Vvp\^,
C. ANALYSIS OF VARIANCE OF DRY WEIGHT DATA
T itle F ile
D u p o11n t 4 | ^ ^ ^ T ooxx :i c i t y - P 1P a
p ro m e la s G ro w th -2 /1 3 / 0 1 T ranstorm
AMOVA T a b l e
NO TRANSFORM ATION
SOURCE B e tw e e n W ith in (E rro r) T ota l
DF 6
21 27
SS 0 0131 0 0799 0 0930
MS 0.0022
0 0038
F 0 5754
(p -v a lu e = 0 7456)
C r it ic a l F = 3 8117 ^ = 2 5727
la lp h a = 0 .0 1 , d f = 6,21) (alph a = 0 05, d f = 6,21)
' S i n c e F < C r i t i c a l F F A I L TO R E J E C T Ho. A l l e q u a l ( a l p h a = 0 0 5 )
D. DUNNETT'S TEST
T itle F ile
D u p o n t.
T n : o r.t t v - P
prom elas G ro w th -2 /l3 /0 1 T ransform
NO TRANSFORMATION
Dunnett's Test
TABLE 1 OF 2
Ho C o n t r o l : T r e a t m e n t
GROUP
IDENTIFICATIO N
TRANSFORMED MEAN
MEAN CALCULATED I N ORIGINAL UNITS
T STAT
SIG 0 05
1
C o n t r o l w/MeOH
0 4068
2
5 m g/L
0 4683
3
10 m g/L
0 4160
4
25 m g/L
0 4295
5
50 m g/L
0 4415
6
100 m g/L
0 3985
7
500 m g/L
0 4217
0 4068 0.4683 0 4160 0-4295 0.4415 0 .3 9 8 5 0.4217
-1 4X03 -0 2121 -0 5217 -0 .7969
0 . 1892 -0 .3440
D unnett c r i t i c a l v a lu e = 2 4600
(1 T a ile d , a lp h a = 0 .0 5 , d f [u se d] = 6,2 0)
(A ctu a l df
6, 21)
Olver Laboratories Incorporated 1116 South M am Street
Blacksburg, V irginia 24060 Phone (540) 552-5548 FAX (540) 552-1715
g5
Company Sanitized. Does not contain TSCACBI
p g -t^
Cn.^r.C'ivsr,n ~T0 m sioano\ C.rWs .
T itle F ile
Dupont
*6
x ic ity -P
prom e_as G ro w th -2 /13/0 1 T ransform
NO TRANSFORMATION
D u n n e tt's Test
'ABLE 2 CF 2
Ho C o n t r o l - : T r e a t m e n c
GROUP
ID E N T IF IC A T IO N
NUM OF REPS
M IN SIG DIFF ( I N ORIG UNITS)
% OF CONTROL
DIFFERENCE FROM CONTROL
C o n t r o l w/MeOH 5 mg/L
10 m g /L 25 m g/L 50 m g /L 100 m g/L 50Q m g /L
4 4 4 4 4 4
4
0 1073 0 1073 0 1073 0 1073 0 1073 0 1073
26 4 26 4 26 4 26 4 26 4 2 6 .4
-0 0615 -0 0093 -0 0228 -0 03 4 8
0 0082 -0 0150
INHIBITION CONCENTRATION (IC25) ESTIMATE
T itle F ile
D u D cn t ^B B *T Q icici ty - P p ro m e la s G row th- 2 /1 3 /0 1 T ransform
NO TRANS FORMATIOt
GRP
ID E N T IF IC A T IO N
MEAN
SMOOTHED MEAN CONCENTRATION
1
C o n t r o l w/MeOH
0 406B
0 .4375
0 0000
2
5 m g/L
0 4683
0 4375
5.0000
3
10 m g /L
0 4160
0.4290
10.0000
4
25 m g /L
0 4295
0 .4290
2 5 .0 0 0 0
s'
50 m g /L
0 4415
0.4290
5 0 .0 0 0 0
6
100 m g/L
0 3985
0.4101
1 0 0 .0 0 0 0
7
500 m g/L
0 4217
0 4101
5 0 0 .0 0 0 0
ICp e s tim a te w it h p = 2s is > 500 0000
OWer Laboratories Incorporated 1116 South M am Street Blacksburg, Virginia 24060 Phone (540) 552-5548 FAX (540) 552-1715
66
Company Sanitized. Does not contain TSCA C81
APPENDIX 7
CHRONIC TOXICITY TEST DATA Ceriodaphnia dubia
67
Company Sanitized. Does not contain TSC CB1
OLVER
la b o r a t o r ie s
OLVER LABORATORIES INCORPORATED ENVIRONMENTAL BIOLOGY LABORATORY
CLIENT TOXICANT/EFFLUEN
TEST SUMMARY SHEET
JOB NO _ PERMIT NO
105 MM
PAGE
OF
ACUTE TOXICITY TEST RESULTS
c h r o n ic lo x ic iiY rEST RESULTS
Ceriodaphnia Fathead Minnow
Ceriodaphnia
TFvST DATEfS}
0 --z li-il* 1
TEST CONDITIONS TFST O R G A N IS M A G F nil 1ITIDNl WATFR
SOURCE AERATION
FPA-MHW OLVER LABS
continuous
EPA-MHW OLVER l.ABS
continuous
/ ` DILUTION WATER
SOURCE AERATION
l - f i I'X'S. EPA-MHW OLVER LABS continuous
TEST ACCEPTABILITY CONTROL SURVIVAL (a90%)
CONTROL SURVIVAL (2 80%) NO OFCONTROLFEMALES
% CONTROL FEMALES WITH 3 BROODS (2 6 0 %)
t o o '/
10
lo /
Fathead Minnow
EPA-MHW Ot.VER LABS
continuous
AVE NO YOUNG/SURVIVING FEMALES (2 15)
18 -0
AVE WT/SURV CONTROL ( 2 0 25 mg)
STATISTICAL RESULTS SURVIVAL IN 100%
1L^c50,,
qr% r i METHOD
SURVIVAL IN HIGHEST ( Soo yj CONC NUMBER OF REPLICATES NUMBER OF ORGANISM/REPLICATE NORMAL DISTRIBUTION? HOMOGENEOUS VARIANCE? NOEC METHOD NOEC SURVIVAL NOEC REPRODUCTION/GROWTH R<;PYoci o/l/CrVO
Ho/
to
1
Yti S No- S bunfl P/H '5 S loo "' Pi/L lo ma h_ o f loorf^y L*-
> 5 o o mfl/L
G G G
COMMENTS
h i
g. non- Cji/iAiositos,
<nUr>t
__r cjfan^L
n o \ c . on^g c k -2-5 itx-Ml, g A i:_ c /> W h b r, 5 a s - iA un 1 U . o '3 iU 'J f c h 'llA J p i
_Ajic%JLu. Q-fA \o'Q--r
! - tv ^ - Kln&C )> bg-liJH<* A o b g .
M W EM PLM eW O D EH CH 'BK M O M im T CSTSU M W rO
A
Sggi f i W
VHl-----
P v ^ r ^ S f l U . A ' A ----R f f t
< ^ c u ic,-k Ih r*-?1
d -ir------l u 0 m 3 /* R evised M arch 21, 2001
Company Sanitized. Does not contain TSCA CBI
OLVER LABORATORIES INCORPORATED ENVIRONMENTAL BIOLOGY LABORATORY
CLIENT TOXICANT/EFFLUENT
TEST SUMMARY SHEET
JOB NO
La0 n 5 ___________ PAGE I O F ___ L
PERMIT NO
N/A______________________________
TFRT DATFS1
ACUTE TOXICITY TEST RESULTS Ceriodaphnia Fathead Minnow
CHRONIC TOXICITY TEST RESULTS Ceriodaphnia 2/ z d - T / m / o)
TEST CONDITIONS | TEST ORGANISM AGE
DILUTION WATER SOURCE AERATION
TFST ACCEPTABILITY CONTROL SURVIVAL (90%)
PA-MHW OLVER LABS
continuous
EPA-MHW OLVER LABS
continuous
TEST ORGANISM AGE DILUTION WATER
SOURCE AERATION
V" CONTROL SURVIVAL (80%)
NO OF CONTROL FEMALES
% CONTROL FEMALES WITH 3 BROODS (60%)
i --ft h rs . EPA-MHW OLVER LABS continuous
BO/
.IQ____
Fathead Minnow
EPA-MHW OLVER LABS
continuous
AVE NO YOUNG/SURVIVING FEMALES (15)
5 , ____
STATISTICAL RESULTS' SUFlVlVAL IN 100%
LC,,
95% C i
METHOD
f
I
l _______________________________
C O M M E N ^ S ^ ^ L C p r X ^ \ U c A < ! / ^ ua'T c
AVE WT/SURV CONTROL (0 25 mg)
'nvW .nO \
SURVIVAL IN HIGHEST l 5nn -w J CONC
NUMBER OF REPLICATES NUMBER OF ORGANISM/REPLICATE
NORMAL DISTRIBUTION? HOMOGENEOUS VARIANCE? NOEC METHOD NOEC SURVIVAL NOEC REPRODUCTION/GROWTH
H o/.
1o
1
V.s S
NO S
S-kLS
S
too "'3/l.
loo "Wl
d>" 3 /i
f ^1 -AXL Q-
pt-r I L ' V
riituVion oJaV-v-V
'
G G G
l?\|FMI,LAiE\UIODENCinOIOADMIIATESTSUMNATO
R e v is e d M a rc h 21 2001
Company Sanitized. Does no! contain TSCA CSJ*
OLVER
LA B O R A T O R IE S
AQUATIC TOXICITY TEST SAM PLE USE SHEET FOR STANDARD SYNTHETIC DILUTION W ATER
Client tXpan-b
_________ --
Effluent/Toxicant
Synthetic Dilution W ale ^^^F/vM oderatelv Hard Water fMHW)
Testing Requirements
___________ 18-Hour Acute Ceriodaphnia Test
I __________ _ 10-Hour Acute Fathead Minnow Test
___________ 96-Hour Acute Fathead Minnow Test
Job Number
_________
Permit No 'N/A
Page
___________ 7-Day Chronic Fathead Minnow Test
______ X
3-Biood Chronic Ceriodaphnia Test
___________ Other_____________________________
I of I
TEST DAY Carboy No /Identification
1 4F3
Preparation Dale
2) Id I
Time & Day of Use
l am{0 Z /2 i) / f?|
Age of Dilution Waled11
1 tw y
Alkalinity' (mg/L) (Acceplable Rariqe 60-70 nig/L)
0 if
Hardness (mg/L) (Acceplable Range 00TnOmn/l 1 Conduclivitv (i/mhos/cm)
pH Total Residual Cl; (mg/L)
D 0 (mg/L)
Aeralion
/Do
33) (e 'T-ff ND` 78
Conlinuous
2 /d-3 i n oi
3 a jfcfloi
4 ff M
2 I1) 0 1
5 a j i t /oi
|3gpt/pm2 /2 1/O 1 j j 1 "a m / 7- / 22. / 0I ff^anlf&X / /o 1 ,l3 S>fpm'2 / ^ 0}
2 da-Lfi
3 clo.^ s
7 daq i
5 cRy r
\00
38 ND
?& Continuous
lo o
l-s ND
1-8 Conlinuous
Lt
n 3 ii `-I <?
ND
Contlpuous
6=5
Ta
3 151 / ND 18 Continuous
6 T tq
iff 1
7 f* 3-
, ^ / W 01 ^ a m ( ^ 2 7-1*! 0 t
Y cV > 4 5-
(j) ?
n
3 15 8 .0 ND 7J Conlinuous
L>o
1 oO
32S 7 S'
ND 7 -Y Conlinuous
C O M M E N T S h i S y n th e tic d ilu tio n w a le r is p re p a r e d w ith la b o ra to ry d e io n iz e d w a te r a n d r e a o e n l g ra d e c h e m ic a ls fE P A /O O O /^ -O I/O O Z ) (21 E a c h b a lc h of d ilu tio n w a e r r s n o t u s e d for m o r e th a n 14 d a y s fo llo w in g Ih e p r e p a r a t io n d a le _______________________________________________
` N O = N o t D e le c t a b le __________________________ :_______________________________________________________________________________________________________
OLVER
LABORATORIES
Cenodaphnia dubia
S U R V IV A L A N D R E P R O D U C T IO N R E C O R D
C L IE N T P E R M I T N O ___________ E F F L U E N T /T O X IC A N T
B P Pi
P H O T O P E R IO D 16 hr D a y /8 hr N ig h t
C O N C E N TR A TIO N
REP
\Q. '.S u r v iv a l
------
1 (A)
?/ m
C^c\\r<o \
3 (Ci 4 (D) 4 /F* 5 (F)
7 (G i 8 {HI
J TOTAL
10 (J)
_
Day 1
o
o
0
o
0 0 0 0 0 0 o
Day 2
0 O o o o o 0
o
o
o
0
JOB NO
C<?n5__________ __
PAGE i
o f --A --
TEST ORGANISM AGE
K w.n )
START o f TEST gfc. .A M _ Z _ / _ Z o / j N _
END of TEST 3 A M J g J tfIZ _ L Z 5 L/j2-1_
------------------_________________________ ______________________ r
--------- j
R E P R O D U C TIO N C O U N T/D A Y
Day 3
o o o o 0 o o 0 o o
0
Day 4
L-14
Day 5 0'
Day 6 q
O
5 O8
o8
7o
i 1 8*
A
7
S'
*7
H -
7 7`
5?
3 zq
o o o
o
m
Day 7
H l*
H
- J L __
5"
\* ii
q
1z If
_ 7 l_
TOTAL
COMMENTS
IX -
7
1
T E S T SO LUTIO N V O L U M E 15 ml T E S T C O N TA IN ER
5 n
a/
S IZ E 30 ml
FE E D IN G 0 1 ml TYC +
.1 2 -
ST/go
0 1 ml A LGA E/D A Y
H \c?Winr^.S
C O N C E N TR A TIO N
^ O% S u r v i v a l
Cc*y4yoi
/
1
]V\tDriOVAcio\J\
_____________ T O T A L
RHP
1 (A) 2 (B) 3 iC ) 4 (Di 5 (E) 6 (Fi 7 (G 8 (H
9(H
10 (J)
Day 1
O O o 1X
n o
n o
o 0 0 0
Day 2
O 0
__
o o o o o 0 0 0
R P P R O n ilC T IO N C O U N T/D A Y
Day 3
Day 4
Day 5
Day S Day 7
O <3 Lp f o 5 o Ip
._ __> -- --
O7 0
q
0 7 7 q- u
n 3 b> o
2
(O 3
7o
q
n 7 L> o
1o
c H7 o
o
0 7O5 3 0 3> a l 3o J l _
TOTAL
17 0 17 aSL n
n
ao
11
IOL _m _
COMMENTS
C O N C E N TR A TIO N
%S u r v i v a l \oO
REP
Day 1 Day 2
1 (A) 2 (Bi
5 3 (C)
4 (D 5 (E) S IF) 7 (G) 8 (H)
9 ID 10 /J1 TOTAL
____________A N A L Y S T ____________
0
o 0 0
0 D
0
0
o
0 0
L
0 0 0 0 0
o 0 o c o 0
HA'
N \TEMP'_ATE\5lOBENCH\CHRONIC.COReROD WPO
R E P R O D U C TIO N C O U N T/D A Y
Day 3
Day 4
Day 5
O S 5
o5
o
0 *7 o
-q -
o
I
0 7 c?
0 HA
o 77
0 77 0 3 C0
07
o vi as
Sud -5 t? a
Day 6
2
If
fp
? Y
0
n n 0
0
3H
Mf
Day 7
H Lo
Lp b b
9
8q
i b
(p(3
r
TOTAL
/7 7 ._ / 3 /7 D /7 /? /7 /6
Ito
COMMENTS
=X D EAD
- = D IED P R E V IO U S LY
=#S/X O F Y O U N G
PRODUCED BEFORE A D U LT DIED
Sgls]
Resisea 'une CO -000
71
Companyifmmlzed. D oes noi containTSCA CBi
C a n a d a p h rv a d u b ia
SURVIVAL AND
REPRODUCTION RECORD
Ol_^.LaOfVtATEQBlRES
C L IE N T _ J > U 2 2 n i - i
P E R M IT N O _ ------- t lr t
E F F L U E N T /T O X 1 C A N T
D I L U T I O N W A T E R -----P---P-- A
mmu
JOB NO
oH 5
_____T E S T O R G A N IS M A G E .
AM/l^^i A^2-0!LS T A R T of T E S T / :3 Q .
PAGE
3T
P.1M h f S C th-,* hr
E N D of T E S T 3^ KWlfik J _ j2 3 J -
)
punfnPFRIOO 16 nr DaV/B hr Nl9hl
REPCONCENTRATION
^rinval^O--
Day 1 Day2
1 (A) o J2_
O2 (Bl
!L> mf)A_
OJSL
4 IDI
(0 O
o
o
_LL
6(FI J2_ 07 (G)
J2_
o
_Q _
8(HI 0
9(II o
o
REPRODUCTION COUNTVOAY
Day 3 Day 4 Day5 Day6 Day7 o 1T T
j 2_ 5 5 <9
o
H
oo
3HO
G ' (o O
o o
M3
3
3
8 o
3
o
G
3
II to
o J2
H-
TOTAL
COMMENTS
"1 3 " i(c
13
11
11
/9
SL ~7T
TEST SOLUTION VOLUME 15 ml
TPSTCONTAINER
SIZE 30 ml
FEEDING 0 1 mi 'P 'C -
0 1 mi ALGA0OAY -
J1 aI
Tom--
CONCENTRATION RHP "/.Survivai=`TO
REPRODUC3T1DNCOUNT/DAY
Day1 R
Day2 o
Day3 p
Day4 w
Day5 DayS ---
Day7
l
")m\ O o f. H o Lp 3
Z3 m3/i.
fi fFt
" ,'
o
o
o
o
0
o
0
n3 O <3 03
O o
H (r
<9 /r
o o
h--
f) o / 3 ? o
7(G 0 0 o ~~j= r 9> 1 L
cfW\ o 0 o 3 A
o %
0 0 o 3 "IT - O 2.
10(J) o o 0 4
1 10
TOTAL_
0 o o 3# m 19 38
TOTAL
IX Id cl
_1Z_ /G / 2/v
18 II I e! 13 e!
COMMENTS
CONCENTRATION REP ASurvival0
REPRODUCTIONcount/day Day1 Day2 Day3 Day4 Day5 DayS Day7
TOTAL COMMENTS
1(A) o 0 o
2fBl o O o
3o ^5/l-
3fC 4.(D
0 0
0o 00
5(El o O 0
S(R o 0 0
7fGl o O 0
S/H 0 O n
9(H o 0 0
10fJl o TDTAf o
00 0o
___ ANALYST------- li) HA I U-ft"
N.\TEWPLATBBiOBNCH\CHRONiCvCDREPRODWPO
o 5o 0? o
(& ro
5o
W0 G (e
l
er 3
3
a/ J-k'3
{? 3 1r
b3
15 3 3._ (9 L /X
Z. 9
03 4 0// to/t 36) zA 6Lb
1 .2 11
X=DEAD
15
1 G - =DIEDPREVIOUSLY
5
i,'X=FOFvOUNG
53 PRODUCEDBEFORE
<9... ADULTDIED
Il
/7
15 3."
15M
Revised June 20 2000
7?
Company Sanitized. Does not contain TSCAC81
Ceriodaphnia dubia
SURVIVAL AND
REPRODUCTION RECORD
OLVER
l_ABOfrATOR<eS
JOB NO
k 0n5_
PAGE
of 3 .
C L IE N T _ _ D ii it = .
t e s t o r g a n is m a g e .
-Ozy h f S
? A'/-J
P E R M IT N O e f f l u e n t /t o x ic a n t
_
r-ui I iT in w W A T E R __EPf\ '71
S T A R T o f T E S T / '-3Q_ A M
E N D of T E S T _J_L
AM
L
A. / z ? / O >
PHOTOPERIOO 16 hr Dav/8 hr Night
.... ....................-- ----------------
CONCENTRATION REP r-t Q
Day 1
Day 2
Rf;produc TON COLNT/UA Day 3 Day 4 Day 5 Day 6 Day 7
TOTAL
COMMENTS
*/ Slir\MYfll=
-----1 (A)
Jl i
0 _ Q _____ Q ____ ?
O (J - o 5 5
Q
Os
o o 0 h* 5
<2__ O O
O. 9 /x 7 /x
//
<39H / 3
ao
t c " T pni i mnw VOLUME 15 ml TEST CONTAINER SIZE 30 ml
/ On rf'.ci h -
Q O o 5 S 0s
/7
o 0 o V3
O IO
; 9 FEEDING
1 4O 0
o0
S
O 0 VV
0? 0 o /x
l L 0 1ml TYC Q1 ini ALGAE/DAY
i
___________ _ J _________ IQ IAL----
10 (J1
0
o Q
o o o
D *7 .3 0 U
O3
oq
9 3 HS o
t\
15 "7 T T
CONCENTRATION REP %Survival 4 0
5 o o --R5/^
q (F) " C(F
7 (G) 9 fH) q fn 10 (J| TOTAL ...
Day 1
o o 0
O
o
0 o
o o 0 0
Day 2
n
o o 0 o 0
0 0 0
o
___ _
Day 3
o o o o 0 O 0 o 0
D
0
FHPRODUCTION COUNT/DAY Day 4 Day 5 Day 6 Day 7
3
OH
//
S 5 o IZ
5
OH
L
S' 5 Ofx --
-/ o
3 5
3 (5 o 7 / *
F3
S6
*7 t o 75
33
3 ? /y
o jofo
o 9/y
o /o / x
/S ~ T T
. TOTAL
COMMENTS
15 / (7 /G
\
17 ----------- -
m
. ...
-
j
1
CONCENTRATION REP Survival
RFPRnnncTION COUNT/DAY Day 1 Day 2 Day 3 Day 4. Day 5 Day B Day 7
TOTAL
COMMENTS
1 (A) 2 (B 3 (C 4 fDl
X= dead --= DIED PREVIOUSLY
5 (El tt/X = FOF YOUNG
G {Fi
FRODUCED BEFORE
3 (H)
9 (I)
10 (J!
TDTAI
ANALY5T ....
a
N\T.MPLATE'.B'OBNC'H\CHRCNIOCDREPf:?QD'*
OA
ilA 1
D t \ l S L fy 5U3
AOULT OIFD
sygfE
.
-------- ---------- ----
Bompmy Si,llfe,d. Bo m noi c 0 ,,,aln TSC CBI
CHRONIC TOXICITY TEST
CHEMICAL ANALYSIS DATA SHEET
page I o f _7_
OLVER
l a b o r a t o r ie s
CLIENT _ D ^ f c-0.jp-
JOB NO
Cp .13
PERMIT NO _______
EFFLUENT/T0X1CANT
DILUTION WATER
EPS m H uj
INITIAL
DAY 1
DAY 2
DAY
3
pH
D O. (mg/L) Temperature (C)
Conductivity (^m hos/cm )
Hardness (mg/L as CaCOJ >
Alkalinity (mg/L as CaCOJ
A nalyst's Initials
7 .8 7 -8 z5 3 2 ,4
l8 12 " I S' 23.L
5 m SL&
12 7
aS 33C
SLft
FINAL pH D.O (mg/L)
75 7H
T -3 1M
11 H -T
Temperature (C) C onductivity (mhos/cm) Analyst's Initials
3S3 6L
ys 353
5l 6
tS 377 SUb
DAY
4
78 78 i5 3 i5
TEST INITIATION DATE
,_j-_T_-a__I nl
TEST COMPLETION DATE z / l ^ J p A
TEST ORGANISM C m r A n i/mm duhi c, ____
PHOTOPERIOD
16-Hour Dav/B-hour Niqnl
LIGHT INTENSITY 50-100 rt-C
)
DAY DAY DAY
56
7
COMMENTS
7 1 fo
7
3 .5 3
1-1 7 5 2.5 3 15 3 2 8
sUS 52-N $Y/J 5L&
7 5 7 -1
35 347
3au
7U LA
L -X
25
337- SH
A-
INITIAL
DAY 1
PH .
1-8
DO. (mg/L)
78
Temperature (C) Conductivity (pmhos/cm) Hardness {mgTLas CaCOa)
2-5
100
Alkalinity (mg/L as CaCO.)
Analyst's Initials
.5m
FINAL
pH 7 3
D.O (mg/L)
7-7
Temperature (C)
2.S
Conductivity (^mhos/cm) 383
Analyst's Initials
aL
DAY DAY DAY DAY DAY DAY 7 2 3456
7 S 7 - 7 ? 7 f ? 0 7 ?
7 ? 7 f i ? 7 ? - 1-8
2.5 2.S' IS 7 5 7 5 as
33b 33L. 31S' 3 15 3 * 5 3 3.5
100 joo 1
7T 33. DO
l/M lh I'TLz (j3O' k>2 L0 ~-
SlIS L& SeN
SLiS
7 7-7 7 .4 7 . cl 7 H 7 7 (fi-1 7 .0
xS IT 2 5 7 5
358 377 377 375 SL&- US T 4 n 3(?7
7-0 57
25 32V 6L&
7-L L -7
337
COMMENTS ~Vyfa-n1*C-nWch4___ -
74 C o m p a n y S a iTffeecf. Di o e s m l co p a r i t A C B !
CHRONIC TOXICITY TEST
CHEMICAL ANALYSIS DATA SHEEi
Pase ~Z- of 3
O LV ER
L A B O R A T O R IE S
CLIENT _ P uf
JOB NO
fr t
P E R M IT N O __________
E F F L U E N T /T O X iC A N T
D IL U T IO N W A T E R : _
EPP m H P
TEST INITIATION DATE __ - f c - Q IjO-
TEST COMPLETION DATE / 2 3 .Q J ---------------
TEST ORGANISM V n o d c p hni& rii, hm ,----------
PHOTOPERIOD
1S-Hoiir Dav/g-Hour Night
LIGHT INTENSITY 50-100 ft-C
INITIAL
DAY 1
pH
D.O. (mg/L) Temperature (" C ) Conductivity 0-imhos/cm) Hardness (mg/L as CaCOJ
7 -8 7 -8 z5 354
DAY 2
3 S' 3? 1?
33L
DAY 3
3? 3f 05 33L
DAY
4
3? 3? 25
3(5
DAY 5
DAY 6
DAY T
7 .7 7S
3 15
0
7J
25
315
32 3? 25 32?
COMMENTS
A lka lin ity (ng/L as CaCOJ Analyst's Initials
FINAL
pH
D.O. (mg/L) Temperature (C) C onductivity (mhos/cm) Analyst's Initials
INITIAL
PH
D O. (mg/L) Temperature (C) Conductivity (^mhos/cm) "Hardness (mg7L as CaCOJ
5m
SL&
SU5 $L(V i f c f J i r J
33 8H
25 3SH SLB
38 74 7-5 353 53
3 3 7W
7 -3
31 25
7 9 - 7 .O 3 -5 3 -5
337 337
SU5 5 i t J
3L U3 25 32S SL5
DAY 1
CONCENTRATION
DAY 2
DAY 3
DAY
4
(Ti ^ / l
DAY 5
DAY 6
7 -8 7-8
2 -5
79 38
2 .5
3 ? 7 P 7 e! O
3 S 1 8 7.? 7 .2
3.5 3.5
V?
3 3 L 3i 5 3 i 5 3 i 5
SL
r.L 45 25 335 SUY
---------------- --- ------
DAY T
COMMENTS
7
3- 25
325
, -T7]
A lk a lin ity (m g /L as C aC O J
A n a ly s t's Initials
L5m
4L&
FINAL pH
33 33
D O (m g/L) T e m p e ra tu re (C )
3H 3H
as" l 5
Conductivity (ymhos/cm)
353
A n a ly s t's In itia ls
AL&
C&
U \TEMPlATBBIOBENCH\CKRONIC\C.-lRONCHE WPQ
SL l /5 5 & J S/7 5L
3- 1 3' 2-5 373 st&
7 .5
7. 0 25
1,3
l.o 9 -5
3L L8 3b
345 337. 333
527
U Jy
7P Ir ? 25 33? SL
.s.
Revise Novem ber 1 2000
75 Company Sanitized. Does not contain TSCA CBI
CHRONIC TOXICITY TES i CHEMICAL ANALYSIS DATA SHEET
pase "5 of 1
O LV E R
L A B O R A T O R IE S
CLIENT __D w f on-Vg!
JOB NO
Oc 1.1
PERMIT NO EFFLUENT/TOXICANT
DILUTION WATER. ----
:Pf /TNnL*J
TEST INITIATION DATE.
_feo .IoL
TEST COMPLETION DATE, x ' f el 1oI
TEST DRRANISM P?nndo nhn,a. duba-______
PHOTOPERIOD
1fi-Hour Dav/8-Hour Night
LIGHT INTENSITY 50-100 ft-s_
INITIAL
DAY DAY DAY DAY DAY DAY DAY 123 4 567
pH D O (mg/L) Temperature (C) Conductivity [umhos/cm] Hardness (mg/L as CaCOJ
7 -8 7 -8 *5
TS ? x5 33 L
1'S
T? 33L
3 3 "? 7 }7-?
2,5 7 6 3lS 3 i 5
X .o 7S 7$
3 IE
8S 1-3 a? 325
Alkalinity (mg/L as C aC03) Analyst's Initials
5 /n
SL& 5 lA 5V
SLV
FINAL pH D.O. (mg/L) Temperature (C) Conductivity (unhos/cm) Analyst's Initials
INITIAL
37 8 8 33 3H
a5 35! <JL& iU L
DAY DAY
12
T T 7 .3 1-2 3 - ` (/ . 2 3 - 0
3 ^ ?L 1 6 ?
1 5 2 S'
3 V 5 33 5 328 33T
s u y 5Uh US'
2 5 TMe/L.
DAY 3
DAY 4
DAY 5
DAY DAY 7
6
pH D.O (mg/L) T e m p eratu re (C) Conductivity (umhos/cm) ^Hardness (mg7L as CaCOJ
1-8 7-S 3-3^,
18 18 IS 33L
T8 1-3 25 23 L
- 1 5 3 S 7 .3
OY 2 fT
315 3 t 6
y .o
1.2
3 M?
!* 1-3 3.5
3.2S
Alkalinity (mg/L as CaCOJ
Analyst's Initials
J5ro
SLS
FINAL pH D O. (mg/L)
18 qM
11
Temperature (C)
2.5 T5
Conductivity (umhos/cm) 3 2 1 35 8
Analyst's Initials
lA
N'\TEWPLATc\BI06ENCH\CHRCNlC.ChRCNCHE.WPQ
5(i> iLliy
T3 1 IS 3 i 7 .7 - I
7 5 A '5 348 5l& J .N 3
76
J 2 / J 5Li>
1 u T Ip b i L -*
1 5 22
3 3 0 3H I SIA i l A
COMMENTS
COMMENTS
.
Revise November 1 2000
Company Saniffeerf. Does no! confaFn TSCA CB1
WM
OLVER
L A B O R A T O R IE S
CLIENT P u fo n T
JOB NO
''
PERMIT NO
EFFLUENT/TOX1CANT
DILUTION WATER: --
E PR iTiffui
CHRONIC TOXICITY TEST
CHEMICAL ANALYSIS DATA SHEET
Page H or
TEST INITIATION DATE
{z-o f o L
TEST COMPLETION DATE Z p j j .
TEST ORGANISM C t nnrfyl/in/Q -H n/nc----------
DH O TO PE R lO C
15-H our D a v /8 -H our N ight
LIGHT INTENSITY 50-100 ft-c
INITIAL
pH D.O. (mg/L) Temperature (C) Conductivity (jrmhos/cm) Hardness (mg/L as CaCOj) Alkalinity fmg/L as CaCOJ Analyst's Initials
FINAL pH D.O. (mg/L) Temperature (C) Conductivity (umhos/cm) Analyst's Initials
1
INITIAL
AY 1
DAY 2
DAY 3
DAY 4
DAY 5
DAY 6
DAY 7
COMMENTS
7-8 1 -s H 3 D l T o 3 -
7-8 1S z 5 xs
3 ? 3 2 1 1 l i . 3-S 25 a X 5 T ? a i
33L 33L 31
3 iS 3l i
lr (O V lo H i o H i ^ * IO
rH LH (Y (oH (ptf O l
!e0
5m SUS SLfi. HJy
5 J?is/
SLlV
j-Zjj 5/27
k,
i
if- '^Corr<.cTV-\^MtCntcJ1i
Ti 1i 3 34
T3 S (-B> LV
13 L 3 l.o T 5 33 5 A 5EtJ
1 7 1 U "1 1* V <L> L- ^ i,.7-
a a s' 311 32.0 SaS S i i t i 6UV SlV
CONCENTRATION
l O o m 5/<-
DAY DAY DAY DAY DAY DAY DAY 7 12 34 56
COMMENTS
j
pH D.O (mg/L)
7 fl 1 ? 7' 3-? l . l T o 1 - 8 7-8 3 ? 3 ? 3- 1 J 1,2 3 8
Temperature ("C)
z-5 iS a as 3 -6 R 5 as
Conductivity (umhos/cm)
33L H i 3 16 3 '5 s a i
Hardness (mg/L as CaCOJ
Alkalinity (mg/L as CaC03)
A nalyst's Initials
o m SA
FINAL
pH
D.O (mg/L)
3 i q-4 73 TH
Tem p eratu re (C)
T i l
C onductivity (ym hos/cm ) A nalyst's Initials
34? 3LX 5L> SUI
N MEMPLAT\lOBENCH\CHRCNICiCHRONCH w p o
L 5L&-
5/Za/
1 -r " M l o 7 L> 3 o 3 .0 G/(,5 L L
a i Alo a?
33 3 3 4 3 3 i5 3/7 SUV S tr J
5l 6
7-(, Ll ai 30.S1 SLk
-
-
Revise November 1. 2000
77
smp??y Smilizi
not contain TSCA CB1
QoA& IXn^^S'5,-
~Vn ~n- fyfcn^fa/d CcnHol
A. FISHER'S EXACT TEST FOR THE DETERMINATION OF SIGNIFICANT DIFFERENCES IN TEST ORGANISM MORTALITY
F is h e r's Exact Test
NUMBER OF
IDEN TIFICATION CONTROL 5 mg/L TOTAL
A L IV E 10 10 20
DEAD 0 0 0
TOTAL ANIMALS 10 10 20
C r i t i c a l F i s h e r ' s v a l u e ( 1 0 , 1 0 , 1 0 ) ( a lp 'h a = 0 0 5 ) i s 6 0 b v a l u e i s 10 S ince b is g re a te r th a n 6 0 th e re is no s ig n if ic a n t d iffe r e n c e b e tw e e n CONTROL a n d TREATMENT a t t h e 0 05 l e v e l
F is h e r's Exact Test
NUMBER OF
ID E N T IF IC A T IO N
A L IV E
DEAD
TOTAL ANIMALS
CONTROL 10 m g /L
10 0 91
10 10
TOTAL
19 1
20
C r i t i c a l F is h e r 's v a lu e <10,10,1C) !alp h a= 0 05) is S 0 b v a lu e is 9 S in ce b is g re a te r th a n S 0 th e re is no s ig n if ic a n t d iffe r e n c e b e tw e e n CONTROL a n d TREATMENT a t t h e 0 05 l e v e l
Olver Laboratories Incorporated 1116 South Main Street Blacksburg, Virginia 2-1060 Phone (540) 552-554S F4.X (540) 552*1715
78
Company Sanitized. Does not contain TSCA CBI
Campftf'San ~Vp "ttyg. 54JiAP"fd Carikoj
F is h e r's Exact Test
NUMBER OF
ID E N T IF IC A T IO N
CONTROL 25 m g/L + ' TOTAL
ALIVE 10 9 19
DEAD 0 1 1
TOTAL ANIMALS 10 10
. 20
C r i t i c a l F is h e r 's v a lu e (1 0 ,1 0 ,1 3 ) (alpha= 0 05) is S 0 b v a lu e is 9 S i n c e b i s g r e a t e r t h a n S 0 m e r e i s no s i g n i f i c a n t d i f f e r e n c e b e tw e e n CONTROL a n d TREATMENT a t t h e 0 05 l e v e l
F is h e r's Exact T est
NUMBER OF
ID E N T IF IC A T IO N
CONTROL 50 m g/L
ALIVE
10 7
DEAD
0 T
TOTAL ANIMALS
10 10
TOTAL
17 3
20
C r i t i c a l F is h e r 's v a lu e (1 0 ,1 3 ,1 0 ) (alph a = 0 05) is 5 0 b v a lu e is 7 S in c e b is g r e a te r th a n S 0 th e re is no s i g n i f i c a n t d iffe r e n c e b e tw e e n CONTROL and TREATMENT a t t h e 0 05 l e v e l
01ver Laboratories Incorporated
V y 1116 Smith Mam Street
^ Blacksburg, Virginia 24060
Phone (5*40) 552-5548 PAX (540) 552-1715
79
Company Sanitized. Does not contain TSCA CB!
F is h e r's Exact Test
NUMBER OF
ID E N T IF IC A T IO N
A L IV E
DEAD
TOTAL ANIMALS
CONTROL
10 0
i 100 mg/L
73
10 10
TOTAL
17
\
Critical.Fisher's value (10,10,10) !alpha=0 05) is 6 0 b vain Since b is greater than 6 0 there is no significant difference between CONTROL and TREATMENT at the 0 05 level
20
F is h e r's Exact Test
NUMBER OF
ID E N T IF IC A T IO N CONTROL
500 mg/L TOTAL
A L IV E 10 4 14
DEAD 0 6 6
TOTAL ANIMALS 10 10 20
C ritic a l S ince b b e tw e e n
F is h e r 's v a lu e (1 0 ,1 0 ,1 0 ) (alcha = 0 05) is 6 0 b v a lu e is 4 is le ss than o r equal to 6 0 th e re is a s ig n ific a n t d iffe re n c e CONTROL a n d TREATMENT a t t h e 0 . 0 5 l e v e l .
Olver Laboratories Incorporated
Kf 1116 South M ain Street
Blacksburg, Virgmta 14060 i>l , - t e nv c 7 z~ <Q n v . c u n cc"> i " i :
80
Company Sanitized. Does not contain TSCA CBl
k n q \ H S > S ) - C a m p t v' s n n 4 o
tA y u W A
C?n~W l
;r o u p
i
2
3 4 5
6
Summary o f F is h e r 's E x a c t T e s ts
ID E N T IF IC A T IO N
CONTROL 5 m g/L
10 m g/L 2 5 mg/ L 50 m g /L 100 m g/L 500 m g/L
NUMBER
EXPOSED
10 10 10 10 10 10 10
NUMBER DEAD
0 0 1. 1
3 3 S
i
O lver Laboratories Incorporated 1116 South Mam Street Blacksburg, Virginia 24060 Phone (540) 552-554S FAX (540) 552-1715
81
Company Sanitized. Does not contain TSCA CBt
Qo-V<X kna\^b\S-
-~Vp ~\Vai tbWxtkM Co^Vroi
B. C H I -SQUARE TEST FOR NORMALITY OF DATA
T itle F ile .
Dupon
T o x ic ity -C
d u b ia C h ro m c -2 /2 0 /0 1 T ransform -
C h i-S quare T e st f o r N o rm a lity
NO TR A N S FO R M A TIO N
INTERVAL
EXPECTED OBSERVED
< -l 5
4 0200 4
A c tu a l and E xpected F requencies
-1 5 to c -0 5
-0 5 to 0 5
14 5200 14
2 2 .9 2 0 0 27
>0.5 to 1 5
14 5200 12 .
>15
4 0200 3
C h i-S q u a re = 1 4412
( p - v a lu e = 0 8370)
; C r it ic a l C h i-S q u a re
= 13 277 ( a lp h a = 0 .0 1 , d f = 4) = 9 488 ( a lp h a = 0 .0 5 , d f = 4)
D a t a PASS n o r m a l i t y t e s t ( a l p h a = 0 01) C o n t i n u e a n a l y s i s
C. TEST FOR HOMOGENEITY OF VARIANCE
- T itle F ile
Dupon
o cicity-C
d u b ia C h ro n ic -2 /2 0 / l T ransform
NO TRANSFORMATION
B a r t l e t t 's T e st f o r H om ogeneity o f V a ria n ce
C a lc u la t e d 31 s t a t i s t i c = 11 0373
(p -v a lu e = 0 0506)
D a t a PASS B1 h o m o g e n e i t y t e s t a t 0 01 l e v e l C o n t i n u e a n a l y s i s
C r i t i c a l B = 15 0863 = 11 0705
(a lp h a = 0 01, d f = 5) (a lp h a = 0 05, d f = 5)
Olver Laboratories Incorporated
V 1116 South Main Street
Blacksburg, Virginia 24060 Plione (S40) 552-5548 FAX (540) 552-1715
82
Company Sanitized. Does not contain TSCA CUT
T^>o-W
CorAPO-<\c'0A 4d iWg- 'frW-icaid_0 `iN"Wa\
D. SUMMARY STATISTICS ON REPRODUCTION DATA
Title File
DuDon
Toxicity-C dubia Chronic-2/20/Q1 Transform
MC TRANSFORMATION
Summarv Statistics on Data
TABLE 1 of 2
GRP IDENTIFICATION
1 Control 5 ma/L
3 10 mg/L 4 25 mg/L 5 50 mg/L 6 100 mg/L
N
10 10 10 10 10 10
MIN
14 0000 15 0 0 0 0 13.0000
9 0000
10 0000 8.0000
MAX
22 0000
19.0000
21.0000
19 0000 23 0000
22.0000
MEAN
13 0 0 0 0 16 6000 17.1000 13 9000 15.2000 17.2000
Title File
Dunon
Toxicity-C dnbia Chronic-2/20/01 Transform
NO TRANSFORMATION
Summary Stati sties on Data
TABLE 2 Of 2
GRP IDENTIFICATION
1 Control 2 5 mg/L 3 10 mg/L 4 , 25 mg/L 5 50 mg/L b 100 mg/L
VARIANCE
7 7778 2 3778 6 7667 1 0 3222 1 1 9556 14 8444
SD
2 7889 1.1738 2.6013 3 .2128 3 .4577 3.8528
SEM
0 8819 0.3712 0.8226 1.0160 1.0934 1.2184
CV %
15 4937 7 0710
15 .2 1 2 2 23 113 8 2 2 7479 2 2 4003
Olver Laboratories Incorporated
V 1115 South M am Street
Blacksburg, Virginia 24060
83
Phone
(540)
552-5548
FAX
(540)
552-1715
Company
Sanitized.
Does
not contain
TSCA
CB1
f\ocA u,S .C s-
E. ANALYSIS OF VARIANCE OF REPRODUCTION DATA
Title Dupont File
To:ticity-C dubia Chronic-2/2O/Ol Transform
A1IOVA Table
~TP ^ W - ,S~VQ. / - y ja fc j
ChoVr
NO TRANSFORMATION
SOURCE Between W i c m n (Error) Total
DF 5
54 59
SS 113 9333 477 4000 531 3333
MS 22 7867
8.8407
F 2 5775
(p-value = 0 0366)
Critical F = 3 3759 (alpha = 0 01, df = 5,54) ^ = 2 3 3 6 1 (alpha = 0 0 5 , df = 5 , 5 4 )
Since F > Critical F REJECT Ho All equal (alpha = 0 0 5 )
F. DUNNETT'S TEST
Title. Dupon
File
<&
Toxicicy-C dubia Chronic-2/20/01
S Transform.
NO TRANSFORMATION
Dunne11's Test
TABLE 1 OF 2
Ho ControlTreatment
GROUP
IDENTIFICATION
TRANSFORMED MEAN
MEAN CALCULATED IN
SIG
ORIGINAL UNITS
T STAT 0 05
1
Control
18 .0 0 0 0
18 0 0 0 0
2
5 mg/L
16 6000
16 5000
1 0529
3
10 mg/L
l7 1 0 0 0
17 .1 0 0 0
0 6768
4
25 mg/L
13 9000
13 9000
3 0834 *
5
50 mg/L
15 2G00
15 2 0 0 0
2 1057
6
100 mg/L
17 2 0 0 0
17 2 0 0 0
0 o0 1 b
Dunne 1 1 critical value = 2 3100
(1 Tailed, alpha = 0 05, df [used] = 5,40) (Actual df = 5,54)
Olver Laboratories Incorporated
Sf 1116 South M ain Street
sS Blacksburg, V irginia 24060 Phone (540) 552-5543 F-VX (540) 552-1715
84
Company Sanitized. Does not contain TSCA CBl
t>Q.-Vo f^ncA^ Si-s-- Cciri\P&f\'sr'a 4p JtW-
0> nV c`A
Title File
Du d o n
Dunnett's Test
GROUP
IDENTIFICATION
Transform
NO TRANSFORMATION
o n to P3 O
ABLE 2
ControlTreatment
NCM OF REPS
MIN SIG DIFF
% OF
DIFFERENCE
(TN ORIG UNITS) CONTROL FROM CONTROL
1
Control
10
5 mg/L
10
3 0715
17 1
1 4000
10 mg/L
10
3.0715
17 1
0 9000
25 mg/L
10
3 .071S
17 1
4 1000
50 mg/L
10
3 0715
17.1
2 8000
100 mg/L
10
3 0716
17.1
0 8000
G. INHIBITION CONCENTRATION ESTIMATE
Titl. Dupont -Conyl Toxicity-C dubia C h r o n i c ^ 2 / 2 0 / 0 1
File
zonceric
Transform.
NO TRANSFORMATION
GRP
IDENTIFICATION
MEAN
SMOOTHED MEAN CONCENTRATION
1
Control
18 0 0 0 0
18 . o o o o
0 0000
2
5 mg/L
IS 6000
IS ..8500
5 .. 0 0 0 0
3
10 mg/L
17 1 0 0 0
I S .. 8 5 0 0
1 0 .. 0 0 0 0
4
25 mg/L
13 ,.9000
1 5 .. 9 2 5 0
25 0 0 0 0
5
50 mg/L
15 . 2 0 0 0
15 9 2 5 0
50 0000
6
100 mg/L
17 2 0 0 0
15 9 2 5 0
100 0000
7
500 mg/L
17 4000
15 . 9 2 5 0
500 0000
estimate with p = 25 is > 500 0 0 0 0
O lvcr Laboratories incorporated ^ U16 South M am Street
Blacksburg, V irginia 24060 Phone (540) 552-554S FAX (540) 552-1715
85 Company Sanitized. Does not contain TSCA CBI
----- ----
frnc.\u<.'S-
"'
"_J "
'
-Vo C r^)% ^
pn ^ a n g \ I i a
A. FISHER 'S EXACT TEST FOR THE DETERMINATION OF SIGNIFICANT DIFFERENCES IN TEST ORGANISM MORTALITY
11 1
Fisher's Exact Test
NUMBER OF
IDENTIFICATION
DEAD
ALIVE
TOT.AL ANIMALS
CONTROL w/MeOH
I
9
5 mg/L
0 10
l
,
TOTAL
1 19
10 10
20
Critical Fisher's value (10,10,1) (alpha=0.05) is negative no significant difference
b value is 0
Fisher's Exact Test
nr .
NUMBER OF
IDENTIFICATION
ALIVE
CONTROL w/MeOH 10 mg/L
9 9
TOTAL
IB
DEAD
1 1 2
TOTAL ANIMALS
10 10 20
Critical Fisher's value (10,10,9) (alpha =0.05) is 4.0 . b value a,s 9 Since b is greater than 4 0 there is no significant difference between CONTROL and TREATMENT at the 0 .OS level
Otvcr Laboratories Incorporated I I 16 South M a in Street
sS Blacksburg, V irg in ia 24060
Phone (540) 552-5548 FAX (540) 552-1715
Company6Sanitized. Does not contain TSCA CBi
"f^ O -'V g -
Cc. ri\ P o - A -0 a r i ^ r G ^
6oJ ^U-L CxAt-^ Vng_'VV-ie<.O\
Fisher's Exact Test
NUMBER OF
IDENTIFICATION
ALIVE
CONTROL w/MeOH 25 mg/L
9 9
i
TOTA.L
ie
DEAD
1 1 2
TOTAL ANIMALS
10 10 20
Critical Fisher's value (10,10,9) !alpha =0 05) is 4 . 0 b value is 9 Since b is greater tnan 4 0 there is no sigmfleant difference
between CONTROL and TREATMENT at the 0 05 level
Fisher's Exact Test
NUMBER OF
IDENTIFICATION
ALIVE
DEAD
TOTAL ANIMALS
CONTROL w/MeOH 50 mg/L
9 .7
TOTAL .
15
1
3
4
10 10
20
Critical Fisher's value (10.10,9) (alpha=0 05) is 4 0. b value is 7 Since b is greater than 4 0 there is no significant difrerence between CONTROL and TREATMENT at the 0 05 level
Olver Laboratories Incorporated 1116 South M a in Street
v\ Blacksburg, Virgim a 24060 Phone (540) 552-554S FAX (540) 552-1715 Company Sanitized. Does not contain T3CA CB1
DaVs- f~r.1n*ciWS*v'-S>-- .C.^*mpcxK-ofxu^itio ~ Corf\v&u\ls.
^oo Q-*kaA roo^y-ic^noi
Fisher's Exac t Test
NUMBER OF
IDENTIFICATION
ALIVE
DEAD
TOTAL ANIMALS
CONTROL w/MeOH
9
1
1 0 0 ma/L
73
l
'TOTAL
IS 4
10 10
20
Critical Fisher's value (10,10,9) (alpha=0 05) is 4 0 b value is 7 . Since b is greater than 4 0 there is ho significant difference between CONTROL and TREATMENT at the 0.05 level.
Fisher's Exact Test
NUMBER OF
IDENTIFICATION
ALIVE
DEAD
TOTAL ANIMALS
CONTROL w/MeOH 500 mg/L
9 4
1
S
10 10
TOTAL
13 7
20
Critical Fisher's value (10,10,9) (alpha= 0 05) is 4.0. b value is 4. Since b is less than or equal to 4 0 there is a significant difference
between CONTROL and TREATMENT at the 0.05 level.
s? Olver L-aborotones Incorporated 1116 South M am Street & Biackiburg, V irginia 24060 Phone (540) 552-5543 FAX (540) 552-1715
Company Sanitized. Does not contain TSCA CBl
'OQ'Vtx ocxAvVSiS-- ComPzjuf\vn^i "Vo Q>o'Tyo\ l^ v'V^ 5*00
cxt^A-^jt ^ 1?A,aad\
GROUP
1 2
3 4 5
6
Summary of ?isher's Exact Tests
IDENTIFICATION
NUMBER EXPOSED
NUMBER DEAD
CONTROL w/MeOH 5 mg/L 10 mg/L 25 mg/L 5 0 mg/L 1 0 0 m g /L 500 mg/L
10
10 10 10 10 10 10
1 0 1 1
3 3 S
SIG 0 05
*
i
Olver Laboratories Incorporated
y 1116 South M am Street
Blacksburg, Virginia 24060
Phone 1540) 552-5548 FAX (540) 552-1715
89
Company Sanitized. Does not contain TSCA CBl
AiAo-Ih^ S --GimoanSAA "V13 Cjn~V,\ \j-a\~W- 5oo AM-- ^.AQtj m g.~i\nQ.o0\
B. CHI-SQUARE TEST FOR NORMALITY OF DATA
Title File
Dupont
Toxicity-C d u m a Chromc-2/20/01 :er Transform
Chi-Square Test for Normality
NO TRANSFORMATION
INTERVAL
EXPECTED OBSERVED
<-l 5
4 0200 5
Actual and Expected Frequencies
-1 5 to <-0.5
-0 5 to 0 5
14 5200 13
22 9200 25
>0 5 to 1 5 > 1 5
14 5200 11
4 0200 3
Chi-Square = 2 6361 (Critical Chi-Square
(p-value = 0 6204)
13 277 (alpha = 0 0 1 , df = 4) 9 488 (alpha = 0 05 , df = 4)
Data PASS normality test (alpha = 0 01) Continue analysis
C. TEST FOR HOMOGENEITY OF VARIANCE
Title Dupont File
Toxicity-C dubia Chronic-2/20/01 cer Transform
NO TRANSFORMATION
Bartlett's Test for Homogeneity of Variance
Calculated B1 statistic = 20 1697
(p-value = 0 0012)
Data FAIL B1 homogeneity test at 0 01 level Try another transformation
Critical B
15 0863 (alpha 11 0705 (alpha
0 0 1 , df 0.05, df
5) 5)
/A
Olver Laboratories Incorporated 1116 South M ain Street Blacksburg, V irginia 2-4060 Phone (540) 552-5548 FAX (540) 552-1715
90 Company Sanitized. Does n o t contain TSCA CB1
D . SUMMARY S T A T IS T IC S ON R EPRO DUCTIO N D ATA
Title File
wDupont
Toxic it' C dubia Chromc-2/20/01 cer Transform
NO TRANSFORMATION
Summary Statistics on Data
TABLE l o f i
GRP IDENTIFICATION
-> Control w/MeOH 2 5 mg/L 3 10 mg/L 4 25 mg/L 5 50 mg/L 6 100 mg/L
N
10 10 10 10 10 10
MIN
0 0000
15 0000 13 0000
9.0000
10 oooo
8.0000
MAX
22 0000
19 0000
21 0000
19 0000 23 0000
22.0000
MEAN
14 3000 16.5000 17 1 0 0 0 13 9000 15 2000 17 2000
Title File
Dupont
Toxi c1 ty -C dubia Chronlc-2/20/01
*z7/cer
Transform:
NO TRANSFORMATION
Summary Statis ics on Data
TABLE 2 Of 2
GRP IDENTIFICATION
1 Control w/MeOH
2 5 mg/L
3 10 mg/L
4.
25 mg/L
5 ` 50 mg/L
6 100 mg/L
VARIANCE
36 6778 1 3778 6 7667
1 0 .3222 1 1 9555 14 8444
SD
6 0562 1 1738 2 6013 3 .2128 3 .4577 3 8528
SEM
1 9151 0.3712 0.8226 1 0160 1.0934 1 2184
CV %
42.3512 7 0710
15.2122 23.1138 22.7479 22.4003
Olver Laboratories Incorporated 1116 South M a in Street
Blacksburg, V irginia 2-J060 Phone (540) 552-554S FAX (540) 552-17X5
91
Company Sanitized. Does not contain TSCA CBl
I3Q-'Va- ^
S - CampoogS^r-, At flrr\v*\S ^
S0 Ml i^Vgc3 VT\ gL'Hio. A g 1
STEEL 's MANY-ONE RANK TEST
Title. File
GROUP
Dupont
Toxiclty-C dubia Chronic-2/20/01
2cer
Transform
NO TRANSFORMATION
Steel's Many-One Rank Test
- Ho Control Treatment
IDENTIFICATION
MEAN IN ORIGINAL UNITS
RANK SUM
CRIT VALUE
SIG DF 0 05
1
Control w/MeOH
14 3000
2
5 mg/L
16.6000
119 00
75 00 1 0 . 0 0
3
10 mg/L
17 1 0 0 0
121 00
75 00 1 0 0 0
4
25 mg/L
13.9000
96 00
75 00 1 0 0 0
5
50 mg/L
15 2000
104 50
75.00 1 0 . 0 0
S
100 mg/L
17.2000
122 00
75 00 1 0 . 0 0
Critical values are 1 tailed l k = 5 )
it
F. INHIBITION CONCENTRATION ESTIMATE
Title File
D u p o nt^Bxj Tcxicity-C dubia Chromc-2/20/01
zceric
Transform:
NO TRANSFORMATION
GRP
IDENTIFICATION
MEAN
SMOOTHED MEAN CONCENTRATION
1
Control w/MeOH
14.4000
16 0333
o oooo
2
5 mg/L
16.60 0 0
16 0333
5 0000
3
10 mg/L
17 1000
16 0333
10 0000
4
25 mg/L
13 9000
15.9250
25.0000
5,
50 mg/L
15.2000
15 9250
50.0000
100 mg/L
17.2000
15.9250
100 0000
7
500 mg/L
17 4000
15 9250
500.0000
ICn estimate with p = 25 is > 500.0000
Olver Laboratories Incorporated 1116 South M ain Street Blacksburg, V irginia 24060 Phone (540) 552-5548 F A X (540) 552-1715
92 Company Sanitized. Does not contain TSCA CBi
i
APPENDIX 8 ACUTE REFERENCE TOXICITY TEST DATA
93 Company Sanitized. Does not contain TSCA CB1
OLVER
la b o r a to r ies
J . i i
_i
Company Sanitized. Does not contain TSCA CBt
OLVER
LABO RATO RIES
REFERENCE TOXICITY TEST DATA SUMMARY SHEET
PAGE ___ i OF I
TESTING MONTH: Cfon
toai
REFERENCE TOXICANT:
C L M o n 'd *.
TEST DATEfSI
ACUTE TOXICITY TEST RESULTS
C erlo d aph n ia Fathead Minnow
l/ig- |/ i i lot
>/i 1 - ' / | a I o/
CHRONIC TOXICITY TEST RESULTS C e rlo d a p h n ia
TEST CONDITIONS TEST ORGANISM AGE DILUTION WATER 1 SOURCE
AERATION
EPA-MHW OLVER LABS
Continuous
1 -VS
EPA-MHW Q1..VER LABS
Continuous
TEST ACCEPTABILITY CONTROL SURVIVAL (90%)
loo'/.
Ion'/.
TEST ORGANISM AGE DILUTION WATER
SOURCE AERATION
CONTROL SURVIVAL (80%) NO OF CONTROL FEMALES
% CONTROL FEMALES WITH 3 BROODS (60%)
EPA-MHW OLVER LABS
continuous
AVE NO YOUNG/SURVIVING FEMALES (15)
STATISTICAL RESULTS SURVIVAL IN 100%
lcm
95% C I METHOD
J2jL
o'/.
2.5 3/ l
5.5 5 /l
7 . 1 - 2 - 8 3 / l H-m - (.. i 21L ttkrm ,J5i_A _ ~ k t __
AVE W T/SURV CONTROL (0 25 mg)
SURVIVAL IN HIGHEST I
JCONC
NUMBER OF REPLICATES
NUMBER OF ORGANISM/REPLICATE
NORMAL DISTRIBUTION?
HOMOGENEOUS VARIANCE?
NOEC METHOD
NOEC SURVIVAL
NOEC. REPRODUCTION/GROWTH
Fathead Minnow EPA-MHW
OLVER LABS continuous
G
COMMENTS. R itW in C A - W x 'u V j
^ `'+ H i n
.. ^
I
*\
Company Sanitized. Does not contain TSCA CBl
OLVER
LA B O R A T O R IE S
REFERENCE TOXICITY TEST DATA SUMMARY SHEET
PAGE 1 OF I____
TESTING MONTH:
Zn,r>l________________
REFERENCE TOXICANT:
d 3Vt.riA.fc.
1 TFST DATEfSl
ACUTE TOXICITY TEST RESULTS
C e rlo d a p h n la Z fn t- z /iu L i
Fathead Minnow z / ; t - Z-Ao / d /
.
CHRONIC TOXICITY T EST RESULTS C e rio d a p h n la
Fathead Minnow
TFST CONDITIONS TEST ORGANISM AGE DILUTION WATER SOURCE AERATION
t H u 04<S EPA-MHW
OLVER LABS Conlmuous
Z J-A.H5 FPA-MHW OLVER LABS Continuous
TEST ORGANISM AGE
DILUTION WATER SOURCE AERATION
FPA-MHW OLVER LABS
continuous
EPA-MHW OLVER LABS
continuous
TEST ACCEPTABILITY CONTROL SURVIVAL (90%)
i ooV.
lo o /
CONTROL SURVIVAL (80%) NO OF CONTROL FEMALES
% CONTROL FEMALES WITH 3 BROODS (60%)
AVE. NO. YOUNG/SURVIVING FEMALES (15)
STATISTICAL RESULTS oUKVIVAL IN TUU/o
'-'-'50
QC0/_ p | METHOD
'
AVE W T/SURV CONTROL (0 25 mg)
o' /. 0 /
SURVIVAL IN HIGHEST i
1CONC
? .\ 3lu ^
1. B - 1 . 5 3 /l
II. 1 3 / l / o. Z - /2 oJ/i
NUMBER OF REPLICATES NUMBER OF ORGANISM/REPLICATE
NORMAL DISTRIBUTION?
ip c a m-.r. VH. if
HOMOGENEOUS VARIANCE?
NOEC METHOD
NOEC SURVIVAL
NOEC REPRODUCTION/GROWTH
SG
SG
SG
COMMENTS: R c-ferLn n -froXv u-P)
v~\il-H o lV 'i u n T w M +K <LXf^cHd__V ^ A l
N?
OLVER
L A B O R A T O R IE S
REFERENCE TOXICITY TEST DATA SUMMARY SHEET
PAGE i O F __ L
Company Sanitized. Does not contain TSCA CBI
TESTING MONTH: tAcMC-U 2 o p l
REFERENCE TOXICANT: fSochurA C V |Uri'4.^....
TEST DATEfSl
ACUTE TOXICITY TEST RESULTS C erlodaphnla Fathead Minnow
3 I lb -aU ftlo l 3[zq - ^ h ilo i
CHRONIC TOXICITY TEST RESULTS C e rlo d a p h n la
TEST CONDITIONS TEST ORGANISM AGE DILUTION WATER SOURCE AERATION
U3 cn
TEST ACCEPTABILITY CONTROL SURVIVAL (90%)
CX.'A Floors
FPA-MHW OLVER LABS
Continuous
I o o '/
2
EPA-MHW PI VER LABS
Continuous
oo7.
TEST ORGANISM AGE DILUTION WATER
SOURCE AERATION
CONTROL SURVIVAL (80%) NO OF CONTROL FEMALES
% CONTROL FEMALES WITH 3 BROODS (60%)
FPA-MHW OLVERLABS
continuous
AVE NO. YOUNG/SURVIVING FEMALES (15)
STATISTICAL RESULTS SURVIVAL IN 100%
LC*
95% C ! METHOD
0/
l.(> 3 /l
l . i - l . 8 3A. ___ Pv-&b'~ir___
o7
11- H 3 J L lo. fe - 12-1 3Jl
AVE. W T/SU pV CONTROL (0 25 mg)
SURVIVAL IN HIGHEST
JCONC
NUMBER OF REPLICATES
NUMBER OF ORGANISM1REPLICATE
NORMAL DISTRIBUTION'?
HOMOGENEOUS VARIANCE?
NOEC METHOD
NOEC SURVIVAL
NOEC RJEPRODUCTION/GROWTH
Fathead Minnow
EPA-MHW O lVFR LABS
continuous
COMMENTS: 7T
-V\o-y^
rg-ooVA
A--
16-APH-200 I
TITLE:
Ceriodaphnia dubia Acute Test
Reference Toxicant Sodium Chloride
Test Date Test Name Mean
Mean+2SD Mean-2 S
LC50
1 1 /2 0 / 2 0 0 0 01/19/2001 01/19/2001 0 1 /2 2 /2 0 0 1 01/24/2001 02/14/2001 03/16/2001
1.73 2.48 2.48
1.6 8
1.53 2.14 1.55
2 .11
2.23 2.09 1.98
2 .0 1
1 94
3.17 3 10 2.99 2.90 2.84 2.78
1.04 1.36
1.2 0
1.06 1.17
1 10
97
O l v e r L a b o r a t o r ie s . In c
Company Sanitized. Does not contain TSC CBI
16-Apr-20Q1
Ceriodaphnia dubia Acute Control Chart
Sodium Chloride Reference Toxicant
LC50 ( g/L NaCi )
LC50
------- Mean
------- Mean+2SD ------- Mean-2SD
I
OLVER LABORATORIES, INC
98 Company Sanitized. Does not contain T SG ACSI
%
I 6-APR-200 I
TITLE:
FATHEAD MINNOW ACUTE TEST
___________ Reference Toxicant. Sodium Chloride (o /L )________
Test Date Test Name Mean Mean+2 SD Mean-2SD
LC50
1 1 /2 0 / 2 0 0 0 12/18/2000 12/19/2000 12/19/2000 12 /2 0 /2 0 0 0 01/17/2001 02/14/2001 03/29/2001
11.7 9.9
10 8
12
11.4 11 4
1 1.1
11.4
10.80 10.80
11 .1 0
11.16
11.2 0
11.19
11.2 1
13.35 .12.60 13.00 12.82 12.70 12.56 12.49
8.25 9.00 9.20 9.50 9.70 9.81 9.93
O l v e r L a b o r a t o r i e s . In c
99 Company Sanitized. Does not contain TSC CBI
1S-Apr-2001
FATHEAD MINNOW Acute Control Chart
Sodium Chloride Reference Toxicant
LC50 ( g/L NaCI )
-- LC50
------- Mean
------- Mean+2SD ------- Mean-2SD
OLVER LABORATORIES, INC
1 00 Company Sanitized. Does not contain TSCA CBl
i
APPENDIX 9 CHRONIC REFERENCE TOXICITY TEST DATA
1 01
Company Sanitized. Does not contain T SC A OBI
OLVER
laboratories
OLVER
LABORATORIES
REFERENCE TOXICITY TEST DATA SUMMARY SHEET
PAGE t OF
102
Company Sanitized. Does no! contain T SC A CBI
TESTING MONTH:
Z oo
REFERENCE TOXICANT: Sodi um C ^ W 'Y e
TFST DATEIS!
ACUTE TOXICITY TEST RESULTS C erlodaphnla Fathead Minnow
TEST CONDITIONS TEST ORGANISM AGE DILUTION WATER SOURCE AERATION
EPA-MHW OI-VFR LABS
Continuous
FPA-MHW OI VER LABS
Continuous
TEST ACCEPTABILITY CONTROL SURVIVAL (*90%)
CHRONIC TOXICITY TEST RESULTS
C e rlo d a p h n ia
I/ 3 - 1/ 10I o1
TEST ORGANISM AGE DILUTION WATER
SOURCE AERATION
IB-T-H hfs.
EPA-MHW OLVER LABS
continuous
CONTROL SURVIVAL (*80%) NO OF CONTROL FEMALES
% CONTROL FEMALES WITH 3 BROODS (*60%)
I uo/.
Io
I g ci'/.
Fathead Minnow
'/zz - i/z n/oi
UrS-
EPA-MHW Ol VFR LABS
continuous
US /
STATISTICAL RESULTS SURVIVAL IN 100%
LCyj f
95% C I METHOD
AVE NO YOUNG/SURVIVING FEMALES (* 15)
AVE W T/SURV CONTROL (*0 25 mg)
SURVIVAL IN HIGHEST ( M-o3A-)CONC NUMBER OF REPLICATES NUMBER OF ORGANISM/REPLICATE NORMAL DISTRIBUTION? HOMOGENEOUS VARIANCE? NOEC METHOD NOEC SURVIVAL NOEC REPRODUCTION/GROWTH
.
O '/. 5 3 ' /
Ves JL
S-HO <S
z-.g.a/u.
0 .7 .S 3//.
>0 S Un G 'h i S *in G 'k i S M rti G harwvcVt-i
2 n 3/l
2 o3 /i
COMMENTS. Pit-lfOnt-l. -VoM'GC'Vj
yts^VV* ujVtc UAvtVM'n
^.
I
Company Sanitized. Does not contain TSCA CBI
OLVER
LABORATORIES
REFERENCE TOXICITY TEST DATA SUMMARY SHEET
PAGE ___L _ 0 F _ J ____
TESTING MONTH: F ^ -W v .Q'Ym Z p p
REFERENCE TOXICANT:
AOU1C. TOXICIFY TEST RESULTS C erlodaphnla Fathead Minnow
IRSI CUNDI I IONS TEST ORGANISM AGE DILUTION WATER SOURCE AERATION
oUJ TEST ACCEPTABILITY
CONTROL SURVIVAL (90%)
EPA-MHW OLVER LABS
Continuous
EPA-MHW OI VER LABS
Continuous
STATISTICAL RESULTS SURVIVAL IN 100%
TEST ORGANISM AGE DILUTION WATER
SOURCE AERATION
CONTROL SURVIVAL (S0%) NO OF CONTROL FEMALES
% CONTROL FEMALES WITH 3 BROODS (60%)
AVE NO YOUNG/SURVIVING FEMALES (15)
AVE W T/SURV CONTROL (0 25 mg)
SURVIVAL IN HIGHEST ( 3- I 5?,, )CONC NUMBER OF REPLICATES NUMBER OF ORGANISM/REPLICATE NORMAL DISTRIBUTION? HOMOGENEOUS VARIANCE?
C e rlo d a p h n la % ln - Z - / / 3 lo I
Fathead Minnow z /;z -
l-B U5.
FPA-MHW OLVER LABS
continuous
l - M Virs FPA-MHW
PI VER LABS continuous
top/.
IO
I Do'/
I d o /.
6 . Cp3 z
O / 35 X IQ
NOEC REPRODUCTION/GROWTH
OLVER
LABORATORIES
REFERENCE TOXICITY TEST DATA SUMMARY SHEET
PAGE ' OF I
104
Company Sanitized. Does not contain TSCA CBI
TESTING MONTH: M tw c V i 'l o t , 1
REFERENCE TOXICANT: 5 o J m m
I I'S I 0 -M1 (S.
ACUIE 1 OXICI fY TEST RESULTS C eriodaphnla Fathead Minnow
CHRONIC TOXICITY TEST RESULTS Ceriodaphnla
3/ 15- 3/ 2.1/ 0/
TEST CONDITIONS TEST ORGANISM AGE DILUTION WATER SOURCE AERATION
EPA-MHW OLVER LABS
Continuous
FPA-MHW OLVER LABS
Continuous
TEST ACCEPTABILITY CONTROL SURVIVAL {2 90%)
TEST ORGANISM AGE DILUTION WATER
SOURCE AERATION
CONTROL SURVIVAL (2 8 0 %) NO OF CONTROL FEMALES
% CONTROL FEMALES WITH 3 BROODS (2 6 0 %)
) - e hrs. EPA-MHW Ol VER LABS continuous
1007. ID
n o V.
Fathead Minnow
I--Z H hrs . EPA-MHW O IV FR 1ABS continuous
<W
STATISTICAL RESULTS SURVIVAL IN 100%
LCM
95% C I METHOD
COMMENTS:
*%
AVE NO YOUNG/SURVIVING FEMALES (215)
AVE WT /SURV CONTROL (2 O 25 mg)
'g -5
Q., o
SURVIVAL IN HIGHEST (H.o /* , )CONC NUMBER OF REPLICATES L NUMBER OF ORGANISM/REPLICATE
NORMAL DISTRIBUTION? HOMOGENEOUS VARIANCE? NOEC METHOD NOEC SURVIVAL NOEC R^PRODUCTION/GROWTH
is :
07.
jo
.Vtj.
MO
frfccl'-S
2 . o 3JL
Qi.%. 3A . D .% 1 SJi-
7 3 V.
10
S Vet G It s S MD G Vts. S s K i'i G
T-* 3/Ll.-z 3 /l
i n-i 3 /l.
yV^, v-Ot'VVv "YWg.
I -A PR -200 I
TITLE:
FATHEAD MINNOW CHRONIC-SURVIVAL
Test Date
01/04/2001 0 1 /2 2 / 2 0 0 1 01/31/2001 02/05/2001 02/12 /2 0 0 1 03/14/2001
Test Name NOEC
2 2
2 2
1.25 2.5
Mode
2 .0 0 2 .0 0 2 .00 2.0 0 2 .00
Mode/0.5 Mode .5 ________ _ __________
4.00 4.00 4.00 4.00 4.00
1.0 0 1.0 0 1.0 0 1.0 0 1.0 0
105
O l v e h La b o r a t o r i e s , In c
Company Sanitized. Does not contain TSCA CBI
15-Ap r-2001
FATHEAD MINNOW CHRONIC
SURVIVAL CONTROL CHART
- m - NOEC ------- Mode ------- Mode/0.5 ------- Mode*0.5
- Olver Laboratories, Inc
l 06 Company Sanitized. Does no! contain TSCA CB(
I S-APR-SO O I
TITLE :
F A T H E A D MINNOW C H R O N IC -G R O W T H
Reference Toxicant: Sodium Chloride (q/L) ______
Test Date
Test Name
Mode
Mode/0.5 Mode 0.5
NOEC
_________________ ______________
01/04/2001 0 1 /2 2 / 2 0 0 1 01/31/2001 02/05/2001 0 2 /12 /2 0 0 1 03/14/2001
2 2 2 2
1.25 1.25
2 .0 0 2 00 2 .0 0 2 .0 0 2 .0 0
4.00 4.00 4.00 4.00 4.00
1 00 1 00 1 00 1.0 0 1.0 0
107
O l v e r La b o r a t o r i e s . In c
Company Sanitized. Does not contain TSCA CB1
1 6-Apr-2001
FATHEAD MINNOW CHRONIC
GROWTH CONTROL CHART
03 fi "_io-- O-C 5c E
I4
CO
cn3 o 01112,, z
0 1 /0 4 /2 0 0 1
01/22/2001
NOEC
0 1 /3 1 /2 0 0 1
Mode
0 2 /0 5 /2 0 0 1
------ 1------
02/ 12/2001
0 3 /1 4 /2 0 0 1
Mode/0.5
Mode*Q.5
Olver Laboratories, Inc.
108 Company Sanitized. Does not contain TSCA CB1
16-APR-200 1
TITLE:
CER10DAPHN1A CHRONIC TEST_SURVIVAL
____________ Reference Toxicant: Sodium Chloride (g/L)_________
Test Date Test Name
Mode
Mode/0 5 Mode'O 5
NOEC
1 2 /01/2000 12/27/2000 01/03/2001 02/07/2001 03/15/2001
2 1 2.00 2 2.0 0
1.5 2 .0 0
2 2 .0 0
4.00 4.00 4.00 4.00
1.0 0 1.0 0 1.0 0 1.0 0
1 09
Olver Laboratories. Inc
Company 'Sanitized. Does no! confalo TSCA CBI
1S-Apr-2001
Olver Laboratories, Inc
11 0 Company Sanitized. Does not contain TSCA OBI
! 6 -APR- 2 0 0 i
TITLE:
CER10DAPHNIA CHRONIC TEST-Reproduction
_____________Reference Toxicant: Sodium Chloride (q/L) ______ __
Test Date Test Name
Mode
Mode/0.5
Mode' 0.5
12/01/2000
12/27/2000 01/03/2001 02/07/2001 03/15/2001
0 25 0.25 0.25 0.19
0.5
0.25 0.25 0.25 0.25
0.50 0.50 0.50 0.50
0.13 0.13 0.13 0.13
111
O l v e r La b o r a t o r i e s In c
Conroany Sanitized. Does not contain TSCA CB1
16-Apr-2001
CER10DAPHN1A CHRONIC
REPRODUCTION CONTROL CHART
NOEC ( g/L Sodium Chloride )
NOEC ------- Mode ------- Mode/0.5 ------- Mode*0.5
Olver Laboratories, Inc.
11 2
Company Sanitized. Does not contain TSCA CB!
APPENDIX 10
DILUTION WATER QUALITY ANALYSES DATA
113 Company Sanitized. Does not contain TSC A CB!
OLVER
L A B O R A T O R IE S
s?
*
4
&
O LVERLABORATORIES
Consulting Engineers . Environmental Laboratories 1116 South Main Street Blacksburg, Virginia 24060
Client Sheet No.: Date: Client: Source: Shipping information:
0004151
Job No.:
30001
May 8,2000
Date Received:
4/12/00
Olver Laboratories incorporated
Blacksburg, Virginia Delivered to Olver Laboratones Incorporated by Olver Personnel
Sample No.: Date Collected: Time Collected: Description:
123511 4/12/00 9 45 a m and 3:00 p m. EPA Moderately Hard Dilution Water
Analysts
pH (Laboratory) (EPA 150 1) Alkalinity as CaC03 (EPA 310 1) Conductivity (EPA 120.1 ) Total Cyanide (EPA 335 2) Ammonia as N (SM 4500 NH3,F) Nitrate as N (ERA 352.1 ) Nitrite as N (EPA 354 1) Hardness as CaC03(EPA 200 7) Total Phenols (EPA 420 1)
MDL = M inim um Detection Limit N/A = Not Applicable ND = Not Detectable
Result
8 09
60 mg/L 317 imhos/cm ND ND ND ND 100 mg/L ND
MM,
N/A
10 mg/L .
1 0 pmhos/cm 0 005 mg/L
0.1 mg/L 0 1 mg/L 001 mg/L
1 mg/L 0 005 mg/L
Date/Time Analyzed
4/12/00, 7 45 pm. 4/20/00, 11 00 a.m 5/02/00,10 45 a m 4/20/00, 8 15am 4/17/00, 5 00 p m. 4/14/00, 3 00 pm. 4/14/00, 1 30 p m. 4/18/00, 5 00 p m 4/24/00, 1 10 pm.
Analyst
SAH ACC AOO DF SAH BCW SAH HT DF
All tests according to Standard Methods for the Examination of Water and Wastewater. 18th Edition, Te?t Methods for Evaluating Solid Waste fPhvsical/Chemican. 2nd and 3rd Editions, and Methods for the Chemical A nalysis of Water and Wastes, EPA
By ---------------------Bnt Ritchey Q Laboratory Manager
Unless otherwise indicated, this report sets forth the results of our analysis of samples delrvered lo our laboratory and shall nol be construed to be a representation by ver Laboratories Incorporated as to the source or method of procuring such samples All reports are submitted as the confidential property of clients and authonralton or pub ication of any statements contained in our reports is reserved pending our wntten approval
Blacksburg, VA (540) 552-6974 114
Page 1 of 6
N SDA T A\LAB\30C301\CLNTSHT\0004151
Company Sanitized. Does not contain TSCA CBl
OLVER
l a b o r a t o r ie s
Client Sheet No Client Date
0004151 Olver Laboratories Incorporated
May 8, 2000
Sample No.: Date Collected: Time Collected: Description:
123511 4/12/00 9 45 a.m and 3:00 p m. EPA Moderately Hard Dilution Water
Analysis
Total Aluminum (EPA 202 2) Dissolved Aluminum (EPA 202 2) Total Arsenic (EPA 200 9) Dissolved Arsenic (EPA 200 9) Total Cadmium (EPA 200 9) Dissolved Cadmium (EPA 200 9) Total Chromium III (EPA 200 9-SM 3500 Cr,D) Dissolved Chromium III (EPA 200.9-SM 3500 Cr,D) Total Hexavalent Chromium (SM 3500 Cr,D) Dissolved Hexavalent Chromium (SM 3500 CrtD)
Total Cobalt (EPA 200 9) Dissolved Cobalt (EPA 200 9) Total Copper (EPA 200 9) D is s o lv e d C o p p e r (EPA 2 0 0 9) Total Iron (EPA 235 2) Dissolved Iron (EPA 236 2) Total Lead (EPA 200 9) Dissolved Lead (EPA 200.9) Total Mercury (EPA 245 1) Dissolved Mercury (EPA 245.1) Total Nickel (EPA 200 9) Dissolved Nickel (EPA 200.9) Total Selenium (EPA 200 9) Dissolved Selenium (EPA 200 9) Total Silver (EPA 200.9) Dissolved Silver (EPA 200.9) Total Zinc (EPA 200 7) Dissolved Zmc'(EPA 200 7) Pnonty Pollutant Organics-
Acid Compounds (EPA 625): 2-Chlorophenol 2.4- Dichlorophenol 2.4- Dimethylphenol 4.6- Dinitro-o-cresol 2.4- Dmitrophenol 2-Nitrophenol 4-Nitrophenol p-Chloro-m-cresol
Pentachlorophenol
Phenol 2.4.6- Tnchlorophenol
Result
0 005 mg/L ND ND ND ND ND ND ND ND ND ND ND ND ND
0 006 mg/L 0 006 mg/L
ND ND ND ND ND ND ND ND ND ND ND ND
ND ND ND ND ND ND ND ND ND ND ND
MP.L
0 003 mg/L 0 Q03 mg/L 0 001 mg/L 0 001 mg/L 0 0001 mg/L 0 0001 mg/L 0 001 mg/L 0 001 mg/L 0 005 mg/L 0 005 mg/L 0 001 mg/L 0 001 mg/L 0 001 mg/L 0 001 mg/L 0 001 mg/L 0 001 mg/L 0 001 mg/L 0 001 mg/L 0 0002 mg/L 0 0002 mg/L 0 001 mg/L 0 001 mg/L 0 002 mg/L 0 002 mg/L 0 0002 mg/L 0 0002 mg/L 0 005 mg/L 0 005 mg/L
10 Ag/L 10 ig/L 10 aq/l 10 A94-
50 Ag/L
10 A9/L
50 A9/L
20 figlL
50 A9/L
10 A9/L 10 aq/l
Date/Time Analyzed
5/02/00, 12.00 p m 5/02/00, 12 00 p m 4/25/00, 2:00 p m 4/25/00; 2.00 p m 4/20/00; 9.30 a m 4/20/00; 9 30 a m 4/20/00, 4 00 p m 4/20/00, 4 00 p m 4/13/00,TOT pm 4/13/00,1 30 p m 4/26/00, 3 00 p m 4/26/00, 3 00 p m 4/18/00, 9 00pm 4/1B/00; 9 00 p m 5/03/00; 12 00 p m 5/03/00; 12 00 p m 5/01/00; 2 00 pm 5/01/00; 2 00 pm 4/21/00; 9 00 a m 4/21/00; 9 00 p m 4/18/00; 7 30 a m 4/18/00; 7 30 a m 4/17/00; 11.45 a m 4/17/00, 11 45 a m 4/18/00; 5 00 p m. 4/18/00; 5 00 pm 4/22/00,11.-30 a m 4/22/00; 11.30 a m
4/2B/00;7 56 a m
Analyst
HT HT HT HT BN BN HT HT SAH SAH HT HT HT/BN HT/BN HT HT HT HT BN BN BN BN BN BN HT HT BN BN
JSL
Page 2 of 6
N \DATA\LAB\30001\CLNTSHT\0004151
115 ' Company Sanitized. Does not contain TSCA CBI
OLVER
LABORATORIES
Client Sheet No Client Date
0004151 Olver Laboratories Incorporated May 8, 2000
Sample No.: Date Collected: Time Collected: Description:
123511 4/12700 9 45 a m and 3 00 p m EPA Moderately Hard Dilution Water
Analysis
Pnonty Pollutant Organics (continued) Base/Neutral Compounds (EPA 625)
Acenaphthene Acenaphthylene Anthracene Benzidine i Benzo(a)anthracene Benzo(a)pyrene 3,4-Benzofluoranthene Benzo(g,h.i)perylene Benzo(k)fluoranthene Bis(2-chloroethoxy)methane Bis(2-chloroethyl)ether Bis(2-chloroisopropyl)ether Bis(2-ethylhexyl )phthala te 4-Bromophenyl Phenyl Ether
Butyl Benzyl Phthalate 2-Chloronaphthalene -4-Chlorophenyl Phenyl Ether Chrysene , Dibenzo(a,h)anthracene 1,2-Dichlorobenzene 1,3-Dichlorobenzene 1,4-Dichlorobenzene 3,3'-Dichlorobenzidine Diethyl Phthalate Dimethyl Phthalate Di-n-Butyl Phthalate 2,4-Dinitrotoluene 2,6-Dinitrotoluene Di-n-Octyl Phthalate 1,2-Diphenylhydrazine Fluoranthene Fluorene Hexachlorobenzene
Result
ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND
MDL
10 Fg/L 10 Ag/L 10 Fg/L 10 u g l l 10 Fg/L 10 Fg/L 10 Fg/L 10 f g/L 10 Fg/L 10 Fg/L 10 FgA10 f g/L 10 Fg/L 10 Fg/b 10 Fg/t 10 Fg/t 10 Fg/L 10 Fg/i 10 Fg/L 10 Fg/L 10 Fg/L 10 Fg/L 20 Fg/L 10 Fg/L 10 Fg/L 10 f g/L 10 Fg/L 10 Fg/L 10 Fg/L 10 Fg/L 10 Fg/L 10 Fg/L 10 Fg/L
Date/Time Analyzed
4/28/00, 7 56 a m
Analyst JSL
Page 3 of 6
N \DATA\LABV30001ICLNTSHT\0004151
116 Company Sanitized. Does not contain TSCA CBI
OLVER
l a b o r a t o r ie s
Client Sheet No Client Date
0004151 Olver Laboratones Incorporated
May 8, 2000
Sample No.: Date Collected: Time Collected: Description:
123511 4/12/00 9-45 a m. and 3:00 p m. EPA Moderately Hard Dilution Water
Analysis
Result
Base/Neutral Compounds (EPA 625} (continued). Hexachlorobutadiene Hexachlorocydopentadiene Hexachloroethane
lndeno( 1,2,3-cd jpyrene Isophorone^ Naphthalene Nitrobenzene N-Nitrbso-dimethylamine N-Nitroso-di-n-propylamine N-Nitroso-diphenyiamine
Phenanthrene
Pyrene 1,2,4-Tnchlorobenzene
ND ND ND ND ND ND ND ND ND ND ND ND ND
MDL
10 ^gIL 10 pg/L 10 pig/L 10 pg/L 10 Aig/L 10 ijqIL 10 figIL 10 figfL 10 f/g/L 10 pg/L 10 Aig/L 10 ig/L 10 Aig/L
DatefTme Analyzed
4/28/00, 7 56 a m
Analyst JSL
Page 4 of 6
N \DATA\LAB\30001 \CLNTSKh0004151
1 17 Company Sanitized. Does not contain TSCACB1
OLVER
la b o r a t o r ie s
Client Sheet No Client Date
8004151 Olver Laboratories Incorporated
May 8, 2000
Sample No.: Date Collected: Time Collected: Description:
123511 4/12/00 9'45 a m and 3 00 p.m. EPA Moderately Hard Dilution Water
Analysis
Volatile C o m p o u n d s (EPA 624)-
Acrolein
A crylom tnle
Benzene Bromodichlbromethane
Bromoform Bromome'thane Carbon Tetrachlonde Chlorobenzene Chloroethane 2 -Chloroethy( Vinyl Ether Chloroform Chloromethane Dibromochioromethane 1.1- Dichloraethane 1.2- Dichloroethane 1.1- Dichloraethene trans-1,2-Dichloroethene 1.2-Dichloropropane ci^-1,3-Dichlorapropene trans-1,3-Dichloropropene Ethylbenzene Methylene Chlonde sym-Tetrachloroethane Tetrachloroethene Toluene 1.1.1-Tnchloroethane 1.1.2-Tnchloroethane Tnchloroethene Tnchiorofluorometha ne
Vinyl Chlonde
Result
ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND
Mm.
10 ug/L 10 pg/L 5 pg/L
5 pg/L 5 pg/L 10 g/L 10 pg/L 5 pg/L 10 pg/L 5 pg/L 5 pg/L 10 pg/L 5 pg/L 10 pg/L 5 ng/L 10 pg/L 10 pg/L 5 /g/L 5 xg/L 5 pg/L 5 pg/L 5 pg/L 5 pg/L 5 pg/L 5 pg/L 10 pg/L 5 pg/L 10 ug/L 10 pg/L 10 pg/L
Date/Time Analyzed
4/13/00. 4 06 p m
Analyst BP
Page 5 of 6
N\DATa4aBV50001\CLNTSHH0004151 118 Company Sanitized. Does not contain TSCACB!
OLVER
la b o r a to r ie s
Client Sheet No
ci,ent
Date
Sample No.: i
Date Collected:
; Time Collected:
i
Description:
Analysis
Pesticides (EPA 608) Aldnn alpha-BHC beta-BHC delta-BHC gamma-BHC Chlordane . 4,4'-DDD ` 4,4'-DDE 4.4'-DDT Dieldnn Endosulfan I Endosulfan II Endosulfan Sulfate Endnn Endnn Aldehyde Heptachlor Heptachlor Epoxide Toxaphene PCBs (EPA 6Q8) PCB-1016 PCB-1221 PCB-1232 PCB-1242 PCB-1248 PCB-1254 PCB-1260
0004151 Olver Laboratories Incorporated May 8, 2000
123511 4/12/00 9:45 a.m and 3 00 p m. EPA Moderately Hard Dilution Water
Result
ND ND ND ND ND . ND
ND
ND ND
ND ND ND ND ND ND
ND
ND ND
ND ND ND ND ND ND ND
MfiL
1 Ag/L
1 Ag/L
1 Ag/L 1 Ag/L 1 Ag/L 1 Ag/L 1 Ag/L
1 Ag/L 1 Ag/L 1 ^g/L 1 Ag/L 1 Ag/L 1 Ag/L 1 Ag/L 1 Ag/L 1 Ag/L 1 Ag/L
1 Ag/L
50 Ag/L 50 Ag/L 50 Ag/L 50 Ag/L 50 Ag/L 50 Ag/L 50 Ag/L
Date/Time Analyzed
4/21/00. 9 26 p m
Analyst SD
4/21/00. 9 26 p m
SD
Page 6 of 6
1 19
N \DATA\LABV3000 UCLNTSHTtOOOd 151
Company Sanitized. Does not contain TSCA CBI
/ .} Si
c h ain of Custody record
.< Consulting Engineers and Environmental Laboratories
Q i w p p 1116 South Main Street Blacksburg, Virginia 24060 lXborat^ S Telephone: (540) 552-6974 FAX: (540) 552-1715
Client:_______ Giver laboratories. Incorporated Company Contact: Bioassav Laboratory_______I-------------------------Address: T .. 111 6 South Main Street. Blacksburg. V A 2406Q.
* Client should complete ill information requested lojhe nghl and in the unshaded areas below, DO HOT WRITE IN THE SHADED AREAS
Telephone:_______ (540) 552-6974 ---------------------------------- --
ttl%J ViJttJ- u!<luu't " U p*||jUS AUtKlUIOg
Sahft&ed. Does not contain TSCA CBI
y Pl 1\/F R
CHAIN OF CUSTODY RECORD
Consulting Engineers and Environmental Laboratories 1116 South Main Street Blacksburg, Virginia 24060 Telephone: (540) 552-6974 FAX: (540) 552-1715
Client.,
Diver I ,abnmtnries. Incorporated,
Company Contact:_Bioa.ssny Laboratory
Address;_____ --------1--1--1-6---South' 'M' ai`n nS`tr-eet. p inr-Kshnrp. VA 24060-
I
APPENDIX 11 CHEMICAL ANALYSES OF BRINE SHRIMP AND YCT FOOD MIXTURES
1 22 Company Sanitized. Does not contain TSCA CB1
OLVER
L A B O R A T O R IE S
1300 Blue Spruce Drive, Suite C Fort Collins, Colorado 80524
Toll Free: 800/331-5916 Tel: 9 7 0 / 4 8 4 - 5 0 9 1 F a x : 9 7 0 / 4 8 4 - 2 5 1 4
SALMON STARTER #1 38- 4763- 91-50
PROCESS DATE:
07/ 26/00
GUARANTEED ANALYSIS
Crude Protein, Min .
.......................... 55 0%
Crude Fat, Min.......
................................15.0%
Crude Fiber, Max..... i
.................................2 0%
Toxic Metals ajid Pesticide Analysis (Note: This analysis is on Lot 3/16/00)
Perform ed by Energy Labs, Billings, MT
A lum inum
Arsenic C ad m iu m C hrom ium C o b alt Copper Iron Lead M ercury Nickel Silver Zinc
Total Metals Detection Limit
"g/g
5
5 1 5 5 5 5 5 1 5 5 5
Result "g/g
20
<5 <1 <5 <5 9 347 <5 <1 <5 <5 103
FPA Methods 8081: Orssnochlorme Pesticides & 8082. PCBTs Analys s Report
Compound*
Result Compound*
RESU
LT
ug/g
A ldrin
alpha-BHC beta-BHC delta-BHC gamma-BHC (Lindane) alp h a -C h lo rd a n e 2 amma-ChIordane 4,4' -D D D 4.4' -D D E 4,4' -D D T D ieid rin Endosulfan I Endosulfan Q Endosulfan sulfate Endrin
<0.10
Endrin ketone
<0.10
H ep tach lo r
<0.10
Heptachlor eponde
<0.10
M ethozvchlor
<0.10
C hlordane (technical)
<0.10
Toxapbene
<0.10
Aroclor-1016
<0.20
Aroclor-1221
<0.20
Aroclor-1232
<0.20
Aroclor-1242
<0.20
Aroclor-1248
<0.10
Arocior-1254
<0.20 - Aroclor-1260
<0.20
Aroclor-1262
<0.20
Aroclor-1268
<0.20
<0.10 <0.10 <1.0 <1.0 <10 <2.0 <4.0 <2.0 <2.0 <2.0 <2.0 <2.0 <2.0 <2.0
E ndrin aldehyde
<0.20
Compound analyzed for but not detected.
INGREDIENTS
v ct, r
Fish Meal, Soy Flour, Com Gluten Meal, Blood Meal, Fish Oil, Liquid Fish Solubles, Torula Dried Yeast, Brewers Yeast, Soy LecUmn, Lignm
Sulfonate, L-Ascorbyl-2-Polypbospbate (Vitamin C), Cholme Chloride, Ethoxyqum (preservative), Canthaxanthin (piggienting agent). Vitamin B12
Supplement, Niacin, Calcium Pantothenate, Riboflavin, Pyndoxme Hydrochloride, Vitamin A Acetate, D-Acuvatcd Animal Sterol (source of
Vitamin D3), Thiamine Mononitrate, Folic Acid, Biotin, dl-Alpha Tocopherol Acetate (source of Vitamin E), Menadione (Vitamin K), Zinc Sulfate,
Copper Sulfate, Manganous Sulfate, Ethylenediarrune Dihydroiodide, Cobalt Carbonate, Ferrous Sulfate, Calcium Carbonate
MANUFACTURED BY: ZEIGLER BROS., INC. P.O. BOX 95, GARDNERS, PA 17324
Aquatic BioSystems, Inc
Quality Research Organisms
123 Company Sanitized. Does not contain TSCA CB1
1300 Blue Spruce Drive, Suite C Fort Collins, Colorado 80524
Toll Free: 800/331-5916 Tel: 970/484-5091 Fax:970/484-2514
YTC TOTAL SOLIDS MEASUREMENT (Methodfrom EPA/505/8-89-002a)
YTC Process Date: Average Total Solids
12/4/00: Best if used by 04/30/01 1760 mg/1
ingredient TOt Numbers
_-
Pines International Wheat Grass WG98S00090; Zeigler Salmon Starter#!: 38-4763-9150, Fleischmanns Yeast- G-3
Analyzed Metals
A lu m in u m
Arsenic Cadmium
i
Chromium '
Conner
Iron
Lead M ercury
Nickel
Silver
Zinc
EPA Required Toxic Metals
Report Limits
Results (msfL)
Compounds
0.1 0.005
<0.1 <0.005
Aldrin alpha-BHC
0.001
<0.001
beta-BHC
0.01
<0.01
delta-BHC
0.01 0.01 gamma-BHC fLindane)
0.03 0.18 alpha-Chlordaue
0.01
<0.01
g am m a-C hlordane
0.001
<0.001
4,4' -D D D
0.01
<0.01
4.4' - DDE
0.005
<0.005
4,4' -DD T
0.01 0.42 Dieldrin
Endosulfan I
Endosullan H
Endosulfan sulfate
Endrin
Endrin aldehyde
Endrin ketone
Heptachlor
Heptachlor epoxide
M ethozychlor
Chlordane (technical)
Toxaphene
Aroclor-1016
Aroclor-1221
Arodor-1232
ArocIor-1242
Aroclor-1248
Arodor-1254
Aroclor-1260
ArocIor-1262
Aroclor-1268
Results (ug/L) <2.0 <2.0 <2.0 <2.0 <2.0 <2.0 <2.0 <4.0 <4.0 <4.0 <4.0
<2.0 <4.0 <4.0 <4.0 <4.0 <4.0 <2.0 <2.0 <20 <20 <200 <40 <80 <40 <40 <40 <40 <40 <40 <40.
Qualifier
U -U
U u u
.u u
u u u
u u u
u u u u u u u
u
u u u u u u u u u
U - Indicates compound was analyzed for but not detected ""Testing performed by Energy Labs, Billings, Montana
Aquatic BioSystems, Inc
Quality Research Organisms
Company SaAffed. Does not contain TSC CBl
OLVER Consulting Engineers Environmental Laboratories
laboratories 1116 South Main Street Blacksburg, Virginia 24060
Client Sheet No.:
0005275
Job No.:
60001
Date:
July 11,2000
Date Received:
5/25/00
Client:
Olver LaboratoriesIncorporated
Source:
Blacksburg, Virginia
Shipping information: Delivered to Olver Laboratories Incorporated by Olver Personnel
Sample No.:
Time Collected:
Date Collected:
Description:
Analysis
Total Aluminum (EPA 202.2) Total Arsenic (EPA 206 2) Total Cadmium (EPA 213 2) Total Chromium (EPA 218.2) Total Cobalt (EPA 219.2) Total Copper (EPA 220 2) Total Iron (EPA 200.7) Total Lead (EPA 239 2) Total Mercury (EPA 245.1) Total Nickel (EPA 200 9) Total Silver (EPA 272 2) Total Zinc (EPA 200.7)
124686
3:45 p m. 5/25/00 Tetramin Flakes (Lot No. 121599)
Result
MEL
Analyzed
Analyst
350 ND 0.0125 1 05 0.425 13.3 905 0 275 ND 13 0.055 82 3
mg/kg as received
mg/kg as received mg/kg as received mg/kg as received mg/kg as received mg/kg as received mg/kg as received
mg/kg as received mg/kg as received" mg/kg as received
31 2 0.15 0 005 0.15 . 0.05
05 0 35 0.05 0.25 0.05 0 01
05
mg/kg as received* mg/kg as received mg/kg as received mg/kg as received mg/kg as received mg/kg as received* mg/kg as received mg/kg as received* mg/kg as received
mg/kg as received mg/kg as received mg/kg as received
6/27/00; 8 00 a m. 7/01/00; 10.00 a.m. 6/19/00; 11.30 a.m. 7/10/00; 1 30 p.m. 6/29/00; 1.00 p m. 6/14/00; 3.00 p m. 6/22/00; 2.00 p m. 6/23/00; 2.00 p m. 7/05/00; 2:00 p m 7/05/00; 2:00 p.m 6/27/00; 3-00 p m. 6/27/00; 8:00 a m
AMT BN ' AMT BN HT
HT HT HT HT HT/BN HT AMT
MDL = Minimum Detection Limit ND = Not Detectable * Sample required dilution: MDL was raised accordingly. ** Due to low spike recovery, the Method of Standard Additions was used to analyze this sample.
All tests according to Standard Methods for the Examination of Water and Wastewater. 18th Edition, Test Methods for Evaluating Solid Waste iPhvsical/ChemiGall. 2nd and 3rd Editions, and Methods for the Chemical Analysis of Water and Wastes. EPA.
By Brit Ritchey Laboratory Manag
U nless otherwise indicated, thus report sets forth the results of our analysis of samples delivered to our laboratory and shall not be construed lo be a representation by Olver Laboratories Incorporated a s to the source or method of procuring such samples. Ail reports are submitted as the confidential property of clients and authorization for publication of any statements contained in our reports is reserved pending our written approval
Blacksburg, VA (540) 552-6974 125
Page 1 of 4
P \DATAIBIO\60001\CINTSHTI0005275
Company Sanitized. Does not contain TSCA CBI
OLVER
LABORATORIES
Client Sheet No Client Date
,
Sample No.: Time Collected: Date Collected: Description:
Analysis
Pesticides {EPA 608)'
- Aldnn alpha-BHC beta-BHC delta-BHC gamma-BHC i Chlordane 4,4'-DDD 4,4'-DDE 4,4'-DDT Dieldnn Endosulfan I Endosulfan II Endosulfan Sulfate Endnn Endnn Aldehyde Heptachlor
. Heptachlor Epoxide
Toxaphene PCBs (EPA 608):
PCB-1016 PCB-1221 PCB-1232 PCB-1242 PCB-1248 PCB-1254 PCB-1260
0005275 Olver Laboratories Incorporated July 11, 2000
124686 3:45 p.m. 5/25/00 Tetramin Flakes (Lot No. 121599)
Bssu
ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND
ND ND ND ND ND ND ND
MOL
5 Aig/kg as received 5 iig/kg as received 5 pig/kg as received 5 Aig/kg as received 5 Aig/kg as received 50 g/kg as received 5 figi\g as received 5 g/kg as received 5 pg/kg as received 5 /jg/kg as received 5 #jg/kg as received 5 g/kg as received 5 Aig/kg as received 5 Aig/kg as received 5 pg/kg as received 5 Aig/kg as received 5 g/kg as received 50 Aig/kg as received
50 fig/kg as received 50 Aig/kg as received 50 ^g/kg as received 50 g/kg as received 50 pg/kg as received 50 pg/kg as received 50 figfkg as received
Date/Time Analysed 6/06/00; 5.56 a m.
6/06/00, 5:56 a.m
Analyst asm/pmw
ASM/PMW
Page 2 of 4
126
P \DATAVBlO\600Q1\CLNTSH'n0005275
Company Sanitized. Does not contain TSCA CBl
OLVER
l a b o r a t o r ie s
Client Sheet No Client Date
0005275 Olver Laboratories Incorporated
July 11,2000
Sample No.: Time Collected: Date Collected: Description:
124687 3:45 p.m. 5/25/00 TYC (Lot No. 51900)
Analysis
Total Aluminum (EPA 202.2)
Total Arsenic (EPA 206.2)
Total Cadmium (EPA 213.2)
Total Chromium (EPA 200.9)
Total Cobalt (EPA 219.2)
Total Copper (EP/k 2202.)
Total Iron (EPA 200.7)
Total Lead (EPA 239.2)
Total Mercury (EPA 245.1)
Total Nickel (EPA 200 9)
Total Silver (EPA 272 2)
Total Zinc (EPA 200.7)
Pesticides (EPA 608):
Aldnn
alpha-BHC '
beta-BHC
delta-BHC
{jamma-SHC
Chlordane
4.4'-DDD
4,4'-DDE
4,4'-DDT
Dieldnn
Endosulfan I
Endosulfan ll
Endosulfan Sulfate
Endnn
Endnn Aldehyde
Heptachlor
Heptachlor Epoxide
Toxaphene
PCBs (EPA 608):
PCB-1016
PCB-1221
PCB-1232
PCB-1242
PCB-1248
PCB-1254
PCB-1260
Result
0.118 mg/L
0.22 mg/L'*
NO 0.004 mg/L
ND 0 054 mg/L 0.372 mg/L
0.012 mg/L
ND 0.004 mg/L
ND 0.521 mg/L
ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND
ND ND ND ND ND ND ND
MEL
Date/Time Analyzed
Analyst
0 025 mg/L* 0.15 mg/L*
0.0001 mg/L 0001 mg/L 0.001 mg/L 0.001 mg/L
0.007 mg/L
0.1 mg/L'
0.25 mg/L
0.001 mg/L 0.0002 mg/L
0 005 mg/L
5 zg/kg as received 5 zg/kg as received 5 zg/kg as received 5 zg/kg as received 5 zg/kg as received 50 zg/kg as received 5 zg/kg as received 5 zg/kg as received 5 zg/kg as received 5 zg/kg as received 5 zg/kg as received 5 g/kg as received 5 zg/kg as received 5 zg/kg as received 5 zg/kg as received 5 zg/kg as received 5 zg/kg as received 50 zg/kg as received
50 /jg/kg as received 50 zg/kg as received 50 zg/kg as received 50 Azg/kg as received 50 /zg/kg as received 50 /zg/kg as received 50 /zg/kg as received
6/27/00; 8:00 a.m 7/01/00; 10:00 a m. 6/19/00; 11:30 am. 7/07/00; 11.30 am. 6/29/00. 1:00 p.m. 6/14/00; 3:00 p.m.
6/22/00; 2:00 p.m.
6/23/00; 2:00 p m. 6/26/00; 10.00 a m. 7/05/00; 2:00 p m. 6/27/00; 3.00 p m. 6/27/00; 8:00 a m. 6/06/00; 6.24 a m.
6/06/00; 6.24 a m.
'A*
AMT BN AMT BN HT HT . HT HT AMT HT/BN HT AMT ASM/PMW
ASM/PMW
* Sample required dilution; MDL was raised accordingly. ** Due to low spike recovery, the Method of Standard Additions was used to analyze this sample
Page 3 of 4
127
P \OATA\BiO\6Q001\CLNTSHT\0005275
Company Sanitized. Does not contain TSCACBI
OLVER
LABORATORIES
Client Sheet No Client Date
0005275 Olver Laboratories Incorporated
July 11, 2000
Sample No.: Time Collected: Date Collected: Description:
124688 5:00 p.m. 5/25/00 Brine Shrimp Nauplii (Lot No. 4400)
Analysts
Total Aluminum (EPA 202.2)
Total Arsenic (EPA 206.2)
Total Cadmium (EPA 213 2)
Total Chromium (EPA 200.9)
Total Cobalt (EPA219.2)
Total Copper (EPA 220 2)
Total Iron (EPA 200.7)
Total L e a d (EPA 239 2)
Total Mercury (EPA 245 1)
Total Nickel (EPA 200.9)
Total Silver (EPA 272.2)
Total Zinc (EPA 200.7)
Pesticides (EPA 608):
Aldnn
alpha-BHC
beta-BHC
-
" detta43HC
gamma-BHC _
Chlordane
4.4 - ODD
4,4'-DDE
4.4- DDT
Dieldrin
Endosulfan I
Endosulfan II
Endosulfan Sulfate
Endnn
Endnn Aldehyde
Heptachlor
Heptachlor Epoxide
Toxaphene
PCBs (EPA 608).
PCB-1016
PCS-1221
PCB-1232
PCB-1242
PCB-1248
PCB-1254
PCB-1260
Result
0.007 0.08 ND
0 001 ND
0 015 1.04 ND ND
0.003 ND
0 069
mg/L mg/L** mg/L mg/L mg/L
mg/L mg/L
ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND
ND ND ND ND ND ND ND
MDL
Date/Time Analyzed '
Analyst
0.005 0.15
0.0001 0.001 0.001 0 001 0 007 0.1 0 25 0.001
0.0002 0 005
mg/L mg/L* mg/L mg/L mg/L mg/L mg/L mg/L* mg/L mg/L mg/L mg/L
'
5 g/kg as received 5 g/kg as received 5 ud/kq as received 5 g/kg as received 5 g/kg as received 50 g/kg as received 5 g/kg as received 5 j.g/kg as received 5 fj.g/kg as received 5 g/kg as received 5 g/kg as received 5 g/kg as received 5 xg/kg as received 5 g/kg as received 5 g/kg as received 5 /g/kg as received 5 g/kg as received 50 u/kd as received
50 /g/kg as received 50 /g/kg as received 50 /g/kg as received 50 /g/kg as received 50 /g/kg as received 50 /g/kg as received 50 /g/kg as received
6/27/00; 8 00 a.m. 7/01/00; 10.00 a.m 6/19/00,11:30 a.m. 7/07/00; 11:30 a.m. 6/29/00, 1.00 p.m. 6/14/00. 3 0 p.m. 6/22/00, 2:00 p.m. 6/23/00. 2.00 p m 6/26/00; 10:00 a m 7/05/00, 2-00 p m 6/27/00. 3 00 p.m 6/27/00; 8:00 a m 6/06/00; 6:53 a m.
6/06/00, 6 53 a.m
AMT BN AMT BN HT HT HT HT AMT HT/BN HT AMT ASM/PMW
ASM/PMW
* Sample required dilution; MDL was raised accordingly. ** Due to low spike recovery, the Method of Standard Additions was used to analyze this sample.
Page 4 of 4
128
P \OATA\BIOU50001\CLNT5HT10005275
Company Sanitized. Does not contain TSCA CB1
)
Auti
k
V CHAIN OF CUSTODY RECORD
S Consulting Engineers and Enviionmenlal Laboratories
Q | w p p 1116 South Main Street Blacksburg, Virginia 24060 l a b o r a t o r ie s Telephone: (540) 552-6974 PAX: (540) 552-1715
* Client ihuuld cmplele sil information requested to (he right ami in the unshaded areas below DO NOT WRIT IN D lC SIIADHU AKUAS
* Sample] w ill be discarded or relumed lo the client two weeks after (he analytical report has been nulled, unless prior irfiig c n ic M i have been made
Client: Olvic-r L abor^T ori^s X uC . Company Contact: 5>ioo.->sqM L-a,bnoykirjj - (Smi Address:_____ ~ - _____________________________ T e le p h o n e :_______ Purchase Order No.,
C o m p o s ite ( / ) # o r C o n ta in e rs
c s in c n .S
3
JuUi lo o o o \
O lv c r S a m p le 10 H
p ii
S a m p le L o c a llo n
(i c , in d u c ili, m u ra li 001, M W I, ele )
D a le C o lle citd
Tim e C o lle citd
S a m ple Type
C o nta iner I ype
/J d ! /Jo 'L '
T ^ ir e s m io F ta K c S L o -t i z is n n
^ Z 5 j
2 M 's
F o p -
-D--------- pf --m------ 6 o u r C t
P T *vc_ fe a
J,
P re ie rva llo n W o n t.
eL3t. A n a ly s e r t u q u e sIc d O
T o - M IAe-V<LK-.
BA / A3
A h A S ,c r, c d .c u ,C o , P c, p b ,u r,7 .n .
i/ 1
P L cA L l A j p C f t S ^ " m c lA vo A G ,0 < ? 3
1 2- W fe> 7 7 " ' r * '/ /JO
T TC - Food M ix P u rC L d+. S I T o d
5 h 5 o o
2^6 -----------o\--m
f\&
A t.
MA K lo n .
Tb-p.1 N s T A \i.
m .A n
e - " ! f t ! , A 5 , C r , C d ( C u . C o , p t , f A s J d J iT L A
1 p * y H c . ( <**>./D -- % { n i c - i h o c ) Gd o ? 3
'-s S d
B n o i 5 onVip Ln+
K J o u tp li/ --
5 [V 5 )c o
c ro o 5 p h -i
f\& A&~
^A W on*
U -'' / 1
T b-W N K'C +'cAS.*
H\ #
.I, f K i . C r . C i C u , C o ,
p ii , Z r
f B i y A ' _i'd s j
C M ic tU o d 6 q 8 ^
S u m p lc i(s ) (S g n a lu re )
4 L0 V
il
itc ln iq u is h c d B y* (S ig n n lu :)
A A U / ild i Itc lin c |tii.s lic d C fy^ ( S ig i'iiilu ic )
R e lin q u is h e d B y : (S ig n n lu ic )
Dale 1mn. R e c e i v e d B y ( S i g n a t u r e )
Date Time R e e l e d B y : ( S i g n a t u r e )
1 Dale lim e
R e c e iv e d B y : (S ig n a tu re )
1
S p e c ia l In s tru c tio n s
| 6 e . iW 'u J r t u r < ir A r p r s s ii u S . d A Y ]
Dale
%% Date
lim e
i'3 n Time
T e m p e ra tu re U jio n rc c c ip l in lo ll = , S am ples tra n sp o rte d o n ice? Yes
M e th o d o f S h ip m e n t.
Hu
1
Dale
lime
C o m m e n ts
C jf
i
l O V'J. **i**t*w * - ul