transmittal of fish study work plan for lake dupree ... · fishes^-, and the audubon society field...
TRANSCRIPT
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HERCULES , Hercules IncorporatedHercules PlazaWilmington, DE 19894
-0 - - . . . --. (302) 594-5000-' ; . . , i ! • .). Telex: 83-5479
Writer's direct dialnumber: (302) 594-7066
September 1, 1988
Hr. Robert E. HannesschlaBer, Chief CERTIFIED MAILReturn receipt requestedSuperfund Enforcement Branch (6H-E)
U . S . Environmental Protection AgencyRegion VI1445 Ross AvenueDallas, Texas 75202-2733
Re; Vertac Off-site Areas - Fine Grid Sampling PlanJacksonville, Arkansas
Dear Mr. Hannesschlager:
Pursuant to paragraph 2 4 . 1 . of the CERCLA Administrative Order on Consent,CERCLA VI-07-88 ( O r d e r ) , for the above-referenced matter, HerculesIncorporated submitted to the U . S . Environmental Protection Agency (EPA) aFish Study Work Plan (Plan) for Lake Dupree on June 27, 1988. The Plan wasapproved by EPA on June 2 9 , 1988. Pursuant to paragraph 2 4 . L . of the Order,work on the Plan commenced within 10 days of approval of the Plan; fish werecollected from Lake Dupree on July 6 and 7 , 1988 by our contractor, the ITCorporation. Now, pursuant to paragraph 2 4 . M . of the Order and the schedulecontained in the Plan, we herewith submit the IT Corporation report for theFish Study Work Plan for Lake Dupree.
One ( 1 ) copy of the report and the analytical laboratory data reports (FinalDioxin Report for Jacksonville Offsite, Volume I , Report and Data Summary, andVolume II, Initial and Continuing Calibrations and Data, July 2 6 , 1988) forthe Fish Study Work Plan for Lake Dupree are enclosed with this letter.
Being transmitted under separate cover to Kate Arthur, EPA, Region VI, with acopy of this letter are five ( 5 ) additional copies of the report without theanalytical laboratory data report as requested.
Enclosures
cc; Kate Arthur (6H-EE)U . S . EPA, Region VIDallas, Texas 75202-2733(by Federal Express)
Florence K . Kinoshita. P h . D .Senior lexicologist
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INTERNATIONALTECHNOLOGY
I CORPORATION
RESPONSIVE TO THE NEEDS OF ENVIRONMENTAL MANAGEMENT
REPORT OH FISH STODY WORK PLAN(FOR 2.3.7.8-TCDD)
LAKE DUPREEJAOTSOMVTT.T.E. ARKANSAS
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REPORT ON FISH STUDY WORK PLAN
fFOR 2.3.7.8-TCDD)
LAKE DUPREE
JAgKfiONVTT.T.K, ARKANSAS
Submitted to:
HERCULES, INCORPORATEDWilraington, Delaware
Prepared by:
IT CORPORATIONKnoxville, Tennessee
August 1988
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REPORT OH FISH STUDY WORK PIAM
(FOR 2.3.7.8-TCDDj
LAKE DOPREE
.TACKSONVTT.T.R, ARKANSAS
APPROVALS: IT Analytical Services
NAME; Dana SimerlyTITLE: Proiect Manager
SIGNATURE:
NAME: Bruce Wagner_____TITLE: Laboratory Manager
S IGNATURE: /^Z^t^ ^X^L
NAME: Carol A. Erikson_____TITLE: Program Manager_______
SIGNATURE: LOW-U. •CAtA^^'——
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1.0 EXECUTIVE SUMMARY
Fish were collected from Lake Dupree, Jacksonville, Arkansas, on
July 6 and 7, 1988 in order to determine the concentrations of
2,3,7,8-tetrachlorodibenzo-p-dioxin (2 , 3 , 7 , 8 - T C D D ) in the edible
portions of fish in the lake. The fish were collected using gill
nets. A total of ten (10) fish representing five ( 5 ) species
were filleted in the field and submitted for analysis for
2,3,7,8-TCDD by high resolution gas chromatograph/high resolution
mass spectrometry. Analyses for 2,3,7,8-TCDD were done on the
left fillet, minus the skin, of each of the ten fish. The
results of these analyses showed 2,3,7,8-TCDD levels ranging
from 0.013 ppb to 0.48 ppb. The individual result for each
sample is listed below:
FIELDSAMPLENUMBER
WH1750LFMS*
WH1751LFMS
WH1752LFMS
WH1753LFMS
WH1754LFMS
WH1755LFMS
WH1756LFMS
WH1757LFMS
WH1758LFMS
WH1759LFMS
FISHSPECIES
Largemouth BuffalofishLargemouth BuffalofishGizzard Shad
Gizzard ShadWhite CrappieWhite CrappieWhite Crappie
Bowfin
Blue CatfishBlue Catfish
2,3,
0
0
0
0
0
0
0
0
0
0
7,8-TCDD(PPb)
.031
.25
.0099
.48
.046
.029
.031
.013
.068
.23
* LFMS: Left Fillet, Minus Skin
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2.0 Introduction and Objective
In compliance with a portion of an Administrative Order of
Consent between the United States Environmental Protection
Agency (USEPA), Region VI, and Hercules Incorporated, Wilmington,
Delaware, IT Corporation, a wholly owned subsidiary of
International Technology Corporation, was comnissioned to prepare
a fish study work plan for Lake Dupree, a small body of water
located in a community park in Jacksonville, Arkansas. The
purpose of the plan was to determine if the edible portions of
edible fish were contaminated with 2,3,7,8,-tetrachlorodibenzo-p-
dioxin ( 2 , 3 , 7 , 8 - T C D D ) .
The collection plan was designed to allow samplers to obtain
several different species of fish from which a representative
number of each species would be selected for analysis. The
fillet portions, minus the skin, of representative fish from the
lake were to be analyzed for 2,3,7,8-TCDD using high resolution
gas chromatography/high resolution mass spectrometry (HRGC/HRMS).
3 . 0 Field Activities
3 . 1 Fish Collection
Upon notification by Hercules Incorporated, of the acceptance of
the fish study work plan, the Field Analytical and Sampling (FAS)
Division of IT Corporation commenced fish sample collection
efforts. Scientific collection permits issued by the Arkansas
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State Game and Fish commission were used for the duration of the
project and all specified conditions were met.
Fish were collected from Lake Dupree on July 6 and 7, 1988 using
four, 6 ' mono filament gill nets, 125 feet long with 3/4 to 2 inch
mesh. The nets were strung from opposing banks in an East-West
pattern with one net in each quarter section of the lake. The
first net was strung West to East in the northernmost quarter;
the second net. East to West in the second quarter; the third
net. West to East in the third quarter and the fourth net was
strung East to West in the southernmost quarter. A 14 foot
aluminum boat equipped with a 5hp motor was operated in a random
pattern in the lake in an effort to increase the swimming
activity of the fish. The nets were checked hourly; fish were
removed and released, or kept for collection when deemed ap-
propriate for the purpose of the fish study.
Fish were keyed and identified using How to Know the Freshwater
Fishes^-, and The Audubon Society Field Guide to North American
Fishes. Whales, and Dolphins2.
After a period of over twenty-four hours and successful col-
lection of five ( 5 ) species of fish, it was decided that these
^ow to Know the Freshwater Fishes. Second Edition, SamuelEddy, Win. C. Brown Company Publishers, 1969.
^he Audubon Society Field Guide to North American Fishes.'•'hales, and Dolphins, Alfred A. Knopr, Inc., 1983.
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species would be representative of the fish population in Lake
Dupree. The five ( 5 ) species collected were:
o LARGEMOUTH BUFFALOFISH, Ictiobus cvprinellus
o GIZZARD SHAD, Dorosoma cepedianum
o WHITE CRAPPIE, Pomoxis annularis.
o BOWFIN (aka DOGFISH and GRINNEL), Amia calva
o BLUE CATFISH, Ictalurus furcatus
From these species, ten (10) specimens were selected for
analysis, including two ( 2 ) Largemouth Buffalofish, two ( 2 )
Gizzard Shad, three ( 3 ) White Crappie, one ( 1 ) Bowfin, and two
( 2 ) Blue Catfish. Excess fish, which duplicated those species
selected for analysis, were returned to the lake.
3 . 2 Sample Handling and Documentation
Each fish selected for analysis was assigned a unique, field
sample number which was scribed on a metal tag; the tag was
attached to the fish using a self-locking nylon tie threaded
through the gills and mouth. Each fish was weighed, measured and
photographed; all measurements and observations were recorded on
individual specimen collection log sheets. Copies of the com-
pleted collection logs are presented in Appendix A ; they have
been typed from the original hand-written logs for clarity.
Table 1 lists the size of each fish specimen selected for
analysis.
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Chain-of-Custody (C/C) records and Request for Analysis (R/A)
forms were initiated by the Sampling Coordinator for the ten (10)
samples in order to track sample transfer from field collection
to receipt at the laboratory, and ultimate disposal. The
originals of the C/C and R/A records accompanied the samples at
all times; a copy of each form was maintained in the field until
completion of the field effort.
After collection and identification, each fish was carefully
filleted on both sides; each fillet was then individually wrapped
in aluminum foil and placed back on the fish in its natural
anatomical position. Each "whole fish" was then wrapped in
aluminum foil and the field sample number written on the outside
of the wrapping with indelible ink. The fish were immediately
placed in a cooler of ice and later transferred to a cooler of
dry ice for shipment to the laboratory.
The single exception to this sample preparation procedure was the
right fillet of specimen WH1750, a Largemouth Buffalofish, which
was hand-delivered to the on-site USEPA representative (Region
VI) . This fillet was individually wrapped in aluminum foil, and
marked with the field sample number. It was kept frozen on dry
ice until its release, under chain-of-custody, to the EPA re-presentative. The remainder of specimen WH1750 (the "whole fish"
less the right fillet) was wrapped in foil with the left fillet
in place, and handled in the same manner as all other samples.
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The prepared fish specimens were shipped frozen on dry ice by
overnight carrier, under full chain-of-custody, to the IT Special
Analysis Laboratory (IT/SAL), in Knoxville, Tennessee, for isomer
specific (2, 3 , 7 , 8 - T C D D ) analysis.
4 . 0 Analytical Program
4.1 sample Receipt
The ten (10) fish specimens were received at the IT/SAL on July
8, 1988. Immediately upon receipt, each specimen was checked
against the accompanying chain-of-custody forms to verify
documentation accuracy and sample condition, and subsequently
logged-in. The left fillet of each fish was removed, assigned a
unique laboratory number for internal tracking purposes and
forwarded for analysis. The laboratory (ITAS) numbers and cor-
responding field sample numbers are listed in Table 2 for
convenient cross-referencing where necessary. The remaining
parts of each fish ( i . e . , right fillet, head, and viscera) were
kept frozen and remain archived at the laboratory.
4 . 2 Sample Preparation
Each fish fillet was ground and homogenized after the skin was
removed. Ten (10) grams of each sample and ten (10) grams of
sodium sulfate, the method blank, were weighed into separate
jars. Each sample and the sodium sulfate blank were spiked with
lOOul of an internal/surrogate standard mixture, containing
5.0ng 1 3 C - 2 , 3 , 7 , 8 - T C D D and l.Onq 3 7 C 1 - 2 , 3 , 7 , 8 - T C D D , and allowed
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to stand overnight for equilibration. After equilibration, ex-
traction by ITAS methodology was performed. The ITAS Standard
Operating Procedure for extraction of biological samples is
presented in Appendix B. The procedure used for each sample is
described, briefly, below.
After overnight equilibration, the sample was blended with lOOg
of sodium sulfate and 50g dry ice until homogeneous, dry and
powdery. These amounts vary slightly from the amounts described
in the work plan, but the amounts used were sufficient for drying
the samples, which is the purpose of the sodium sulfate reagent.
Acetonitrile (150 ml) was then added to each sample, and the
mixture was shaken for three ( 3 ) hours on a platform shaker. The
variation in agitation time from that described in the procedure
(Appendix B) was made based on the nature of the specific samples
and was approved by the laboratory quality control coordinator.
The resulting extract was then filtered into a flask and con-
centrated to approximately 5ml. The concentrated extract was
transferred to a separatory funnel using a ten (10) ml portion of
acetonitrile to rinse the flask. Approximately 15ml hexane was
then added to the separatory funnel.
4.3 Sample Cleanup
To aid in the removal of chemical interferences, each con-
centrated sample and blank extract was treated using separatory
funnel techniques detailed in Option C of the U . S . Environmental
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Protection Agency, Region VII protocol for "The Determination of
2,3,7,8-TCDD in Soil and Sediment," September 1983 revision.
Briefly, the extracts were washed with 20% potassium hydroxide
(KOH) followed by distilled water (to remove KOH residues) ,
followed by three concentrated sulfuric acid (H^SC^) washes,
followed again by distilled water to remove acid residues.
Further routine cleanup consisted of two ( 2 ) column chromato-
graphy steps. The first step involved passing the extract
through a neutral alumina column; in the second step, the extract
is passed through an acid-modified silica gel column which then
flows directly into another neutral alumina column ("dual
column" step). The final extracts were concentrated to near
dryness, then raised to 50ul with isooctane.
4.4 Sample Analysis
Isomer specific analysis for 2,3,7,8-TCDD was performed using a
modified version of the EPA reference method described in "RCRA
SW-846, Method 8280", revised September 1986. The final extracts
were analyzed using high resolution gas chromatography/high
resolution mass spectrometry (HRGC/HRMS) scanning in the selected
ion monitoring (SIM) mode for enhanced sensitivity. A 60m SP-
2331 fused silica capillary column, demonstrated to resolve
2,3,7,8-TCDD from other isomers of TCDD, was used. Before
acquisition of the sample data, a seven ( 7 ) isomer performance
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mixture containing 2,3,7,8-TCDD and the six ( 6 ) most closely
eluting TCDD isomers was run. In addition, a five ( 5 ) point
calibration curve was run in triplicate. The mean response
factors (RFs) obtained from this initial calibration were used
for all subsequent calculations; Table 3 contains the initial
calibration summary data. A shift standard was analyzed on each
day that sample analyses were performed, to demonstrate in-
strument stability. To be acceptable, the measured shift
standard RFs had to be within 10 percent of the mean RFs from the
initial calibration. Shift standard results are summarized in
Table 4. Method accuracy was measured by calculating the
recovery of 37C1-TCDD (surrogate standard) as compared to the
internal standard, ^C-TCDD, for each sample analyzed.
5.0 Analytical Results
The results of the isomer specific analyses for 2,3,7,8-TCDD in
the fillets (without skin) of fish from Lake Dupree obtained by
HRGC/HRMS are reported in Table 5. The "client sample number"
refers to the field sample number assigned at the time of
collection. The measured concentrations of 2,3,7,8-TCDD are
reported in parts per billion ( p p b ) . When no 2,3,7,8-TCDD was
found, a sample specific detection limit was calculated as 2 . 5
times the background signal in the general elution area of the
"C-TCDD internal standard. The additional information contained
in Table 5 ( i . e . , GC/MS analysis date and time, relative ion
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abundance and surrogate percent accuracy) is reported as required
by EPA protocols.
6.0 Analytical Quality Control
To demonstrate that all analytical materials, i . e . , reagents,
glassware and solvents, were free from interferences, a method
blank was processed with the batch of ten fish samples. The
blank was extracted, analyzed and reported according to the same
procedures used for the accompanying samples. The blank was
designated BLK1195 and no 2,3,7,8-TCDD was detected at a de-
tection limit of 0.00l9ppb, successfully demonstrating the
absence of laboratory contamination.
One matrix spike/matrix spike duplicate pair was also prepared
with this batch of ten samples, to provide data for evaluation of
analytical precision and accuracy. The sample to be spiked and
duplicated was selected at random, by the laboratory, at the time
the samples were logged in. Table 6 presents the results of the
matrix spike/matrix spike duplicate analyses, along with the
corresponding precision and accuracy calculations. The relative
percent difference (RPD) of 15.4% is well below the upper limit
of 50% specified by the EPA, demonstrating excellent analytical
precision. The spike recovery of 109% is also acceptable,
falling well within the 60-140% acceptance range, and
demonstrates excellent accuracy.
10
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Surrogate (^Cl-TCDD) recovery ("Percent Accuracy") was also
calculated for every sample and blank as a measure of the
accuracy of the overall extraction and analytical procedure. The
percent accuracy for each analysis is included in Table 5. In
every case, the accuracy is within the 60-140% method-specified
acceptance limits, demonstrating satisfactory laboratory
performance of the analytical method.
The 2,3,7,8-TCDD results generated for this fish study are
satisfactorily supported by all available quality control
information.
11
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TABLE 1
SPECIMEN SIZES: LAKE DUPREE FISH STUDY
FIELDSAMPLENUMBER COMMON NAME
(SPECIES)
SIZEWEIGHT LENGTH(gran) (cm)
WH1750LFMS*
WH1751LFMS
WH1752LFMS
WH1753LFMS
WH175LFMS
WH1755LFMS
WH1756LFMS
WH1757LFMS
WH1758LFMS
WH1759LFMS
Largemouth Buffalofish(Ictiobus cyprinellus)
Largemouth Buffalofishfictiobus cyprinellusl
Gizzard ShadCDorosoma cepedianum)
Gizzard Shad(Dorosoma cepedianum)
White Crappie(Pomoxis annularis)
White CrappiefPomoxis annularis)
White CrappiefPomoxis annularis)
Bowfin(Anna calva)
Blue Catfish(Ictalurus furcatus)
Blue Catfish(Ictalurus furcatus)
540 32
520 32
140 2 2 . 5
140 2 2 . 4
70
50
420
370
460
730
16.8
15.5
30.2
53.2
38
44.1
* LFMS: Left Fillet, Minus Skin
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TABLE 2
CROSS REFERENCE SAMPLE
LABORATORYNUMBER
BB0546
BB0547
BB0548
BB0549
BB0550
BB0551
BB0552
BB0553
BB0554
BB0555
FIELDSAMPLENUMBER
WH1750LFMS*
WH1751LFMS
WH1752LFMS
WH1753LFMS
WH1754LFHS
WH1755LFMS
WH1756LFMS
WH1757LFMS
WH1758LFMS
WH1759LFMS
NUMBER LIST
SPECIES
Largeaouth Buffalofish
Largemouth Buffalofish
Gizzard Shad
Gizzard Shad
White Crappie
White Crappie
White Crappie
Bowfin
Blue Catfish
Blue Catfish
* LFMS: Left Fillet, Minus Skin
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TABLE 3
INITIAL CALIBRATION SUMMARY
TCDD/TCD?
JACKSONVILLE OFPSITE
Date
11-02-87
11-02-87
11-02-87
11-02-87
11-02-87
11-02-87
11-02-87
11-03-87
11-03-87
11-03-87
11-03-87
11-03-87
11-03-87
11-03-87
11-03-87
CC1CC2CC3CC4CC5
Instr.ID
70-250S
70-250S
70-250S
70-250S
70-250S
70-250S
70-250S
70-250S
70-250S
70-250S
70-250S
70-250S
70-250S
70-250S
70-250S
Mean
37
61220
Sol.ID
CC1
CC1
CC1
CC2
CC2
CC2
CC3
CC3
CC3
CC4
CC4
CC4
CC5
CC5
CC5
RF Used (x) =
» RSD =
Cl
pg/nipg/nlP9/til
NativeTCDD
0.952
0.959
0.924
1.05
1.03
1.06
1.07
1.10
1.06
1.02
1.02
1.07
1.13
1.17
1.20
1.05
7.3
10 pg/ul50 pg/til
100 pg/H.11000 pg/ul3000 pg/ul
Measured RFNative
TCDF
1.88
1.86
1.91
1-99
2.03
2.04
2.10
2.33
2.28
2.09
1.82
2.30
2.42
2.63
2.74
2.16
13.0
Natives
Surrogate^'Cl-TCDD
0.931
0.923
0.846
0.956 c'
0.951
0.948
0.974
1.03
0.949
0.945
5.1
sm(bwlO)
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TABLE <
ISOMER SPECIFIC CONTINUING CALIBRATION SUMMARY
JACKSONVILLE OFFSITE
BATCH 1195
Date
07-17-88
07-17-88
07-17-88
07-18-88
07-18-88
07-18-88
Inetr.ID
70-250S
70-250S
70-250S
70-250S
70-205S
70-250S
SolID
PC
CC1
PC
PC
CC1
PC
NativeTCDD
1.08
1.08
HgasSurrogate-"Cl-TCDD
1.00
0.972
ured RF RatioNativeTCDD
1.03
1.03
(He,Surrogate•"Cl-TCDD
1.06
1.03
as/Mean)
TCDD IsoraerResolutionPet. Valley(Applies ForPC Only)
7.9»
5.4»
6.8t
7.4»
Solution ID Codes;
PC ° Performance check solutionCC1 •" Concentration calibration solution #1 - 10 pg/ul
sin(bwll)
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S g 3 E S ° S ^ s s i 5 s s i s s § i l 5
? ° . . . . ? a a a ^ a a a a a a a a a? » B - ^ - » ? ? ? ? P ? ^ ? ^ ! ! i ? P- ; S , B- S " 3 ; ; 5 5 5 5 5 ; ; 3 ;
z z S. o S 2. v » , » « » » » , » > » « , » »" •s?-6<? •° -
^I
3-g g i S S i i y y
•* 8 **
I
•o o» ^ o*
35- ° .3 .3 3 ° 3 3 ?• ?•g ° ° ° 5: g
^ i i ^ ^ I i i ^ j 5 !? S 3 3 g 3 . . . . . . . . . . . .
»„; , • • • • • • • • • • • •X 0 0. 0. Mt A 0 • W
8 a c ^ r > J 0 ^ 0 0 0 0 0 0 0 0 0 0 0r t ^ B M ' r ' ' ? ' ' ^ * ^ ' ^ ' ? * ' ^ ' ^ ' ^ ' ? 1 ^ 1 ^ ^r~ A •— ^ • . ^ . ^ . ^ _ A ^ « > ^ _ k _ * ^ ^ _ i _ J
S 8 5 S S B S S S 8 8 S S
— * f ^ ~ * » K V l m o w ^ m w ' ^ ' f »• " o « t e * o « « o w i r u - 4 o ! — • o S *
a r ^ t ^ ' ^ . p ' - ^ ' ^ O ' O f ^ t ^ l
S —* fiJ -* ufe M 0*• u * u — O f t O ^ f O o r s J o u t r u. • ^ O . - . - ^ . O - . f t . - t ^ - V l - . o l ^s s
?
_ * | \ J - « _ * _» _• r^ _• -i _* _*f r i r u ' V« 0» •0 -• C^ 0 -^ 0- •»1 <\*i.n a ™ o o •o -> M -* — -^ vim r u - o u * - « f > u i o > — • 4 0 ' ^v - k U t h J L n f ^ ^ C f f O i ' i ^ O l U *w < - c » . t ' t > ' - o o - . f > i ^ - ' . - * o y
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Table 6OA/QC REPORT
Project Nane Jacksonville off«lt»_____Coda HF»a»5B
Batch limber 1195___________________________HBHS
Simple Hatrix Fish_______Extraction Method spec I •I______
Report D.t« OB-1Z-M___________________________
GC/MS Run [iaf (I»OIMT») 07-17-M________________
Surrogate Percent AccurBcy
tuitier of Daf Point* - 17Hean Percent Accuracy « ___107X
Ranae' • 9a-Hni
Sanple * BB055;
Preclilon of Duptlotel
Splk« Dup. Vlue (i) •
Splk« Value (b) •
2,1,7,8-
TCPO
0.12
0.14
Precliloo- |a-b| « 100X - 15.W
l*b2
EPA Ringe • SOX
'• 2,3,7,»-
Accuracy of Spike Tcoo
OInervJd Spile Value <b) - 0.14
Orlg. Valir (a) • 0.031
Spike livel (c) • 0.10
Accuracy • b'l x 100X • 109X
c
EPA Rerioc • 60-140X
EPA Ranga for turroaata percent accuracy of 60-UO» applle* to laomer apecffic analyafa only.
«m(bnU)
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APPENDIX A
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EE3 SPECIMEN CULLECTIUN .06 DATE8
TIME 10
1
73
0fi
65
8 8PROJECT NAME: JACKSONVILLE/
LOCATION: , OFFSITE „ ,jacksonvilie,ArkansasPROJECT ff 480078 01 09 01
SAMPLE # WH1750LFMS
Largemouth Buf fa lo - f i sh Specimen Type
SpeciesI c t iobus cyprineTIus
Collection Method
Preservation Method
Gin riets
Dry Ice
Sample Location Description LAKE D U P R E E
PI Prep Lab AU = Austin CE = Cerritos DI = Directors ED = Edison FH = FAS MobileHK = Hiddlebrook PI = Pittsburgh SC = Santa Clara
01 Analysis Request: 01 = 2,3,7,8 TCDD 02 = Total PCDD/DF03 = Total and ISOMER specific PCDD/DF04 =
Fi lm RoU Ho. M Frame No- 22
Sample Team D.Peery, D . S i m e r l y( imt ia i s ;
Prepared By P. Peery Ck'd By DSS(Initials)
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E53 SPECIMEN CULLECTIUN 3G DATE'
TIME 1n1
74
01
6Z
8 8
OFFSITELOCATION:„ Jacksonville,Arkansas
PROJECT 3f 480078 01 09 01
SAMPLE ft WH1751 LFMS
Laroemouth Buffalof ish
Ict-iobus cyprinellus
6 1 1 1 Nets
Dry Ice
Specimen Type
Species
Collection Method
Preservation Method
Sample Location Description LAKE DUPREE
PI Prep Lab AU = Austin CE = Cerritos DI = Directors ED = Edison FH = FAS MobileMK = Middlebrook PI = Pittsburgh SC = Santa Clara
_0^ Analysis Request: 01 = 2,3,7,8 TCDD 02 = Total PCDD/DF03 = Total and ISOMER-specific PCDD/DF04 -
File Roll No. 04 Frame No- 23
Sample Team D.Peery, D.Simerly'Ini+isis)
Prepared By D- Peery Ck'd By DSS
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SPECIMEN CULLECTIUf .06PROJECT NAME: JACKSONV I LLE/
LOCATION: , OFFSITE , ,Jacksonville,ArkLOCATION: , OFFSITE , ,Jacksonville,ArkansasPROJECT ff 480078 01 09 01
DATE'
TIME--01
74
n2
R5
8 8
SAMPLE # WH1752LFMS
Gizzard Shad
Dorosonia cepedianum
Gill Nets
Dry Ice
Specimen Type
Species
Collection Method
Preservation Method
Sample Location Description LAKE DUPREE
^01 Prep Lab AU = Aust in CE = Cerritos DI = Directors ED = Edison FM s FAS MobneHK = Hiddlebrook PI = Pittsburgh SC = Santa Clara
_^_ Analysis Request: 01 = 2,3,7,8 TCDD 02 = Total PCDD/DF03 » Total and ISOMER specific PCOD/OF04 =
Film Roll No. 04 Frame No-
Sample Team D.Peery, D.Simerly(Initi.i?c'l
Prepared By D- Peery Ck'd By DSS
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SPECIMEN COLLECTION G DATE8
TIME--01
74.
04
63
8 8PROJECT NAME: JACKSONVILLE/LOCATION- OFFSITE——-"• * — vii • - , •ii n iJacksonvil le,ArkansasPROJECT ff 480078 01 09 01
SAMPLE if- WH1753LFMS
Gizzard Shad
Gill Nets
Dry Ice
Specimen Type
Species
Collection Method
Preservation Method
LAKE DUPREESample Location Description
PI Prep Lab AU = Austin CE = Cerritos DI = Directors ED = Edison FM = FAS MobileHK = Hiddlebrook PI = Pittsburgh SC = Santa Clara
_^_ Analysis Request: 01 = 2,3,7,8 TCGD 02 = Total PCDD/DF03 = Total and ISOMER specific PCDD/DF04 '
Film Roll No. Frame No. 25
Sample Team D.Peery, D.Simerly^^mtials)
Prepared By D- Peery Ck'd By DSS
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SPECIMEN CULLECTIUN J6 DATE-
TIME80
1 .
7
•i
0
0
65
8 8PROJECT NAME: JACKSONVILLE/
OFFSITELOCATION:„ Jacksonville,Arkansas
PROJECT ff 480078 01 09 01
SAMPLE ff WH1754LFHS
White Crappie
Pomoxi's annularis
Gill Nets
Dry Ice
Specimen Type
Species
Collection Method
Preservation Method
LAKE DUPREESample Location Description
PI Prep Lab AU = Austin CE = Cerritos 01 = Directors ED = Edison EH = FAS MobileMK = Middlebrook PI = Pittsburgh SC = Santa Clara
Analysis Request: 01 = 2,3,7,8 TCOD 02 = Total PCDD/DF03 = Total and ISOMER specific PCDD/DF04 =
Film Roll No. W Frame No. 26
Sample Team D.Peery, D.Sinierly(Initialsl
Prepared By D- Peery Ck'd By DSS
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EJJ SPECIMEN CULLECTIUN •J6 DATE8
TIME'
0
1
75
03
60
8 8PROJECT NAME: JACKSONVILLE/
LOCATION: OFFSITEJacksonvil le ,Arkansas
PROJECT ff 480078 01 09 01
SAMPLE f f M H 1 7 5 5 L F M S
W h i t e Crapp ie
Pomoxis a n n u l a r i s
G i l l nets
Dry Ice
Specimen Type
Species
Collection Method
Preservation Method
_tl&_
NA
Age
Sex
50 qr Weight1 5 - 5 cn1 Length
NA Girth
NA
NA
Sample Location Description LAKE DUPREE
PI Prep Lab AU = Aus t in CE = Cerritos DI = Directors ED = Edison FH = FAS Mobi leMK = Middlebrook PI a Pittsburgh SC = Santa Clara
01 Analysis Request: 01 = 2,3,7,8 TCDD 02 = Total PCDD/DF03 = Total and ISOMER specific PCDD/DF04 =
Film Roll No. Frame No.04 27
Sample Team D.Peery, D-Si 'mer ly( I n i t i a l s )
Prepared By D- Peery Ck'd By DSS/ T - i- + < -
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03 SPECIMEN COLLECTION JG DATE'
TIME'0
0
7q
00
7
0
8 8PROJECT NAME .'JACKSONVILLE/LOCATION- OFFSITE——•"—' " •J" • •, , • i ^ A iJacksonville,ArkansasPROJECT # 480078 01 09 01
SAMPLE # WH1756LFMS
M h i t e C r a p p i e
Pomoxis annu la r i s
Gin nets
Dry Ice
Specimen Type
Species
Collection Method
Preservation Method
LAKE DUPREESample Location Description
PI Prep Lab AU = Austin CE = Cerritos DI = Directors ED = Edison FM = FAS MobileMK = Itiddlebrook PI = Pittsburgh SC = Santa Clara
_^_ Analysis Request: 01 = 2,3,7,8 TCDD 02 = Total PCDD/DF03 = Total and ISOMER specific PCDD/DF04 =
Film Roll No. Frame No-W 28
Sample Team D.Peery. D.Simerly('"•'tials)
Prepared By 0. Peery Ck'd By DSS(Initials)
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SPECIMEN COLLECTia. .06 DATE-
TIME8Q0
79
00
70
8 | 8PROJECT NAME: JACKSONVILLE/
LOCATION: , 01:FSITE . .Jacksonville,ArkansasPROJECT ff 480078 01 09 01
SAMPLE ^WH1757LFMS
Bowfin
Ami a calva
Gill Nets
Dry Ice
Specimen Type
Species
Collection Method
Preservation Method
_UA_
NA
NA
NA
Age
Sex
370 qr Weight
53 .2 ^ Length
NA Girth
Sample Location Description LAKE DUPREE
PI Prep Lab AU = Austin CE = Cerritos 01 = Directors ED = Edison FM = FAS MobileHK = Hiddlebrook PI = Pittsburgh SC = Santa Clara
_0_ Analysis Request: 01 = 2,3,7,8 TCOD 02 = Total PCDO/DF03 = Total and ISOMER specific PCOD/DF04 =
Filni Roll No-
Sample Team D( I n i t i a l s )
04
-Peery,
Frame No-
D.S imer ly
29 & 30
Prepared By D. Peery Ck'd By DSS(Initials)
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SPECIMEN COLLECTIUl _OG DATE-
TIME'01
70
00
70
8 8PROJECT NAME: JACKSONV I LLE/LOCAT I ON: OFFSITE
„ Jacksonville,ArkansasPROJECT if 480078 01 09 01
SAMPLE H- WH1758LFMS
Blue Catfish
I c t a t u r u s furcatus
Gill Nets
Dry Ice
Specimen Type
Species
Collection Method
Preservation Method
Sample Location Description LAKE DUPREE
01 Prep Lab AU = Austin CE = Cerritos DI = Directors ED = Edison FM = FAS MobileHK = Biddlebrook PI = Pittsburgh SC = Santa Clara
_m_ Analysis Request: 01 = 2,3,7,8 TCOO 02 = Total PCOO/OF03 = Total and ISOMER specific PCDD/DF04 =
Film Roll No. Frame No.Ot 31
Sample Team D-Peery, D . S i m e r l y( I n i t i a l s )
Prepared By D . Peery Ck'd By DSS(Initials)
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SPECIMEN COLLECTIL LOS DATE-
TIME'0
1
7
n0
?7
n8 8
PROJECT NAME: JACKSONVILLE/
LOCATION: , OFFSITE , „,, Jacksomnlle.ArkansasPROJECT ff 480078 01 09 01
SAMPLE S WH1759LFMS
piiio Catfish
[c ta lurus furcatus
Gin nets
Dry Ice
Specimen Type
Species
Collection Method
Preservation Method
Sample Location Description LAKE DUPREE
PI Prep Lab AU = Austin CE = Cerritos DI ° Directors ED = Edison FH = FAS MobileHK. = Kiddlebrook PI = Pittsburgh SC = Santa Clara
_M_ Analysis Request: 01 = 2,3.7,8 TCDD 02 = Total PCOD/OF03 = Total and ISOMER specific PCDD/DF04 =
FiTn Roll No. t)4 Frame No- 32
Sample Team O.Peery, D.Sjmer1y_[ In i t ia l s )
Prepared By P. Peery Ck'd By DSS(Initials)
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APPENDIX B
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STANDARD OPERATING PROCEDURE
ITAS-SPECIAL ANALYSIS LABORATORY
TITLE:
EXTRACTION METHOD FORBIOLOGICAL SAMPLES
SOP NO: SALS 09DATE INITIATED: 01/15/86REVISION NO: 3DATE REVISED: 10/23/87PAGE 1 OF 5
PREPARED BY APPROVED BY DATE QA CONCURRENCE DATE
^^•^^ ^^^< ^//^ c^i-Q^w- ^sr
/ ^1.0 PURPOSE
This analytical method describes the procedure used to extractdioxins and dibenzofurans from biological samples.
2.0 APPLICATION
The biological tissue sample is spiked with an internal/surrogatestandard mixture and blended with dry ice. The sample is jar-extracted with acetonitrile and concentrated by standard K-Dtechniques in preparation for cleanup steps.
3.0 REFERENCES
3.1 RCRA SW-846, Method 8280 (September 1986 revision)
3.2 EPA Method 613 Federal Register; Vol. 49, No. 209;43368-43373.1984
3.3 Bruailey, W. C. , J. A. G. Roach, J. A. Sphone, P. A.Dreifuss, D. Andrzejewski, R. A. Niemann, and D.Firestone, 1981, "Low-Resolution Multiple Ion DetectionGas Chromatographic—Mass Spectrometric Comparison ofSix Extraction—Cleanup Methods for Determining2,3,7,8-Tetrachlorodibenzo-[-dioxin in Fish", J. Agric.Food Chem. 29, 1040-1046.
3.4 Harless, R. L., E. 0. Oswald, and M. K. Wilkinson,1980, "Sample Preparation and Gas Chroniatography--MassSpectrometry Determination of 2 ,3 ,7 ,8-Tetrachlorodibenzo-p-dioxin", Anal. Chem. 52 ( 8 ) , 1239-1245.
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SOP NO: SAL309DATE INITIATED: 01/15/86REVISION HO: 3DATE REVISED: 10/23/87PAGE 2 OF 5
4.0 ASSOCIATED SOPS
4 . 1 ITAS-SAL SOP No. 312, "Caustic and Acid Cleanup".
4. 2 ITAS-SAL SOP Ho. 1001, "Safety Procedures".
5.0 PROCEDURE
5.1 Reagents
5 . 1 . 1
5 . 2
5 . 1 . 2
5 . 1 . 3
5 . 1 . 4
5 . 1 . 5
5 . 1 . 6
5 . 1 . 7
5 . 1 . 8
Cautions
5 . 2 . 1
5 . 2 . 2
Spiking standard solutions; for isoroerspecific and totals analysis, samples will bespiked with C^-2, 3 , 7,8,-TCDD internalstandard at a concentration of 500 ng/ml and"d^^iS^ ,a-T!CDD surrogate standard at aconcentration of 100 ng/ml, plus ,,C-labeledPenta CDD, Penta CDF, Hexa CDD, Hexa CDF,Hepta CDD, Hepta CDF and Octa CDD, at aconcentration of 500 ng/ml and all in thesame isooctane solution.
Sodium Sulfate - ACS, granular, anhydrous.Prepare by heating to 450-C for 16 hours.After preparation, store in glass jars atroom temperature.
Dry ice.
Acetonitrlle; UV grade.
Methylene chloride, pesticide quality orequivalent.
Hexane; pesticide quality or equivalent.
Acetone; technical grade.
Toluene; pesticide grade or eguivalent.
Samples received for this preparationprocedure are of unknown composition, but maybe of potentially carcinogenic, mutagenic,toxic or in other ways hazardous.
It is mandatory that the initial weighing ofthe samples, addition of isotopically labeledcompounds and mixing of the sample beperformed inside the designated dioxin hoodin the high hazard laboratory.
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SOP NU; SAL309DATE INITIATED: 01/15/86REVISION NO: 3DATE REVISED: 10/23/87PAGE 3 OF 5
5 . 0 PROCEDURES (CONTINUED)
5 . 2 . 3 Personnel involved in this sample preparationprocedure shall be thoroughly familiar withlaboratory SOPs on the processing of highhazard samples. (See ITAS-SAL SOP No. 1001,"Safety Procedures".)
5.3 Glassware - All glassware and stainless steel (blendercups, spatulas, etc.) used in sample preparation andcleanup procedures are solvent rinsed. The solventsused are acetone, toluene, methylene chloride andhexane, in this order. Allow to air dry in a hood.
5.4 Equipment and Materials
5 . 4 . 1 Blender.
5 . 4 . 2 Amber colored glass jars with teflon linedscrew caps - 240 al.
5 . 4 . 3 Platform shaker.
5 . 4 . 4 Snyder columns, three ball macro.
5 . 4 . 5 500 ml round bottom flask.
5 . 4 . 6 Heating mantle.
5 . 4 . 7 Concentration device; nitrogen blow downapparatus, N-EVAP.
5 . 4 . 8 Glass funnels, short stem.
5 . 4 . 9 Filter paper, Whatman No. 4 or equivalent.
5.4. 1 0 Analytical balance.
5.4.11 Separatory funnel; 125 ml volume.
5.5 Extraction
5 . 5 . 1 Prepare designated dioxin hood as instructedin laboratory SOP for processing high hazardsamples.
5 . 5 . 2 Weigh out 10 grams of the sample and transferto a stainless steel blender jar.
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SOP NO: SAL309DATE INITIATED: 01/15/86REVISION NO: 3DATE REVISED: 10/23/87PAGE 4 OF 5
5.0 PROCEDURES (CONTINUED)
5 . 5 . 3 Spike sample with 100 ul of spiking solution,containing both internal and surrogatestandards, adding the solution to severalsites over the surface of the sample.
5 . 5 . 4 Add 100 grams of anhydrous granular sodiumsulfate into blender jar and blend mixturefor approximately 1 minute.
5 . 5 . 5 Add 50 grams of dry ice and blend until thesample is thoroughly powdered.
5 . 5 . 6 Transfer powdered sample into 240 ml ambercolored glass jar. (The screw cap for thisjar must have a teflon liner.) Rinse blenderjar several tines with acetonitrile. Therinsings plus enough additional acetonitrileto make up 150 ml are then added to the glassjar.
5 . 5 . 7 Shake mixture on electric platform shaker for2 hours.
5 . 5 . 8 After shaking, filter mixture through glassfunnels lined with No. 4 Whatman filter paperinto 500 ml round bottom flask. Rinse theglass jar 3 times with small amounts ofacetonitrile, adding these rinsings to flask.
5 . 5 . 9 Concentrate extract volume down toapproximately 5 ml in the round bottom flaskusing Snyder columns and heating mantle.
5 . 5 . 1 0 Transfer the concentrated extract to a 125 mlseparatory funnel. Rinse flask several timeswith acetonitrile, then several times with atotal of approximately 15 ml of hexane andadd this to the separatory tunnel. Proceedto caustic and acid cleanup of extract, SOPNo. SAL 312.
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SOP NO: SAL309DATE INITIATED: 01/15/86REVISION NO; 3DATE REVISED: 10/23/87PAGE 5 OF 5
5.0 PROCEDURB (CONTINUED)
5 . 6 Cleanup of Glassware
5 . 6 . 1 After use, glassware is solvent-rinsed withtoluene and methylene chloride. Wash withdetergent and rinse with copious amounts oftap water and several portions of distilledwater. Place glassware in oven and heat to400'C for 30 minutes. Remove from oven whencool and store in clean environment.
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I INTERNATIONALTECHNOLOGY
I CORPORATION
FIBAL DIOXCT REPORT
TOR
JACKSONVILLE OFFSITE
VOLUME I
KEPORT A11D DATA SUMMARY
PREPARED BY IT ABALYTICAL SERVICES
KBOXVILLE, TEBBESSEE
JOLT 26, 1988
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JACKSONVILLE OFFSITE
Case Narrative
Ten (10) fish were received on 07-08-88 for the analysis of2,3,7,8-TCDD (please see Table 1 ) . The samples and blankwere spiked with an internal standard/surrogate mixturecontaining 5. 0 ng 13C-2 , 3 , 7 , 8-TCDD and 1.0 ng :i7Cl-2,3 , ' J , 8 -TCDD. The samples were extracted utilizing ITAS developedprocedures. Sample extracts were analyzed using a modifiedversion of the,EPA reference method described in "RCRA SW-846, method 8280," revised September 1986.
sample Preparation
Fish samples (fillet only) were ground and homogenized. Ten(10) grams of the sample and ten (1 0 ) grams of sodiumsulfate (a blank) were weighed into separate jars. Thesamples and blank were spiked with the internal standard/surrogate mixture and allowed to stand overnight foreguilibration, followed by an extraction utilizing ITASmethodology.
Sample Cleanup
To aid in the removal of chemical interferences, the samplesand blank were first treated using separatory funneltechniques found in Option C of the U . S . Environmental Pro-tection Agency, Region VII Protocol for "The Determinationof 2,3,7,8-TCDD in Soil and Sediment," September 1983 revi-sion. Extracts were washed with 20% KOH and distilled waterfollowed by three concentrated HySO^ washes. Further clean-up consisted of two steps of column chromatography, Thefirst step involved a neutral alumina column while thesecond was a dual column system utilizing acid-modifiedsilica gel followed by neutral alumina. Final extracts wereconcentrated to near dryness and raised to 50 p.1 with aisooctane.
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GC/MS Analysis
Isoner Specific TCDD - The sample extracts were analyzedusing HRGC/HRMS scanning in the selected ion monitoring modefor enhanced sensitivity. The column used for this isomerspecific analysis was a 60 m SP-2331 fused silica capillarycolumn. Before acquisition of the sample data, a sevenisomer performance mixture containing the six most closelyeluting TCDD isomers was run.
In addition, a five point calibration plot was run intriplicate. The mean response factors obtained from thisfifteen point calibration were used for all subsequentcalculations (see Table 2 ) . The shift standard, analyzed onthe same day as the samples, produced a response factorwithin 10% of the fifteen point curve for TCDD (please seeTable 3 ) . Accuracy of the method is obtained by therecovery of ^Cl-TCDD versus ^C-TCDD.
GC/MS Results
Isomer Specific TCDD - The results for the isomer specificanalysis, shown in Table 4, are reported in ppb. Adetection limit is calculated from 2 . 5 times the signal inthe area of the elution of ^C-TCDD whenever a samplecontains no detectable 2,3,7,8-TCDD.
QA/QC
Table 5 lists the results of the QA/QC samples. In allcases, precision and accuracy are within the limitsestablished for acceptance of dioxin/dibenzofuran data.
sm(bwlO)
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APEEBDIX A
CROSS REFEBHICE U:ST
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TABLE 1
CROSS REFERENCE LIST
IT SAMPLE
BB0546
BB0547
BB0548
BB0549
BB0550
BB0551
BB0552
BB0553
BB0554
BB0555
# CLIENT
WH1750
WH1751
WH1752
WH1753
WH1754
WH1755
WH1756
WH1757
WH1758
WH1759
SAMPLE
LFMS
LFMS
LFMS
LFMS
LFMS
LFMS
LFMS
LFMS
LFMS
LFMS
MATRIX
BUFFALO FISH
BUFFALO FISH
SHAD FISH
SHAD FISH
CRAPPIE FISH
CRAPPIE FISH
CRAPPIE FISH
BOW FIN FISH
CATFISH
CATFISH
sm(bwlO)
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0 -.
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TABLE 2
INITIAL CALIBRATION SUMMARY
TCDD/TCDP
JACKSONVILLE OFFSITE
Date
11-02-87
11-02-87
11-02-87
11-02-87
11-02-87
11-02-87
11-02-87
11-03-87
11-03-87
11-03-87
11-03-87
11-03-87
11-03-87
11-03-87
11-03-87
CC1CC2CC3CC4CC5
Instr.ID
70-250S
70-250S
70-250S
70-250S
70-250S
70-250S
70-250S
70-250S
70-250S
70-250S
70-250S
70-250S
70-250S
70-250S
70-250S
Mean
37
61220
Sol.ID
CC1
CC1
CC1
CC2
CC2
CC2
CC3
CC3
CC3
CC4
CC4
CC4
CC5
CC5
CC5
RF Used (x) =
% RSD =
Cl
pg/nipg/^ipg/^i
NatTC
0.
0.
0.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1-
7.
ive:DD
952
959
924
05
03
06
07
10
06
02
02
07
13
17
20
05
3
10 pg/ul50 pg/iil
loo pg/^il1000 pg/(xl3000 pg/|il
Measured RFNative
TCDF
1.88
1.86
1.91
1.99
2.03
2.04
2.10
2.33
2.28
2.09
1.82
2 .30
2 .42
2.63
2.74
2 .16
1 3 . 0
Natives
%
0.
0.
0.
0.
0.
0.
0.
1.
0.
0
5
ogate-TCDD
931
923
846
956
951
948
974
03
949
.945
.1
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KPPSSDJX C
ISOMBB SPHGIFIC COH'nBniBG CALIBRATIOH SUMMARY
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TABLE 3
ISOMER SPECIFIC CONTINUING CALIBRATION SUMMARY
JACKSONVILLE OFFSITE
BATCH 1195
Date
07-17-88
07-17-88
07-17-88
07-18-88
07-18''-88I
07-18-88
Instr.ID
70-250S
70-250S
70-250S
70-250S
70-205S
70-250S
SolID
PC
CC1
PC
PC
CC1
PC
Measured RFNative SurrogateTCDD —Cl-TCDD
1.08 1.00
1.08 0.972
RatiNativeTCDD
1.03
1.03
o rrleas/Mean)Surrogate-'Cl-TCDD
1.06
1.03
TCDD IsomerResolutionPet. Valley(Applies ForPC Only)
7 .9%
5 . 4 %
6 . 8 %
7 . 4 %
Solution ID Codes:
PC = Performance check solutionCC1 = Concentration calibration solution #1 = 10 pg/ul
sm(bwll)
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APPEHDIX D
ISOMER SPEGrFTC DATA SUMHABI
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fABLE 4
2,3,7,8-TCDD RESULTS
Lab: IT/SAL
Case No; Jacksonville Of fs i te
Batch/Shipment No. 1195
Column: 60 Meter Sp-2331
Instr. ID. 70-250 S
Sample
Client
UH1750LFMS
"H1751LFHS
UH1752LFMS
WH1753LFMS
UM1754LFMS
MH1755LFMS
WK1756LFMS
WH1756LFMS
yH1756LfMS
KH1757LFMS
UH1758LFHS
UK175tLFHS
RB
a Corrected
RB - Reagent Blank FB - Field Blank
0 • Lab Duplicate FO - Field Duplicate
BS • Blank
MS • Matrix
MSO - Matrix
»
IMS
BB0546
BB0547
BB0548
BB0549
BB0550
BB0551
BB0552
BB0552HS
BB0552MSD
BB0553
BB0554
BB0555
BLK1195
for contributi
Spike
Spike
Spike Duplici
Uet Ut.(q)
ND - Not Detected
DL • Detection Limit
Aliouot
10.0
10.0
10.0
10.0
6.76
6.46
10.0
10.0
10.0
10.0
10.0
10.0
10.0
ion by native
ate
PPB T
Meas.
O.Oil
0.25
0.0099
0.48
0.046
0.029
O.OS1
0.14
0.12
0.01!
0.06S
0.23
ND
TCDD;
OL Date
(0.0019) 07-17-88
I:DD GC/MS Ana
07-17-88
07-17-88
07-17-88
07-17-88
07-18-88
07-17-88
07-17-88
07-17-88
07-17-83
07-17-88
07-17-88
07-17-88
0.9% of m/l 322 subtracted.
lysis
Time
13:46
14 :19
14:51
15:26
1'.;17
1*:32
17:05
19;20
19:54
17:40
18:13
18:46
13 :11
Ret. Ion
320/322
0.83
0.82
0.80
0.83
0.75
0.87
0.75
0.81
0.79
0.85
0.72
0.76
.»t'"nd...332/334
0.76
0.80
0.85
0.77
0.75
0.80
0.75
0.72
0.80
0.82
0.80
0.77
0.81
PpB Sl
Meas.
20.2
20.7
21.5
23.4
21.2
22.4
20.8
22.3
21.6
20.3
20.9
19.5
21.9
Ji-rogate
» Acc'v
101
103
108
117
10*
1 1 2
104
1 1 2
108
102
104
98
1 1 0
320
66.25
621.84
27.71
1402.34
100.38
53.83
58.79
196.88
169.39
36.98
155.88
840.46
Relatf
322
79.58
759.77
34.42
1680.30
133.36
61.65
78.27
244.24
213.71
43.54
216.92
1098.60
ve Ion Abur
259
50.55
601.35
25.96
1304.06
101.87
46.35
61.77
189.85
217.40
31.08
156.48
707.37
ufance
32Sa
421.28
520.59
607.16
668.79
713.10
628.22
410.04
327.93
296.38
551.54
517.21
744.74
620.72
332
956.36
1188.69
1369.55
1311.88
1521.37
1314.14
894.75
653.61
642.44
1292.28
1164.67
1753.62
1343.44
3 '.
1^1.34
1476.60
1617.11
1711 .61
2028.83
1615.44
1194.26
901.89
805.56
1580.24
1456.58
2<.. .I*
1655.53
sm(bu14)
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APPBBDIX E
QA/QP SUMMARY
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TABLE 5. QA/QC REPORT i
Project Name Jacksonvi I Ie Offsite______Code ITFK25558___ Surrogate Percent Accuracy
Batch Mumber 1195______________________________MRHS Isomer.
Sample Matrix Fish________Extraction Method Special_______ ^ec1 lc
Report Date 08-12-88______________________________ Muntier of Data Points = ____17____
BC/MS Run Date CIsomers) 07-17-88__________________ Mean Percent Accuracy = 107%
Range' = 98-117%
Sample » BB0552_______
2,3,7,8-
Precision of Duplicates TCDD
Spike Oup. Value (a) » 0 .12
Spike Value (b> = 0.14
Precision = |a-b| x 100X = 15.4%
a»b
2
EPA Rang;- = 50%
^ 2,3.7,8-
Accuracy of Spike TCDD
Observed Spike Value (b) = 0.14
Orig. Value (a) s 0.031
Spike Levrl (c> = 0.10
Accuracy = b-a x 100% = 109X
c
EPA Range = 60-140%
EPA Range fo; surrogate percent accuracy is 60-140X for 2,3,7,8-TCDD only.
sm(bu14)
•"I '•
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INTERNATIONALTECHNOLOGY
I CORPORATION
FIBAL DIOXCT REPORT
FOR
JACKSOHVILLE OFPSITE
VOLUME 11
IBITIAL ABD CONTIBUIBG CALIBRATIONS AHD DATA
FREPAEED BY IT ANALYTICAL SERVICES
KBOXVILLE, TEHBESSEE
JULY 26, 1988
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ISOMER SPECIFIC IHITIAL CALIBRATION
11-03-87
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•111^15 £-NO'rS? 12.34PH53S (uO Sus^OSTD;F: 1 . 31S.373£ K . 313.8378 U 321,3349 ^ 32?.3e4? N . 331.3363T.;.:t^lJLSTD I - 18PG/ULRUN ^
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tnr-LE 1 INJECTION 1 G R O U P 1 CHANNEL 3t5. 94.
AREA RETENTION TIME
i 1. &St'?A'?E*<i3 i t ;29:37
.2 S. &925S2E*®! »:3a:i»6
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AMPLE 1 INJECTION 1 5ROUP i CHANNEL 317.9»
A R E A RETENTION TIME
1 2. 17748»E<-»3 i.'i:29:37
£ 1. 137177E-162 »:3i»:»&
3 3. lS7?53E»ei B:31:42
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'U1@£I5 £-NOV-3? 1^34?8-250S CEI^) S^ISOSTD;? 1 ^ 249,163£ B ^ £42,9343 ^ £53.9c98 [ 30£,965£ E ' 303.S93?'.;.:;t UL STD I - 19PG/UL.RUH #1ir,'.'i
•^ V'i, '^C - TC^i-
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, -^ --: n' • • o->, •-•-i'.>r--co
c i 03i— co*' 0 —
»—. •-•-•«-0 •S:'•—• c'~"I..-1 - -
C«JIur:'f-fff-ff0-1•33C"":'
^^\J-1. <-'-'
COLOi0_I
r-ff • -tSf •—:•H-« CXJ0-1 =»*=
I iT-ir^' -T- 3=r-^- O? r-3
•3r:« Ot:<3.:< " --0-J 0-1 __I
- - —a- : '0-> 0-1 '---.-— c=« __
- - ' ' 1- "-1oai ica> — ..r--'. -— ^_co ,_,
• o-i • .r- 0~" T,_i
ICT CO »—— 0-1
T" '" I=J| -r-0-1 •35i I—— -j-
••vt- CO f—,
'"'-'—I A•-C« •3= ' 4-
0^ OJ Bl——————.——————^———«-———^—————T-- - •'• i •S.:' CS:i <S:' fS.1 'SJ '"a CS' •'S'l
i _ •;"!: li i.-t •::l~. .COi »••-•.. <:)0 !-€•» •-I*-' i':"-i '-".I
.-- ; 1 - " ''
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•maaifi HON? i3^7H5@3 CE!-) SUS^ISISTD^ 1 J ^ 313,9?9£ K ^ 313,83?9 L = 321.3348 ^ 32P.834? }•{•• 331.3368M^lflTIVE TCDD VS, 13C-TCDO
l Q ^ C S l , n , G l , hOCI ' ^ = 214,93 T = ^ 4 B 4M.?^-
.3]_______________,' ^ ® _______ ' .-1^J('£1,I1,G1 ' , ' T,^| ' ' / t i = 45^.7? T = £ 6 ^ 4 @ 3£.48?^
a^——————————————, /iSn^, . i i i , . i i . i>,.^71B9-L 31,11,01 . ^ 1,^| ' / R = 5o^G T = £ 6 ^ 4 0 16^.
fi I / '••- (^/
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AMPLE t INJECTION 1 6ROUP 1 CHANNEL 3»3.1H
AREA RETENTION TIME
1 1. 18'?3B2Ei-<il »:27:'»A
2 8.73283»E*S£ »:29:'tl
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aMPLE 1 INJECTION 1 GROUP 1 CHANNEL 3i»6. fiH
AREA RETENTION TIME
1 1. 14.9A4SE-93 a :29 :41
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?MFLE I INJECTION 1 GROUP 1 CHANNEL 331.9t
AREA RETENTION TIME
1 4. 8l»'H72E-n»3 «: 2A: 39
2 5. 18A1S7E**! i>:31:t i
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•MFi-E 1 INJECTION 1 G R O U P i CHANNEL 33S. 93
AREA RETENTION TIME
1 fe. i89153i»E*t3 «: 24: 39
2 5. 3931S7E*B1 i?:31:i?l
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-Ui02I6 2-NOV-S7 13^?@-25@S CEI^) 3^I30STD^ 1 ^ 240,1692 B ^ 242.9349 C ^ 253,9298 D ' 392,3652 ^ 383.3S3?fe^TIVE TCDF VS. 13-C-TCDO
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?r1Pl.E 1 INJECTION 1 GROUP 1 CHANNEL 3 3 1 . 9il
AREA RETENTION TIME
1 2. <;&239&E»iiiS »:2&:il«i
: 1 lS3*37E*ai ii..31:iiil
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,°LE i IMJECTIOri l ^fiOJr i ::•; ••.;>IKEL 33'3 °3
•°ei RETENTION TIME
2 c a"il-^^lE-»-'-'-l ^ 'I ''"
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U1S£F £-NOV-;r 14^3'5-^S (EK- S^'ISOSTO•R 1 R ^ £43,1S3£ 8' £4£,Sa49 C ^ E5S.923S D ^ 382.S£5£ ^ 303.8987^^NfiTIVE TCDF ^, 13-C-TCDD
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199 031,11,01 . ^2^-^ . . . • ^^
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108|C £1.11,01 . ^'^I.^I ' 1 ^)^= 1^.93 T = 26^41 ££4
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inFLE I INJECTION 1 GROUP i CHANNEL 3l>3. 981
AREA RETENTION TIME
1 A. 3efl.AS7E*itl <r27'.»7
2 a.9«£128E*«3 »:2? 41
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aMPLE 1 INJECTION 1 GROUP 1 CHANNEL 3M.'?iii
AREA RETENTION TIME
1 a. &8S453E*»1 »:27:ii&
2 s.287795E*»3 «:29:'U
3 1. <398i»*E->-i»2 «:3i>:i»<?
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aMPLE 1 INJECTION 1 GROUP 1 CHANNEL 331. '?•>.
AREA RETENTION TIME
1 It. 9il755E--e3 i»:2&:»®
= 6.'t25931E*«H »:31: '»1
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<MPLE 1 INJECTION 1 6ROUP t CHANNEL 333 .93
AREA RETENTION TIME
1 &. J<i&*71E»®3 a:26:fl.B
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fR = £3^.96 T = 26^40 ^.1 'i /^T^)"•.. (1^
1@0JS1, I1 ,G1 ' ' ' . / . q^ , 1.80I • ' \^-- 1214.48 T = 26^49 6 ' ' 221
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2.MPLE 1 INJECTION i GROUP 1 CHANNEL 3<3.fS
AREA RETENTION TIME
1 &. a3173.i»E-i-<ll »:27:ii7
•.: ». AS41»8E*l!l3 H: 29: 11
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.(IPLE 1 INJECTION 1 GROUP 1 CHANNEL 3as. f*
AREA RETENTION TIME
1 7. 5i>A(>S3E->-ei «;27:»A
S 5. 927&24E-1-B3 a: 29: 11
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aMPLE 1 INJECTION 1 6ROUP 1 CHANNEL 331.fl
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M1FLE 1 INJECTION 1 GROUP 1 CHANNEL 333.93
AREA RETENTION TIME
1 5. a»l»178E»e3 8:26:39
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^10219 2-NOH7 15^378-£5@S (EI^) Sus^ISOSTDOR 1 ^ £40.1692 B ^ £4£.9349 ^ £5S.9£98 D ^ 392.3652 ^ 3@3,89S7T p x f c ^ f l T I V E T C D F V S . 13-C-TCDD
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'112118 £-NOH? 16^1 P8-250S CEM Sus^ISOSTDJR 1 .1^ 318,9?9£ ^ 319.83PS L ^ 3£1,S94@ ^ 3£?.884? N ^ 331.9363' e x L ^ N f l T I V E T C D O V S . 13C-TCDD
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,MPLE 1 INJECTION 1 SROUP 1 CHANNEL 3'?3. 9<"
ABEA RETENTION TIME
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*HPLE t INJECTION 1 GROUP 1 CHANNEL 3*5.99
AREA RETENTION TIME
1 5. »4i8595E<->»i a:27:l>e
2 &. SiAlliAE-fiB » :29 :42
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-"PL"; 1 INJECTION 1 GROUP I '-riaf-Ni
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^112111 2-NOV-37 17^170-2583 (EM S^ISOSTO^ 1 J ^ 31S,9792 K ^ 313,8378 L 3£1.894@ ^ 327.3847 N ' 331,3388T £ ; ! L ™ V E T C O D V S , 13C-TCDD
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IMFLE 1 INJECTION 1 GSOUP 1 CHANNEL 242. ?3
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DATA
BATCH 1195
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TCDD ISOMER SPECIFIC
DATA SUMMARY
IT SAMPLE «_____^__- DATE ANALYZED:,
TIME ANALYZED:
^et 2,3,7,8-TCDD Detection Surrogate Surrogat>Weight/ Con^. Limit 320/322 332/334 Measured PercentVolume n<t .PPtr' npt; nq ppb opt ro.67-0.90) (0.67-0.90) (PPb) Accurac-.
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'D - Not DetectedS - Native TCDD SpikeD - Duplicate (Intralab)
Corrected area 328 [328 - (0.009 x 3 2 2 ) ]
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W 17-JUL-8813^4S ?6-25eS i:E!^5 S^LSOSTD;' 1 K ' 31S,83?8 L ' 321,5548 B' 327,^ ^ 331.33S8 0' 333,9333al^TI'f'E TCDO, 3?i;L, ffi 13C-TCDD
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TCDD ISOMER SPECIFIC
DATA SUMMARY
IT SAMPLE f ^;<^—,-^/7DATE ANALYZED:
TIME ANALYZED: / ' - / . / /
Net 2,3.7,8-TCDD Detection
Weight/ Cony. Limit 320/322 332/334y01""16. n<7(J3pB pp<- ncr ppb ppt (•0.67-0.901 10.67-0.901
-• "- C^ ,•••'. '
SurrogateMeasured(PPb>
^. 7
Area332
Area_334
Area320
c^t, y /
Area322 „
^^"^
Area259
Area*328
COMMENTS;
'.0 - Not DetectedS - Native TCDD SpikeD - Duplicate (Intralab)
Corrected area 328 (32S - (0.009 x 3 2 2 ) ]
Checked By: ^^^ 7,/^^
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'! IS'II 'IS^WHSIJ 381 «3 H\
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TCDD ISOMER SPECIFIC
DATA SUMMARY
IT SAMPLE < ^'6-^-y DATE ANALYZED: ^^-^
TIME ANALYZED: /. S-/
Net 2,3,7,8-TCDD Detection Surrogate SurrogateWeight/ Cope. Limit 320/322 332/334 Measured Percentvolume M fab pp» nq ppb ppt f0.67-0.90\ f0.67-0.90L fPPb) Accurac\
rea Area Area Area Area Area*——— - 2-i 320 322 259 328
-/v^ tjd2_iL 77,7/ ;c/ Js-^ ,^.^,
COMMENTS; ^ ; , , .3<,'-y ^ ^-^ /3 '
0 - Not DetectedS - Native TCOO Spike0 - Duplicate (Intralab)
Corrected area 328 (328 - (0.009 x 322 ) ]
Checked RV. ^/^
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» 17-J1JL-S3 14'51 ;'H58S (Eh5 SusW..•' 1 ^ 313,83?3 U 321.S348 B ^ 32?,3W ^ 331.936S 0' :B3,333SH t ' H f l T I ' / E T e [ D , 3 7 C L , W D 1 3 C - T C D D
' / ^/ , .«/ ' • "
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TCDD ISOMER SPECIFIC
DATA SDHMARy
IT SAMPLE »__i;%/" $""' /9 DATE ANALYZED:_____7- / ^•'.-^
TIKE ANALYZED:____/^~ ' ^ {:
NetWeight/Volume
2,3,7,a-TCDO DetectionCone. Limit
rcr^D&.Dpt nq ppb opt
Surrogate Surrogate320/322 332/334 Measured Percent
f0.67-0.90> (0.67-0.90) _fppb) Accuracy
^-^'L /.7.-77 ,yf,'/ ,/•</'-
Area332
Area*328
Area334
Area320.
Area322
Area
•/: /, /"/'// l'/^ ^'/ //•• S'"'- J/0
COMMEMTS: / ^ / ' ' ' ' /^ •S f > ' i / ' f ' ' : ' l ' L -'^ ^l^
SD - Not DetectedS - Native TCDD SpikeD - Duplicate (Intralab)
•corrected area 328 (32S - (0.009 x 322)]
Checked By: ^^} ••7-/^'P'
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i^c- .^-.y ^ 7 -• /
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3 17-.JIJL-3S 15^6 ?8-258S (EI») SUS^ISOSTD^ 313.897S L ^ 321,S94@ t 327.SM7 ^ 331,336S 0' 333,93;I BB8549 18G FISH
N^C 31,11,01
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17-11-S315^6 78-256S (EH^ mm [.••• 3E1.3948 B' 327.SS47 H: 331,9368 0^ 333,S33S
COD, 37CL, M 13C-TCDO
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TCDD ISOMER SPECIFIC
DATA SOMKARY
IT SAMP3
NetWeight/
Area. 332
/^/. 3^
-E <
2,3
P<7
(
^?^5-^
,7.8-TCDDCone./055> ppf
y.^yfa
Area-32A
^^S--^3
7
DetectionLimit
ng Dob not
Area320
/C€>.'^y
E
I
320/322r0.67-0.901
^.^
Area322
/33.
>ATE AN?
THE ANA
332(0.67
£>•
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iLYZED:
.LYZED:
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7'3'
Area
/(5/5
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^ ' - / , / ~ ^
SurrogateMeasured
<DDb)
31-^
Area*-328
1 ;;> 77-?, /^
^^r
Surrogat'PercentAccurac'.
/;<%.•'
COMMENTS:
. " D - Not Detected5 - Native TCDO SpikeD - Duplicate (Intralab)
Corrected area 328 [328 - (0.009 x 3 2 2 ) ]
C.ec.ed By: \^
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IS'II ' IEO^HHSIJ 3^'3 (i]nigno]]ii esseag in'
W^ ••] m'W ^ S636'8S3 ^ 3 6t£6'3t3 ••3 SCT3 ^QISOSI'^S M3) S8S3-8^'I^I 88-if-EI f!
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"M 1S-J11-331-M7 PH58S (EMU 321.SWJ [ SEW N' 331,3363 0' 333,3333
i?CL, M 13C-TCDD /
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-/' \ si^-a ^ - J' \---
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91______^ V____•M^S1,I1,01 D ; 133^ T : a ; 4 3
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TCDD ISOMER SPECIFIC
DATA SUMMARY
IT SAMPLE f ^/'u>~•,'/ DATE ANALYZED:
NetWeight/Volume
(-.>/{-
Area
,' ^ ; /^/ -/'
2,3.C
P?/<r"^
•"?.-;7. •^Area
7,8-TCDD^n^.DDbippt--ryi•^ ^
DetectionLiait
ncr Dob oot
Area320
TI
320/322(0.67-0.90}
^7
Area322
^ --^'
ME ANALYZED;
332/334(0.67-0.901
rr>.•^'
Area259
; -- -•
/^ • J;
Surrogat<Measure<
<DOb)
.^.'-/
^
e Surrogati3 Percent
Accurac'.
/•/J>
Area*328
,/-y ^ --
A-^ A '^'7 /••-' ":-''''COMMENTS:
'0 - Not DetectedS - Native TCDD Spike0 - Duplicate (Intralab)
Corrected area 328 [328 - (0.009 x 322 ) ]
Checked By: /^^ -7^^f-
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•\ lO'll 'ISS^NMSIJ 39t'9 IS6933 Tl ;
m'^. m'i.K ••\\ eiwsie ^ OT'ses 'J mm ••]m^ W) Wi 3£'9188-lfir-^I ti
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TCDD I60MER SPECIFIC
DATA SOHMARY
IT SAMPLE «__j^^ DATE ANALYZED ••________-£;
TIKE ANALYZED : / / , < '
Net 2,3,7,8-TCOD Detection Surrogate SurrogatfWeight/ COP•?- Limit 320/322 332/334 Measured PercentVolume Jig ^pb ppt- nq ppb ppt CO.67-0.90) /0.67-0.90) fppb) Accurac-.
rea Area Area Area Area Area*-——'- - 21 320 322 259 328
'//1'/-'' //7'-/:^.- ^->"/ ~?£r.^7 ^7 7 ? - . . - 7 . ^ .
D - Not DetectedS - Native TCOD SpikeD - Duplicate (Intralab)
corrected area 328 [328 - (0.009 x 322) ]
Checked By: ^L^£^_
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TO- ML-8S 17^ ?B-253S (EM S IM• J ^ 246.33?S 8-' 242.3343 C ' ^SSS D' 38E.3E52 E' 393.9'
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m 17-JIH'S 1/^570-E5BS (EM Sus.'M1 ^ 313,3978 L 321.S348 B^ 327,8847 t^ 331.336S 0' 333,3338
;i t™"ETCDD,3?CL,M)13C-T(;;..'.
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TCDD ISOMER SPECIFIC
DATA SUMMARY
IT SAMPLE ( ,/W;: _ DATE ANALYZED:
NetWeight/
/A
Area-212
12J^1
2,3.7,8-TCDD( 9 .
nq/bpb ppt-
.•?75-^,>-<
7 " '
Area-13^1
%-/,5'/
DetectionLimit
na DDb Dot
Area320
//^
320f0.67
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^.sv
TIME
1/322-0.90) »
sy
Area322
ANA
332.).67
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Area
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SurrogatMeasure..-(PPb) .
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Area*328
•'./??-9 Z
COMMENTS:
-0 - Not DetectedS - Native TCDD Spike0 - Duplicate (Intralab)
Corrected area 328 (328 - (0.009 x 3 2 2 ) ]
Checked By: /^/^ -7^ / f-'FS^
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w iMS'e \^ ft ,N3=1 CT3 ^W^^
f:1 v i k' i '.'-K^VW^WS^-^Xt!S!-S^——————JlSiiiiMiiif-fia-tfT. „
\ ,;1 /8 ^H ^ G = I ra ^ig'^iiii'eo
a ; G = l fiS-SSI ^'^fr^^S
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TCDD ISOMER SPECIFIC
DATA SUMMARY
IT SAMPLE « /-,',•-•'.' "•;'< ' ^ DATE ANALYZED ••_______
TIME ANALYZED: . ' ' - ' / . -.
NetWeight/
2,3,7,8-TCDD DetectionCong. Limit
no ^PP^ pp«- nq ppb ppt
Surrogate Surrogat*320/322 332/334 Measured Percent
(0.67-0.901 (0.67-0.90^ (ppb) ACCUC^C\
,' •'. .T'--
. /Z- /ft^
Area332
Area-224.
_ygS , L-
Area320
/(.L/ ?/
Area322
-,'7? ?/
Area259
^y?^'
Area*328
. 3'
COMMENTS:
D - Not DetectedS - Native TCDD Spike0 - Duplicate (Intralab)
corrected area 328 [32S - (0.009 x 3 2 2 ) ]
Checked By: fr^ ^/^
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, ;^r---)--"-•^-
<<? 6 /^ ?-/ ^
£ P-JJL-8819^ 78-2583 (El*)- ' ' ' F' 305,8387 G ' 315,9419 H ' 317,93:
,•.__-''—,—— ..'„_______-___•__."». '"—"t.•-..—,« ———•j
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TCDD ISOMER SPECIFIC
DATA SUMMARY
IT SAMPLE f /•^^'-'•S'^ DATE ANALY2ED:_
TIME ANALYZED:_
7 / / -•'-
/^-•/'-g'
Net 2.3,7,8-TCDD Detection Surrogate Surrogat.Weight/ Conq. Limit 320/322 332/334 Measured Percentvolume ncr PD^ pot nq ppb ppt JO. 6-7-0.90) l0.67-O.SO) fPpb) Accurac1
Area Area Area Area Area Area*332, 334 3,0 322 259 328^320 322 _259
^/- -. ^•/ /'- ^•^ ^ -COMMENTS: A"" '-
SO - Not DetectedS - Native TCOD Spike0 - Duplicate (Intralab)
'Corrected area 328 [328 - (0.009 x 322) ] „
^1^ l^if^Checked By :_<//•" ' -————
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• —.--, r- - .,,. ——,, )..
l a ' I I ' IS 3^041168'HSIJOBITSnfS^K
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^-l-fr/-^ roa/O' ^y , '"., ., ^2< - ^<. "t,.-"
f> s-^ / -<^ — c - '
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^ . . . > ' •N3=1 CTSI ^lE'n'isoto
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H I 18 1 ••-
••, I'-T 'T r .T '•, l / i'^'. bt 'i / i'^
L ^ 3 = l 88'IE ^i^ts^
iffiS'S^O S3£6'1£^H ASS'a^l W^ ••-} W6!£ ^ 1 ^OISOSI^^ M35 WL \ 88-1PKI t£SK
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TCDD rSOMER SPECIFIC
DATA SUMMARY
IT SAMPLE ( /\;-'C'"'''^'^/ DATE ANALYZED: ,7- ^,' .'j.'y-
TIHE ANALYZED: / y / .
Net 2,3,7,8-TCDD DetectionWeight/ Cone. Litnit 320/322 332/334Volume nq pvtv ppf nq Ppb ppt (0.67-0.90) CO.67-0.901
^
Surrogate Surrogat.Measured Percent
fppb) Accurac'
Area332
/ I W.i.: 7
Area..331
^A-/.-^
Area320
s /^. .yy
Area322
^.
Area259
/y7 ^
Area*328
COMMENTS:
-.D - Not DetectedS - Native TCDD SpikeD - Duplicate (Intralab)
Corrected area 328 [328 - (0.009 x 3 2 2 ) ]
Checked By:
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_t- o.-.~? ESS"-•-• .rs.:" -•on CA:.*-':• c-n •3.:'
C2.:« ___ «=0i•:=-• "- i oo
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f-'-f •33 "=x= c-yi "—-
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P-JH 13^131W (EM: 1 1 f.:- 310,8978 L 321.S948 ^ WM ^ S31.336S ^ : :i33,333Ea^ffiTIVE TCDD, 37CL, ffi 13C-TCDD
r.( T < ^.^ ^ ,, SiB C Sl,[l^ Q ; 1^3 T = S^S
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11 ,-/•• 'J^6
£N5 M ^15 ^ ^ S^y
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TCDD ISOMER SPECIFIC
DATA SUMMARY
IT SAMPLE « / , ' y S 5 5 ' DATE ANALYZED:
TIME ANALYZED: /-=?. < '-
Net ^^.P.s-TCDO Detection Surrogate SurrogatiWeight/ 'OS- Linit 320/322 332/334 Measured PercentVolume per/fob ppf- nq ppb ppt f O . 67-0.90) (0.67-0.901 fppb) Accurac'
/ .. ^^7 — . ^6- ^1. >^ /^< y'.'y^
Area332
Area334
Area320
JW.W
Area Area Area*328
COMMENTS:
<D - Not DetectedS - Native TCDD Spikeo - Duplicate (Intralab)
Corrected area 328 [328 - (0.009 X 322)J
Checked By: M^ /^
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TCDD ISOMER SPECIFIC
DATA SUMMARY
IT SAMPLE «__y/ //^DATE ANALYZED: •?- / ~' -•-•--'
TIME ANALYZED: /? . ' / /
Net 2,3.7,8-TCDD DetectionWeight/ Cone. LlSlt
Yolmn.e, M pb ppt ncr ,j-ipS pptSurrogate Surrogati
320/322 332/334 Measured Percent! 0 .67-0.90) ( •0 .67-0 .90) fppb) Accurac'
r'. d' /
Area332 Area
_33^4
A-^i ^^
Area320
Area322
Area259
Area*328
•r-. '^
COHMENTS:
.<o - Not DetectedS - Native TCOD Spike0 - Duplicate (Intralab)
•Corrected area 328 [328 - (0.009 x 3 2 2 ) ]
cnec^ BV: ^
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3(1195 17-JUL-8S 13:117H58S W SUS^ISOSTD? 1 K ' 319,8978 L 321,8948 11^ 327,8347 H ^ 331,3368 0 ^ 333,3333»t^f f iTIVETCDD,37CL, i013C-TCDO , /