Document xzQw3jKox607gJwG7O6Jg72Xg
AR226-2732
The miracles c^f science"
Study Title
MODELING RELEASES OF AMMONIUM PERFLUOROOCTANOATE INTO THE OHIO RIVER
Author William R. Berti Report Completed on
May 22, 2000 Performing Laboratory E. I. du Pont de Nemours and Company Environmental and Microbiological Sciences & Engineering Corporate Center for Engineering Research
Central Research & Development Glasgow, Building 300, P.O. Box 6101
Newark, DE 19714-6101 Report No. EMSE-054-00
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DuPont EMSE Report No. 054-00 GENERAL INFORMATION
Chemical Studied: Ammonium perfluorooctanoate Synonyms/Codes: APFO, C-8, FC-143 DuPont Notebook No.: Not Applicable
Sponsor; Robert Pinchot E. I. du Pont de Nemours and Company
BARLML CRP-711 /2210-B Study Initiated/Completed: September 1999 to May 2000
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DuPont EMSE Report No. 054-00
MODELING RELEASES OF AMMONIUM PERFLUOROOCTANOATE INTO THE OHIO RIVER
SUMMARY
PDM indicated that APFO concentrations of 1.0 |ig APFO/L would be exceeded about 50% of the time during the year. APFO concentrations of in the river would exceed 0.1 [I.B, APFO/L 90% of the time during the year and 10 [is, APFO/L about 2.2% of the time during the
year.
Average annual APFO concentrations in the Ohio River calculated by using a Microsoft Excel spreadsheet was 0.423 pg APFO/L. Modeled APFO concentrations in the river ranged from a low of 0.199 p.g APFO/L in March to a high of 0.965 ^ig APFO/L in September, which correspond to high and low river flows, respectively. Average Ohio River flows and volume data calculated from. the US Geological Survey was collected at the Belleville Dam and used in the spreadsheet model. The Belleville Dam is on the Ohio River 13 miles downstream of the Washington Works Plant. This river flow data is the closest location downstream from the plant where this type of information is available.
Study Conducted and Report Prepared by:
William R. Berti Senior Research Biologist
(date)
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DuPont EMSE Report No. 054-00
INTRODUCTION/PURPOSE
APFO (ammonium perfluoroocatanoate) is a fluorinated surfactant used in the manufacturing of Teflon at Washington Works. A portion the APFO (18,416 kg in 1996) was released to the Ohio River as part of an NPDES permitted release for the facility (WV0001279). The molecular weight of APFO is 431.098 g/mole. Other properties of APFO are listed below.
Made by 3M Company Health rating of 2
Exposure limits 0.01 mg/m3 skin 8 hr LDso acute oral rat = 680 mg/kg BODzo = nil Biodegradation = nil
BCF=1.8
Molecular formula CF3(CF2)6COO'NFL^+ pH ~ 5 (0.5% aqueous)
pKa=2.8(-COOH) Melting point = 56-58C (-COOH)
COD = 700 mg/kg Koc = 25 Water solubility >1000 mgAPFO/L Vapor pressure (at 22C) =7.1*10'05 mm Hg
Our objective was to calculate the concentrations of APFO that could reasonably be expected to occur in the Ohio River downstream of the NPDES permitted outfall at the DuPont Washington Works.
MATERIALS/METHOD
Releases of ammonium perfluorooctanoate (APFO) to the Ohio River from the DuPont Washington Works Plant were modeled using the Probabilistic Dilution Model (PDM Beta Version 4.0 Beta June 11, 1999, US EPA Office of Pollution Prevention and Toxics) and a constructed Microsoft Excel spreadsheet model. APFO release data for 1996 were used in both
modeling exercises.
PDM inputs included the NPDES number of WV0001279. This corresponds to a reach number of 05030202039, a mean streamflow of4.75E+04 million liters per day (MLD), a low streamflow of 9980.47 MLD and an effluent How of 216.75 MLD. We assumed that APFO was
released 335 days/year, the loading was 55.138 kg/day, and the wastewater treatment efficiency was 0%. We then varied the APFO concentration as the Concentration of Concern (COC) from 0.1 to 50 u,g APFO/L to determine the COC percent of year exceedence.
Microsoft Excel spreadsheet used river flow data from the US Geological Survey (USGS: <http://waterdata.usgs.gov/nwis-w/WV/data.components/hist,cgi?statnum=03159530>). This is the mean daily river flow in cubic feet/sec measured at the Belleville Dam from 10/1/1974
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DuPont EMSE Report No. 054-00
to 9/30/1985. The Belleville Dam is on the Ohio River 13 miles downstream of the Washington Works Plant. This river flow data is the closest location downstream from the plant where this type of information is available. This river flow data compares well with Ohio River monthly average flows at Pittsburgh, PA, Huntington, WV, and Cincinnati, OH from the US Amy Corps of Engineers (ftp://www.lrd-wc.usace.army.mil/MonthlyJ.itm/). The average daily river flow for the month was calculated from available data between those two dates. This was then converted to the average measured flow per month. We assumed the APFO was discharged to the river at a constant rate except for the month of October when production at Washington Works is usually suspended for annual maintenance. We assumed that the total discharge of was 18,416 kg APFO (40,600 Ibs APFO) divided by 11 months. Table shows the results of this spreadsheet model.
RESULTS/DISCUSSION PDM indicated that APFO concentrations of 1.0 pg APFO/L would be exceeded about , 50% of the time during the year. APFO concentrations of in the river would exceed 0.1 pg APFO/L 90% of the time during the year and 10 p.g APFO/L about 2.2% of the time during the
year (Table 1). Figure 1 shows model input/output. Average annual APFO concentrations in the Ohio River calculated by constructing and
using a Microsoft Excel spreadsheet mode] was 0.423 ug APFO/L (Table 2). Modeled APFO concentrations in the river ranged from a low of 0.199 pg APFO/L in March to a high of 0.965 u.g APFO/L in September, which correspond to high and low river flows, respectively. Average Ohio River flows and volume data calculated from the US Geological Survey was collected at the Belleville Dam and used in the spreadsheet model. The Belleville Dam on the Ohio River 13 miles downstream of the Washington Works Plant. This river flow data is the closest location downstream from the plant where this type of information is available.
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DuPont EMSE Report No. 054-00
Probabilistic Dilution Model (PDM) results ot'APFO concentrations and percent of year that the concentration ofAPFO will be exceeded in the Ohio River.
Concentration
ofAPFO
Percent of year
concentration exceeded
ug/L
0.1 0.5
1 3 6 10 25 50
%
90.9 71.6 51.0 17.8 6.1 2.2 0.2 0.0
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DuPont EMSE Report No. 054-00
Table 2. Month
Microsoft Excel spreadsheet calculations of modeled APFO concentrations in the
Ohio River.
Measured flow Measured flow
APFO discharge to Ohio River in 1996
Estimated APFO concentration in Ohio
River
January February
March April May
June July August September
October November December
Average Total
ff/sec
64,001 88,909 111,236 94,017 67,107 47,379 30,989 30,502 25,339 33,030 42,330 78,986
713,824
L/mo
4.69E+12 6.74E+12 8.43E+12 6.90E+12 5.09E+12 3.48E+12 2.35E+12 . 2.31E+12 1.73E+12 2.50E+12 3.11E+12 5.99E+12
4.44E+12 5.33E+13
kg
1,674 1,674 1,674 1,674 1,674 1,674 1,674 1,674 1,674
0
1,674 1,674
18,416
f^g/L
0.357 0.248 0.199 0.243 0.329 0.482 0.713 0.724 0.965 0.000 0.539 0.280
0.423 0.345
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DuPont EMSE
FIGURE 1:
ADSORPTION-DESORPTION STUDIES OF AMMONIUM PERFLUOROOCTANOAT
Probabilistic Dilution Mode] (RDM) Beta Version 4.0 input and output screen,
Chemical ID: Scenario @:
Reach. nu'm'heg
Gag-incf st-ation Period ojE record 8 of obsei.-vacions
Mean sI^reajnfio'KT Low st-reaMflot.T
K t S 1-uen-c. flow
Release days
C-S
1
QS030202Q39
Facility name E.I.DU POKT DE HEHOURS & CO.
,,Paca.-.i.a-ty
,
loca't.xori
PARKERSBURG,
TiJV
6102
^ 1 Receiving ST^reaia- name OHIO R
1996
HA
4.7e+04 [.[LD 998 0.47 HLD 21 6.75 HLD
INPUT DATA
335 days/year
H-P&ES ITujfl^er WVL1001279
P' Facility on r e sell?
D iscliarge v.\fpe P Diract.
1Indirect
Dat a source Faa.cSrch - Direct.
(L isc)
Ixiivo1001279
R elease a
r HFG r PRO r II.ID
^J r" coini
r C01.IS
Loading C one ent. r at-i on of Concern <COC)
Wast; ei.rac.er treacinent efficiency
P,esult.s HisteoEy
COC
(ug/L)
t YEAR COC EXCEED El;
.(DAYS COC EXCEEDED
E6.138
1 0 0
kg/sice/d ay Results {,(C. OC
-i-ig/L
Percent. Q f ye ar
%
Days per ye ar
Exceedence) 2. 24 S. 1'^
.
days/ye ar
RELEASE
LOADIHG.
DAYS (teg/sit a/day)
WASTB OTATER -i. TREATMENT
0. 1
90- 9
33.L- 6
0. S
7.1- 6
261- 5
1.
S1.
186.
S.
8-4
30-6
10.
2.2
8.2
33S. 33S-
33S-
335. 335-
SS. 1 SS. 1 S- 1 55- 1
55.1
0.
0- ----
0.
0. 0.
^J
Sllbntit
Done j Save j Pcinc
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