Document byg6rbj8JwVoQ8ModX89YzeQy
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DIETARY ACUTE NORTHERN BOBWHITE STUDY REVISED Tissue analysis is now included.
TEST SUBSTANCE_____________________________
Identity: Perfluorooctanesulfonate; may also be referred to as PFOS or FC-95. (1-Octanesulfonic acid, 1,1,2,2,3,3,4,4,5,5,6,6,7,7,8,8,8heptadecafluoro-, potassium salt, CAS # 2795-39-3)
Remarks field: The test substance is a white powder. Sample was taken from 3M lot number 217. Sample was stored under ambient conditions prior to testing. Purity determined to be 90.49% by LC/MS, 1HHMR, 19F-NMR and elemental analyses techniques.
METHOD
Method: OPPTS 850.2200, OECD 205, and FIFRA Subdivision E. Section 71-2 Type: Dietary acute GLP: Yes Year completed: 1999 (Test), 2000 (Report) Species: Colinus virginianus Supplier: Wildlife International Ltd. Production Flock, Easton, Maryland Analytical monitoring: Test substance concentration in standards and samples were determined by reversed-phase HPLC and mass spectroscopy. PFOS measured on Day 0 for homogeneity in feed and verification, and Day 5 for stability. Test phases: Acclimation - 10 days
Exposure - 5 days Post-exposure observation - 3 or 17 days
Statistical methods: Lc50values calculated by probit
analysis using the computer software of C.E. Stephan. Body weight data were compared by Dunnett's test using TOXSTAT software. No statistical analyses were applied to feed consumption data. Test bird age: 10 days Pretreatment: None
Test conditions: Housing and environmental conditions: Indoors in batteries of thermostatically controlled brooding pens. Each pen's floor space measured approximately 72 X 90 cm. Ceiling height was approximately 23 cm. External walls, ceilings and floors were constructed of galvanized steel wire and sheeting. Identification: Each group of birds identified by pen number and test concentration. Individuals identified by leg bands.
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Number of replicates : Six for controls, two for each treatment group Number of bobwhite per replicate : five Number of concentrations: seven plus a negative control Feed and water: Game bird ration formulated as below, water from the town of Easton public water supply. Both provided ad libitum during acclimation and testing.
Game Bird Ration
Ingredients
Percent
Fine Corn Meal
44.83
Soy Bean Meal, 48% Protein
30.65
Wheat Midds
6.50
Protein Base
6.00
Agway Special, 60% Protein
4.00
Alfalfa Meal, 20% Protein
3.00
Dried Whey
2.50
Ground Limestone
0.90
Eastman CalPhos
0.60
Methionine Premix + Liquid
0.35
Vitamin and Mineral Prem ix (see below)
0.32
GL Ferm (Fermatco) 1
0.25
Salt Iodized
0.10
'Fermentation by-products (source of unidentified growth factors)
Vitamin and Mineral Premix
Vitamin or mineral Vitamin D 3 Vitamin A Riboflavin Niacin Pantothenic Acid Vitamin B12 Folic Acid Biotin Pyridoxine Thiamine Vitamin E Vitamin K (Menadione dimethylpyrimidinol bisulfite) Manganese Zinc Copper Iodine Iron Selenium
Amount Per Ton 2,000,000 I.C.U.
7,000,000 I.U. 6 grams 40 grams 10 grams 8 mgs 600 mgs 64 mgs 1.2 grams 1.2 grams
20,000 I.U. 5.8 grams 102 grams 47 grams 6.8 grams 1.5 grams 51 grams 182 grams
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Prophylaxis : None Brooding compartment mean temperature: 38 + 2oC Ambient room mean temperature: 27.3 + 1.2oC Average relative humidity: 31 + 14% Photoperiod: Sixteen hours light per day Lighting: fluorescent lights which closely approximate noon-day sunlight; average of approximately 139 lux of illumination
Test diet preparation: Test substance mixed directly into the ration by means of a Hobart mixer. No carrier was used.
Diet sampling: Homogeneity of the test substance in the diet evaluated by collecting six samples from the 18.3 ppm concentration and six from the 1171 ppm concentration. Samples collected from the top, middle, and bottom of the left and right sections of the mixing vessel. These samples also served as the verification samples for these concentrations. Verification samples of the other treatment groups (two samples from each) and the control (one sample) were collected at preparation on Day 0. Stability samples were collected at the end of the exposure period (Day 5) from the control (one sample) and each treatment group (two samples each).
RESULTS___________________________________________________
Nominal concentrations: Bk control, 18.3, 36.6, 73.2, 146, 293, 586, and 1171 ppm Measured concentrations: <LOQ, 19.5, 40.2, 74.5, 174, 291,537, and 1196 ppm Element value: Dietary LC50 = 220 (164 - 289) ppm
No mortality concentration = 73.2 ppm NOEC (body weight gain) = 73.2 ppm All element values based on nominal concentrations
Analytical Methodology: Diet samples were extracted with methanol. Analyses of test solutions were performed at Wildlife International Ltd. using high performance liquid chromatography with mass spectrometric detection (HPLC/MS). When determining the concentration of the test substance in the test solutions, the same and most prominent peak response for perfluorooctanesulfonate was used. No attempt was made to quantify on the basis of individual isomeric components. The LOQ (limit of quantitation) was 1.15 ppm in this study. The mean percent recovery of matrix fortifications analyzed concurrently during sample analysis was 94.7. Samples collected for determination of homogeneity in diet ranged from 102-107% of nominal. Samples collected for verification in diet had measured values from 92 to 119% of nominal. Measured values for
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ambient stability samples taken at Day 5 ranged from 101-122% of nominal.
Summary of analytical chemistry data:
Homogeneity in Avian Diet
Nominal Test Concentration,
ppm
Measured Values at Day 0, ppm
18.3 1171
18.5, 23.4, 18.3, 17.3, 19.4, 19.9, 1239, 1221, 1118, 1301, 1163, 1133
Mean Measured Concentration
, ppm 19.5
Percent of Nominal
107
1196
102
Verification in Avian Diet
Nominal Test Concentration,
ppm
Negative Control
Measured Duplicate Concentrations at Day 0, ppm
< LOQ
Mean Measured Concentration
, ppm -
Percent of Nominal
-
36.6
45.7, 34.6
40.2
110
73.2
77.8, 71.2
74.5 102
146
176, 172
174 119
293
274, 307
291 99
586
550,523
537 92
Ambient Stability in Avian Diet
Day 0 Mean Measured
Concentration,
ppm Negative Control
Measured Duplicate Concentrations at Day 5, ppm
< LOQ
Mean Measured Concentration
, ppm -
Mean Percent of
Day 0
-
19.5
19.2, 19.9
19.6 101
40.2
44.4, 53.8
49.1 122
74.5
76.4, 77.9
77.2 104
174
177, 174
176 101
291 537 1196
318, 315 560, 665 1260, 1187
317 613 1224
109 114 102
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Biological observations Mortalities and clinical observations: One incidental mortality occurred in the control group as a result of a broken leg on the morning of Day 5. It was subsequently euthanized on Day 6. Two other birds in the control group were intermittently noted with foot lesions associated with cage mate aggression. Otherwise, all control birds were observed to be normal in appearance and behavior throughout the test.
The first treatment-related mortalities occurred on Day 3 in the 586 and 1171 ppm treatment groups. Mortality occurred through Day 8 in all dose groups > 146 ppm with some of the deaths being during the post-exposure period. There were no treatment-related mortalities or overt signs of toxicity at concentrations < 73.2 ppm.
There was 11% mortality in the 146 ppm treatment group, and two additional birds displayed clinical signs of toxicity (wing droop). All other birds in this test group displayed normal appearance and behavior for the duration of the test. Recovery with normal appearance and behavior occurred on Day 9 to test termination.
There was 80% mortality (occurring on Days 5,6, and 7) for birds in the 293 ppm treatment group. Signs of toxicity observed prior to death included a ruffled appearance, reduced reaction to stimuli (sound and motion), lethargy, wing droop, loss of coordination, lower limb weakness and convulsions. Recovery with normal appearance and behavior occurred on Day 9 to test termination.
There was 100% mortality (occurring from Day 3 through Day 7) for birds in the 586 ppm treatment group. Signs of toxicity observed prior to death included a ruffled appearance, reduced reaction to stimuli (sound and motion), lethargy, depression, wing droop, loss of coordination, lower limb weakness, lower limb rigidity, prostrate posture, and convulsions.
There was 100% mortality (occurring from Day 2 (noted on Day 3 for Day 2 afternoon) through Day 4) for birds in the 1171 ppm treatment group. Signs of toxicity observed prior to death included a ruffled appearance, reduced reaction to stimuli (sound and motion), lethargy, depression, wing droop, loss of coordination, lower limb weakness, and lower limb rigidity.
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Body weight gain: When compared to the control group, there
were no apparent treatment related effects on body weight among the birds in concentrations < 73.2 ppm. During Days 0-5, statistically significant reductions in body weight gain or body weight loss occurred in the 146, 293, and 586 ppm treatment groups. Body weight effects could not be determined for test organisms in the 1171 ppm group due to total mortality.
Feed Consumption: No apparent treatment related effects were noted for feed consumption for birds in concentrations <146 ppm. Reduced feed consumption was noted for birds in treatment groups > 293 ppm from Days 0-5. No treatment-related effects on feed consumption in any of the surviving treatment groups during the Day 6-8 post-exposure period were observed.
Gross Necropsy: All birds that died during the study, half of those
surviving at Day 8 and the rest at test termination were subjected to a gross necropsy. Necropsy results for birds found dead were similar, including thin condition, loss of muscle mass, altered spleen color, autolysis of tissues and pale organs. These necropsy findings were considered to be treatment related. The single bird euthanized from the 293 ppm treatment was found to have treatment related necropsy findings. Necropsy results for all other birds euthanized on Day 8 and Day 22 were unremarkable.
% Cumulative Mortality
Nominal Concentration
, ppm
Day 1
Day 2
Day 3
Day 4
Day 5
Negative
0
0
0
0
0
Control
18.3 0 0 0 0 0
36.6 0 0 0 0 0
73.2 0 0 0 0 0
146 0 0 10** 0 0
293 0 0 0 0 20
586 0 0 10 20 50
1171
0
0 30 100 100
*No mortalities occurred in any of the treatment levels from Day 8 to Day 22 ** Bird euthanized on day 3 after sustaining a broken leg.
Day 6
0
0 0 0 0 40 80 100
Day 7
Day 8*
00
00 00 00 10 10 80 80 100 100 100 100
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Summary of Analytical Results for Liver Tissue1(ug/g wet) during Day 1 through Day 7 Test Period2 - Individual Values Reported
N om inal
Day 3 Liver Day 4 Liver
Day 5 Liver
Day 6 Liver
Day 7 Liver
Conc., ppm
Conc.
Conc.
Conc.
Conc.
Conc.
146 111
293 249 202 153, 124
586 NE NE 126 235 111
1171
134 132,123,124
1Concentrations were not corrected for purity of PFOS standard used (lot 171). No attempt was
made to correct for moisture content.
2Reported results are only for concentrations where mortality occurred. During this time period,
the negative control and concentrations <293 ppm exhibited no mortality. (One bird euthanized
after sustaining a broken leg.) There was also no mortality in concentrations > 293 ppm during
days 1 and 2.
NE = Not Extracted
Summary of Analytical Results for Liver Tissue (ug/g wet) and Serum
(ug/mL) at Day 8 and Day 221 - Average Value Reported
Nom inal Conc., Day 8 Liver
Day 8 Serum
Day 22 Liver
Day 22 Serum
ppm
Conc.
Conc.
Conc.
Conc.
Negative Control <LOQ (~0.070)
<LOQ (0.010)
0.215
0.115
18.3 18.5 <LOQ 3.25 5.89
36.6
25.8
3.04
2.92 7.27
73.2
44.0
41.2
10.0 26.2
146 70.3 41.6 25.8 40.5
293
NE
Not applicable
Not applicable
Not applicable
586
NS
NS
Not applicable
Not applicable
1171
NS
NS
Not applicable
Not applicable
"'Concentrations were not corrected for purity of PFOS standard used (lot 171). No attempt was
made to correct for moisture content in relevant tissue, liver.
NS = No Sample analyzed.
NE = Not Extracted
Body Weight (grams)
Exposure Period
Recovery Period
Nominal Concentration
(ppm)
Mean Body
Weight, Day 0
Mean Body Mean Body Mean Body Mean Body
Weight
Weight
Weight
Weight
Change Change Change Change
Day 0-5 Day 5-8 Day 8-15 Day 15-22
Mean Total Mean Body Body Weight Weight, Change, Day Day 22
8-22
Negative Control
18.3
20 21
+10 +8 +23 +22 +11 +9 +24 +23
45 47
82 87
36.6
20 +11 +8 +26 +24 50
89
73.2
20 +9 +7 +24 +20 44
79
146 20 +7* +6** +24 +21 45 79
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293
20
2** 1** +14 +20
34
55
586
20
_4**
~
-- --
--
--
1171
20
~
~
--
--
--
-
Note: Numbers may not add manually due to rounding. Values for 293 ppm treatment group are impacted
by the fact that only one bird remained in that treatment group after Day 8.
` Statistically different from the control group at p<0.05 (Dunnett's t-test).
" Statistically different from the control group at p=<0.01 (Dunnett's t-test (--) = No data available due to mortality.
Mean Average Feed Consumption
Nominal Concentration,
ppm
Grams
Grams
Grams
Grams
Feed/Bird/Day Feed/Bird/Day Feed/Bird/Day Feed/Bird/Day
Days 0-5
Days 6-8
Days 8-15 Days 15-22 '
Negative Control
9
10
9
13
18.3
9 11 10 12
36.6
8 12 14 15
73.2 10 13 13 15
146 9 10 11 14
293 5 9 8 9
586 6 19 _ _
1171 4 -- -- -(--) = No data available due to mortality.
Gross Pathological Observations from Birds that Died in Study
Finding
Abdominal cavity, some autolysis Abdominal cavity, autolysis throughout Crop, empty Emaciated Fractured leg G.I. Tract empty Gizzard contents bile stained Heart, anterior portion mottled white color Heart, pale Intestinal contents tar-like Keel, prominent Kidneys, pale Liver, pale and mottled Loss of muscle mass Muscular-skeletal, pale Small in stature Spleen, black Spleen, dark
Male, Female, and Undetermined
___________ (ppm)____________ Control 146 293 586 1171
N = 1 N = 2 N = 8 N = 10 N = 1(
0
022
4
0
001
1
0
025
2
0
025
8
1 100 0
0 011 0
0 025 1
0
0 10
0
0 002 1
0
002
0
0 0 1 3 10
0
002
0
0
100
0
0
047
9
0
100
0
0
030
0
0 001 0
0
000
2
Spleen, grey Spleen, grey-brown Spleen, pale Spleen, small Spleen, small and pale Thin Not remarkable
0
001
0
0 000 1
0 0 10 1
0 000 1
0 003 0
0 004 2
0
0 10
0
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CONCLUSIONS____________________________________________ The dietary LC50 value for Northern Bobwhite exposed to perfluorooctanesulfonate was determined to be 220 ppm with a 95% confidence interval of 164 to 289 ppm. The slope of the concentrationresponse curve was 7.005 and the chi-square value was 0.023. The no mortality concentration was 73.2 ppm. Based upon treatment related mortality, signs of toxicity and effects upon body weight gain at the 146 ppm test concentration, the no observed effect concentration was 73.2 ppm.
Author and/or submitter: 3M Corporation, Environmental Laboratory, P.O. Box 33331, St. Paul, Minnesota, 55133
DATA QUALITY____________________________________________
Reliability: Klimisch ranking = 1.
REFERENCES
This study was conducted at Wildlife International Ltd., Easton, MD at the request of the 3M Company. The tissue analysis was conducted by 3M Environmental Laboratory, St. Paul, MN.
OTHER____________________________________________________
Last changed: 5/3/00, 6/28/01