
|
Table 9.02: Chronic toxicity of selenium to freshwater fish |
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|
Species |
Life Stage |
Data type |
Chemical |
Hardness (mg/L as CaCO3) |
Other Measured Parameters |
Conc. in water (mg/L) |
Conc. in diet (µg/g) dry wt |
Effect |
Reference |
|
Brachydanio rerio |
- |
- |
selenite |
- |
- |
3.000 |
- |
7-d, mortality |
Niimi and LaHam, 1975 |
|
(zebrafish) |
- |
- |
selenite |
- |
- |
1.000 |
- |
10-d, mortality |
|
|
- |
- |
selenite |
- |
- |
10.000 |
- |
10-d, change in % hatch or time to hatch |
||
|
Carassius auratus |
- |
- |
selenite |
- |
- |
32.700 |
- |
5-d LC50, mortality |
Cardwell et al., 1976a |
|
(goldfish) |
- |
- |
selenite |
- |
- |
22.300 |
- |
6-d LC50, mortality |
|
|
- |
- |
selenite |
- |
- |
17.200 |
- |
7-d LC50, mortality |
||
|
- |
- |
selenite |
- |
- |
13.000 |
- |
9-d LC50, mortality |
||
|
- |
- |
selenite |
- |
- |
11.500 |
- |
11-d LC50, mortality |
||
|
- |
- |
selenite |
- |
- |
8.800 |
- |
14-d LC50, mortality |
||
|
- |
- |
selenite |
- |
- |
12.000 |
- |
7 and 9-d LC50, mortality |
Weir and Hine, 1970 |
|
|
- |
- |
selenite |
157.0 |
- |
6.300 |
- |
14-d LC50, mortality |
Cardwell et al., 1976a,b |
|
|
- |
- |
selenite |
- |
- |
5.000 |
- |
10-d, mortality |
Ellis, 1937; Ellis et al., 1937 |
|
|
- |
- |
selenite |
- |
- |
2.000 |
- |
46-d, gradual anorexia and mortality |
Ellis et al., 1937 |
|
|
- |
- |
selenate |
175.0 |
- |
8.780 |
- |
7-d EC50, death and deformity |
Birge, 1978 |
|
|
Ctenopharyngodon idella (grass carp) |
adult |
F,M,1 |
selenate / selenite (60:40 ratio) |
- |
pH = 7.5-11.0 |
0.025 |
- |
~ 500-d study, mortality: none recorded alive (1 found dead and 3 unaccounted for, out of 4) |
Crane et al., 1992 |
|
Dorosoma petenense (threadfin shad) |
all life stages |
F,M,1 |
- |
- |
Temp. = 20.0-38.0 °C |
0.010 |
and 15.000-70.000 in diet |
2 yr study, mortality and deformity of fry, juveniles and adults; significant decrease in standing crop |
Cumbie and Van Horn, 1978 |
|
Gambusia affinis (western mosquitofish) |
- |
F,M,1 |
- |
- |
- |
.340-.390 |
- |
long term study (1984), (compared to control) mean survival of fry was 70%; shorter length and earlier stage of development in stillborn fry than in live fry |
Saiki and Ogle, 1995; BOR, 1987 |
|
- |
F,M,1 |
- |
- |
- |
.340-.350 |
- |
long term study (1985), (compared to control) mean survival of fry was 77%; shorter length and earlier stage of development in stillborn fry than in live fry; whole body conc. of in dry wt of fish is 100 ug/g |
||
|
Ictalurus platycephalus (flat bullhead) |
all life stages |
F,M,1 |
- |
- |
Temp. = 20.0-38.0 °C |
0.010 |
and 15.000-70.000 in diet |
2 yr study, mortality and deformity of fry, juveniles and adults; significant decrease in standing crop |
Cumbie and Van Horn, 1978 |
|
Lepomis cyanellus (green sunfish) |
all life stages |
F,M,1 |
- |
- |
Temp. = 20.0-38.0 °C |
0.010 |
and 15.000-70.000 in diet |
2 yr study, mortality and deformity of fry, juveniles and adults; significant decrease in standing crop; complete reproduction failure |
Cumbie and Van Horn, 1978 |
|
Lepomis macrochirus (bluegills) |
adult fish, eggs, and 30 day old fry |
F, M, 1 |
Na2Se04/ Na2Se03 (6:1 ratio) + diet (seleno-L-methionine) |
- |
- |
0.010 |
and in diet 4.600- 33.300 |
11 wk study, during spawning, monitoring fry for 30 days after hatch, revealed that fry were significantly affected, especially of those whose parents had a combination with high diet Se (33.3 ug Se/g) |
Coyle et al., 1993 |
|
adult |
F, M,1 |
selenite |
179.0 |
pH = 8.0; D.O. = 3.6-9.5 mg/L; Temp. = 4.6-26.4°C; Alkalinity = 160.0 mg/L |
0.010 |
- |
356-d chronic study, effect on reproduction and progeny showed that reduction in survival was seen in the last 98 days; adult growth was reduced during intermediate stage. |
Hermanutz et al., 1992 |
|
|
adult |
F, M,1 |
selenite |
179.0 |
pH = 8.0; D.O. = 3.6-9.5 mg/L; Temp. = 4.6-26.4°C; Alkalinity = 160.0 mg/L |
0.300 |
- |
356-d chronic study, and effect on reproduction and progeny showed that complete mortalityresulted from this conc.; adult growth was reduced during intermediate stage. |
||
|
adult |
F, M,1 |
selenite |
179.0 |
pH = 8.0; D.O. = 3.6-9.5 mg/L; Temp. = 4.6-26.4°C; Alkalinity = 160.0 mg/L |
0.010 |
- |
40 wks, exposure before spawning, resulted in reduced embryo and larval survival and produced larvae with a high incidence of edema, lordosis, and internal hemorhaging |
||
|
adult |
F, M,1 |
selenite |
179.0 |
pH = 8.0; D.O. = 3.6-9.5 mg/L; Temp. = 4.6-26.4°C; Alkalinity = 160.0 mg/L |
0.300 |
- |
40 wks, exposure before spawning, resulted in reduced embryo and larval survival and produced larvae with a high incidence of edema, lordosis, and internal hemorhaging |
||
|
- |
- |
selenite |
- |
- |
30.700 |
- |
7-d LC50, mortality |
Cardwell et al., 1976a |
|
|
- |
- |
selenite |
- |
- |
27.700 |
- |
8-d LC50, mortality |
||
|
- |
- |
selenite |
- |
- |
23.600 |
- |
10-d LC50, mortality |
||
|
- |
- |
selenite |
- |
- |
20.500 |
- |
12-d LC50, mortality |
||
|
- |
- |
selenite |
157.0 |
- |
12.500 |
- |
14-d LC50, mortality |
||
|
- |
- |
- |
- |
- |
17.600 |
- |
14-d LC50, mortality |
||
|
Lepomis macrochirus (bluegills) (cont.) |
adults exposed in the field and spawned in the laboratory |
F,M,1 |
- |
- |
Alkalinity = 20.0 mg/L |
0.009-0.012 |
- |
2-yr study, mortality and deformity of larvae; total reproductive failure; in larvae 28.20 ug Se/g dry wt; carcass (minus gonad) = 5.9-7.8 ug Se/g wet wt; ovary = 6.9 wet wt (38.8-54.2 dry wt); testis = 4.37 wet wt |
Gillespie and Baumann, 1986 |
|
juveniles |
F,M,1 |
- |
- |
Temp. = 21.0 °C |
- |
in diet 54.000 (satiation feeding-diet of mayfly nymph) |
44-d, fish showed gross pathological and behavioral signs of selenosis; food avoidance was also seen; 75% mortality; skeletal muscle = 5.0-7.0 ug Se/g wet wt; liver = 8.0-86.0 wet wt |
Finley, 1985; Adams, 1976 |
|
|
juveniles |
F,M,1 |
- |
18.0 |
Temp. = 25.0 °C |
- |
in diet 45.000 (satiation feeding) |
7-d, 100% mortality; whole body = 21-32 ug Se/g dry wt |
Carolina Power and Light Company, 1985 |
|
|
juveniles |
F,M,1 |
- |
19.0 |
Temp. = 25.0 °C |
- |
in diet 25.000-70.000 (satiation feeding) |
61-d, 100% mortality; whole body conc. = 44.0-53.0 ug Se/g dry wt |
||
|
juveniles |
F,M,1 |
- |
Temp. = 26.0 °C; Alkalinity = 26.0 mg/L |
0.009-0.012 |
in diet 21.000-73.000 (satiation feeding) |
14-d, 100 % mortality; muscle = 13.1-17.5 ug Se/g dry wt; viscera = 27.5-37.5 dry wt |
Duke Power Company, 1980 |
||
|
larvae |
F,M,1 |
selenite |
318.0-330.0 |
- |
0.400-2.000 |
- |
48-d, LC50 |
Adams, 1976 |
|
|
juvenile |
F.M,1 |
selenite and selenate in water and seleno-L-methionine in diet |
20.0-25.0 |
pH = 6.1-6.6; D.O. = 8.1-8.6 mg/L; Temp. = 20.0°C |
0.005 |
in diet 5.100 as seleno-L-methionine |
180-d study, hematological changes and gill damage that reduced respiratory capacity while increasing respiratory demand and oxygen consumption |
Lemly, 1993 |
|
|
juvenile |
F.M,1 |
selenite and selenate in water and seleno-L-methionine in diet |
20.0-25.0 |
pH = 6.1-6.6; D.O. = 8.1-8.6 mg/L; Temp. = 4.0°C |
0.005 |
in diet 5.100 as seleno-L-methionine |
180-d study, high Se in combination with low water temp. caused reduced activity and feeding, depletion of 50-80% of body lipid and significant mortality within 60 days. |
||
|
Lepomis macrochirus (bluegills) (cont.) |
juvenile |
F,M,1 |
selenite and selenate (6:1 ratio) |
134.0 |
pH = 8.1; Temp. = 17.0°C; Alkalinity = 60.0-65.0 mg/L |
0.640 |
- |
60-d LOAEC, increased mortality |
Cleveland et al., 1993 |
|
- |
- |
selenite and selenate (6:1 ratio) |
- |
- |
0.160-2.800 |
- |
60-d, change in behaviour |
||
|
- |
- |
selenite and selenate (6:1 ratio) |
- |
- |
0.160-2.800 |
- |
18-d LOC |
||
|
juvenile |
F,M,1 |
selenite and selenate (6:1 ratio) |
134.0 |
pH = 8.1; Temp. = 17.0°C; Alkalinity = 60.0-65.0 mg/L |
2.800 |
- |
30-d, measurable changes in length and or weight of test organism; significant reduction in condition factor (K) |
||
|
juvenile |
F,M,1 |
seleno-L-methionine |
134.0 |
pH = 8.1; Temp. = 17.0°C; Alkalinity = 60.0-65.0 mg/L |
- |
in diet 25.000 ug Se/g wet wt as seleno-L-methionine |
30-d, significant reductions in condition factor (K) |
||
|
juvenile |
F,M,1 |
seleno-L-methionine |
134.0 |
pH = 8.1; Temp. = 17.0°C; Alkalinity = 60.0-65.0 mg/L |
- |
in diet 13.000 ug Se/g wet wt as seleno-L-methionine |
90-d, significant reductions in condition factor (K) |
||
|
all life stages |
F,M,1 |
- |
- |
Temp. = 20.0-38.0 °C |
0.010 |
and 15.000-70.000 in diet |
2 yr study, mortality and deformity of fry, juveniles and adults; significant decrease in standing crop; complete reproduction failure |
Cumbie and Van Horn, 1978 |
|
|
Lepomis microlophus (redear sunfish) |
- |
- |
- |
- |
- |
0.005 |
- |
contaminated lake resulted in substantial alterations in the liver including necrosis, cytoplasmic vacuolation, Kupffer cell proliferation and many abnormalities in ovaries; mean hepatic conc. of fish is 7.63 ug Se/g and 4.33 in ovaries |
Sorensen, 1988 |
|
Micropterus salmoides (largemouth bass) |
all life stages |
F,M,1 |
- |
- |
Temp. = 20.0-38.0 °C |
0.010 |
and 15.000-70.000 in diet |
2 yr study, mortality and deformity of fry, juveniles and adults; significant decrease in standing crop; complete reproduction failure |
Cumbie and Van Horn, 1978 |
|
Oncorhynchus kisutch (coho salmon) |
larvae, fry |
F,M,1 |
selenite |
325.0-330.0 |
- |
0.160 |
- |
43-48-d LC50 |
Adams, 1976 |
|
Oncorhynchus mykiss (rainbow trout) |
- |
- |
- |
- |
- |
- |
in diet 10.000-13.000 |
results indicate reduced growth rates in rainbow trout |
Hilton et al., 1980; Hilton and Hodson, 1983; and Hicks et al., 1984 |
|
- |
- |
selenate |
45.0 |
- |
2.891 |
- |
chronic effect, early life stage |
Spehar, 1986 |
|
|
egg |
F,M,1 |
- |
28.0 |
- |
0.030-0.170 |
- |
60-d, significant number of mortalities |
Goettl and Davies, 1976a |
|
|
egg |
F,M,1 |
- |
28.0 |
- |
0.030-0.170 |
- |
12-mos, significant mortality |
||
|
- |
- |
selenite |
135.0 |
- |
0.047 |
- |
41-d (early life stage), reduced hatch of eyed embryos |
Hodson et al., 1980 |
|
|
eyed eggs |
F,M,1 |
- |
135.0 |
Temp. = 0°C |
0.028 |
- |
post fertilization through hatching, significantly reduced hatching |
||
|
- |
- |
selenite |
135.0 |
- |
0.053 |
- |
50-wk, decreased iron in blood |
||
|
- |
- |
- |
- |
- |
- |
in diet 5.410-6.920 |
9-d LC50 |
||
|
- |
- |
selenite |
330.0 |
- |
2.700-2.750 |
- |
5-d LC50 |
Adams, 1976 |
|
|
- |
- |
selenite |
334.0 |
- |
0.250 |
- |
21-d study, results showed reduced growth in trout fry |
||
|
- |
- |
selenite |
334.0 |
- |
0.460 |
- |
21-d LC50 |
||
|
- |
- |
- |
0.290 |
- |
96-d LC50 |
||||
|
- |
- |
selenite |
325.0 |
- |
0.280 |
- |
96-d LC50 |
||
|
larvae |
F,M,1 |
selenite |
325.0-330.0 |
- |
0.500 |
- |
48-d LC50, mortality |
||
|
- |
- |
- |
- |
- |
0.060-0.130 |
- |
life cycle LC50 |
USEPA, 1980 |
|
|
embryos |
- |
- |
- |
- |
0.080 |
- |
1 yr study, fish developed external deformities |
Goettl and Davis, 1976a |
|
|
sac fry (21.7 mm, 0.075 g) |
F, M, 1 |
selenite |
272.0 |
pH = 7.4; Temp. = 12.0°C; Alkalinity = 237.0 mg/L |
0.047 |
- |
90-d, significant mortality; whole body=1.07 ug Se/g wet wt in survivors; length was reduced at 30 and 60 days |
Hunn et al., 1987 |
|
|
sac fry (21.7 mm, 0.075 g) |
F, M, 1 |
selenite |
272.0 |
pH = 7.4; Alkalinity = 237.0 mg/L |
0.100 |
- |
90-d study, showed survival significantly reduced; whole body=2.65 ug Se/g wet wt in survivors; length and wt. were significantly reduced after 90 days |
||
|
sac fry (21.7 mm, 0.075 g) |
F, M, 1 |
selenite |
272.0 |
pH = 7.4; Alkalinity = 237.0 mg/L |
0.012 |
- |
30, 60 and 90-d studies, results of study indicate safe level of 0.010 mg/L for inorganic Se would not sig. affect growth but conc. near this level (0.012) reduce levels of calcium in backbone |
||
|
- |
- |
selenite |
272.0 |
- |
0.055 |
- |
90-d LC50 |
||
|
Oncorhynchus mykiss (rainbow trout) (cont.) |
juveniles |
F,M,1 |
selenite |
28.0 |
Temp. = 11.0°C |
- |
in diet 8.900 |
42-wk, significant mortality |
Goettl and Davies, 1977b |
|
- |
- |
selenate |
104.0 |
- |
5.000 |
- |
28-d EC50, death and deformity |
Birge, 1978; Birge and Black, 1977; Birge et al., 1980 |
|
|
- |
- |
selenite |
- |
- |
0.044 |
- |
increased mortality |
Davis et al., 1988 |
|
|
Onchorhynchus tshawytscha (chinook salmon) |
egg to 90 day |
F, M, 1 |
selenate : selenite (6: 1 ratio) |
612.0 |
pH = 7.8; Temp. = 12.0°C; Alkalinity = 215.0 mg/L |
0.035 |
- |
well-water (30, 60 and 90-d) (0.250, 0.5, 1, 2 and 4 ratio,1= 1.4 B, 0.049 Mo, and 0.035 Se) conc. of Se in salmon were correlated with reduced survival and growth of fish in well water |
Hamilton and Wiedmeyer, 1990 |
|
0.3 g |
F, M, 1 |
Se as (6: 1 of Na2Se04/ Na2Se03) |
371.0 |
pH = 7.8; Temp. = 12.0°C; Alkalinity = 215.0 mg/L |
0.035 |
- |
freshwater (30, 60 and 90-d) (0.250, 0.5, 1, 2 and 4 ratio,1= 1.4 B, 0.049 Mo, and 0.035 Se) whole-body conc. of Se increased with increasing exposure conc.; reduced survival in a 15-d seawater challenge test |
||
|
- |
- |
- |
- |
- |
3.200-5.300 |
- |
30-d, measurable changes in length and/or weight of test organism |
Hamilton et al., 1990 |
|
|
swim-up larvae |
F, M, 1 |
selenomethionine |
210.0 |
pH = 7.7; Temp. = 13.7°C; Alkalinity = 109 mg/L |
- |
in diet 3.200-35.400 ug Se/g wet wt (mosquito-fish from San Luis Drain or fortified with selenomethionine) |
90 d freshwater study, survival was reduced in fish fed = 9.6 of either diet; reduced growth in fish fed = 5.300 of SLD diet = 18.200 fortified diet; reducedgrowth, whole-body concs. and survival, strongly correlated to concs. of Se in both diets |
||
|
fingerlings 70 mm |
F, M, 1 |
selenomethionine |
- |
pH = 7.4 for first 30 days and 6.9 for rest; Temp. = 12.6 for first 30 days and 13.3°C for rest; Alkalinity = 109 mg/L |
- |
in diet 3.200-35.400 ug Se/g wet wt (mosquito-fish from San Luis Drain or fortified with selenomethionine) |
120-d brackish water study, survival was unaffected but growth was reduced infish fed = 9.600 and 18.200 of SLD diet or 35.400 of selenomethionine diet. Survival was reduced in a 10-day seawater challenge test in fish fed 35.400 of either diet |
||
|
fry |
F, M, 1 |
- |
371.0 |
Temp. = 12.0°C |
0.017 |
- |
30-d, significant mortality |
Hamilton et al., 1986 |
|
|
Onchorhynchus tshawytscha (chinook salmon) (cont.) |
- |
- |
- |
- |
- |
- |
in diet 26.000 ug Se/g (not stated whether wet or dry wt) |
30-d, measurable changes in length and or weight of test organism |
Hamilton et al., 1986 (cont.) |
|
parr |
F,M,1 |
- |
74.0 |
Temp. = 10.0°C |
- |
in diet 13.000 (from Se contaminated organisms, 3% body weight per day feeding) |
6-wk, reduced smolting success; in survivors, whole body = 2.9 ug Se/g wet wt, 13.4 dry wt |
||
|
Perca flavescens (yellow perch) |
- |
- |
selenite |
10.2 |
- |
4.800 |
- |
10-d LC50 |
Klaverkamp et al., 1983 |
|
Perca fluviatilis (European perch) |
adult |
F,M,1 |
- |
- |
- |
5.600 |
- |
in fish tissue LOAEC |
Crane et al., 1992 |
|
Perca fluviatilis (European perch) (cont.) |
- |
- |
- |
300.0 |
pH = 7.9; Temp. = 15.0°C |
0.025 |
- |
10-12-d, change in % hatch or time to hatch |
|
|
adult |
F, M, 1 |
selenate / selenite (60:40 ratio) |
- |
pH = 7.5-11.0 |
0.025 |
- |
513-d chronic study, mean wt 71.38 g, Se conc in muscle and gonad, 5.63 ug Se/g wet wt and 6.96. Almost a 50% mortality |
||
|
- |
- |
- |
- |
- |
0.025 |
- |
529-543-d, change in male or female reprocuctive ability |
||
|
Pimephales promelas (fathead minnows) |
adult |
F,M,1 |
25% seleno-L-methionine, 50%selenate and 25% selenite |
139.4 |
pH = 8.19; D.O. = 8.48 mg/L; Temp. = 25.7 °C; Alkalinity = 247.4 mg/L |
- |
in diet 20.000 and 30.000 ug Se/g wet wt |
105-d study, growth significantly inhibited; no effect on the reproductive parameters |
Ogle and Knight, 1989 |
|
adult |
F,M,1 |
25% seleno-L-methionine 50% selenate and 25% selenite |
- |
Temp. = 25°C |
- |
in diet 40.000 ug Se/g wet wt |
in a range finding experiment, feeding and growth were reduced but no mortality attributed to starvationwas observed; at this and higher treatments, no spawning occurred |
||
|
adult |
F,M,1 |
25% seleno-L-methionine 50% selenate and 25% selenite |
- |
Temp. = 25°C |
- |
in diet 80.000 and 160.000 ug Se/g wet wt |
in range finding experiment fish developed severe edema within 24 hrs and were not observed feeding during remainder of experiment |
||
|
Pimephales promelas (fathead minnows) (cont.) |
adult |
F,M,1 |
25% seleno-L-methionine 50% selenate and 25% selenite |
- |
Temp. = 25°C |
- |
in diet 5.000-30.000 ug Se/g wet wt |
14-98-d, measurable changes in length and or weight of test organism |
Ogle and Knight, 1989 (cont.) |
|
adult |
F,M,1 |
25% seleno-L-methionine 50% selenate and 25% selenite |
- |
Temp. = 25°C |
- |
in diet 5.000-30.000 ug Se/g wet wt |
98-d, change in male and/or female reproductive ability |
||
|
adult |
F,M,1 |
25% seleno-L-methionine 50% selenate and 25% selenite |
- |
Temp. = 25°C |
- |
in diet 20.000 ug Se/g wet wt |
LOAEC, from day 56 on, observable differences in mean weight of fish was obvious |
||
|
embryos |
F, M,1 |
selenite |
- |
- |
0.010 |
- |
1-yr study, 24.6% edema compared to control of 0.9%; and 23.4% occurance of lordosis compared to 5.6% in control; larvae rather than egg development is affected by Se |
Schultz and Hermanutz, 1990 |
|
|
- |
- |
selenite |
- |
- |
4.500 |
- |
5-d LC50, mortality |
Cardwell et al., 1976a |
|
|
- |
- |
selenite |
- |
- |
3.200 |
- |
6-d LC50, mortality |
||
|
- |
- |
selenite |
- |
- |
2.900 |
- |
7-d LC50, mortality |
||
|
- |
- |
selenite |
220.0 |
- |
0.113 |
- |
chronic effect-early life stage |
Kimball Manuscript |
|
|
- |
- |
selenite |
220.0 |
- |
0.420 |
- |
8-d LC50 (fed) |
||
|
- |
- |
selenate |
45.0-47.0 |
- |
0.566 |
- |
chronic effect-early life stage |
Spehar, 1986 |
|
|
0.03 g (25-35 days old) |
- |
selenite |
329.0 |
pH = 7.3; D.O. = 5.3-6.2 mg/L; Temp. = 25°C; Alkalinity = 332.o mg/L |
0.600 |
- |
14-d LC50, mortality (fed) |
Halter et al., 1980 |
|
|
2 days old |
- |
selenite |
329.0 |
pH = 7.3; D.O. = 5.3-6.2 mg/L; Temp. = 25°C; Alkalinity = 332.o mg/L |
10.000 |
- |
17-d, change in ability to grow to a more mature life stage and in time between separate life stages |
||
|
2 days old |
- |
selenite |
329.0 |
pH = 7.3; D.O. = 5.3-6.2 mg/L; Temp. = 25°C; Alkalinity = 332.o mg/L |
40.000 |
- |
17-d, change in % hatch or time to hatch |
||
|
Pimephales promelas (fathead minnows) (cont.) |
- |
F,M,1 |
- |
- |
- |
0.010 |
- |
1 yr (approx), malformations (extended operculums, pointed snouts, exaggerated mandible angles, humped backs, and missing scales |
Hermanutz, 1992 |
|
- |
F,M,1 |
- |
- |
- |
0.030 |
- |
1 yr (approx), high mortality; malformations: extended operculums, pointed snouts, exaggerated mandible angles, humped backs, and missing scales |
||
|
adult |
- |
selenite |
157.0 |
- |
2.100 |
- |
9-d LC50 |
Cardwell et al., 1976a,b |
|
|
larvae, adult |
- |
selenate |
330.0-338.0 |
- |
1.100-2.000 |
- |
48-d LC50 |
Adams, 1976 |
|
|
- |
- |
- |
- |
- |
0.083-0.153 |
- |
life cycle LC50 |
USEPA, 1980 |
|
|
KEY |
|||||||||
|
LC = Lethal Concentration |
M = Measured |
||||||||
|
EC = Effective Concentration |
N = Nominal |
||||||||
|
S = Static Test Method |
NA = Not Available |
||||||||
|
F = Flowthrough Test Method |
1 = Primary |
||||||||
|
2 = Secondary |
|||||||||