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Chemical | Exposure Endpoint Type | Endpoint Value | Life Cycle Stage | Toxicity Endpoint Type | Type |
---|---|---|---|---|---|
Duration of Incubation or Gestation | review | Exposure Factor Datasets | |||
Body Weight - Mean | review | Both Adults and Juveniles | Exposure Factor Datasets | ||
Age at Fledging, Metamorphosis, Weaning | review | Exposure Factor Datasets | |||
Clutches or Litters per year | review | Exposure Factor Datasets | |||
Clutch or Litter Size | review | Exposure Factor Datasets | |||
Age at Sexual Maturity | review | Exposure Factor Datasets | |||
Hatching Success | review | Exposure Factor Datasets | |||
Fledging or Weaning Rate | review | Exposure Factor Datasets | |||
Population Density | review | Exposure Factor Datasets | |||
DIELDRIN | review | TOX-MORT - dose-response data | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|---|
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-) | 293.43-820.93 ppm, lipid weight | concentrations of DDT, DDE, DDD (combined) in skin and brains, 2 years post-application | Not Reported | Not Reported | 3.2 km NE of Davis | 2 birds | 0.22 kg DDT/ha | TOX-EXP IND - accumulation | 1 application | experimental application | Toxicity Factor Datasets |
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-) | see figure | figure showing concentration of DDT and metabolites in skin and brains before and after application | Not Reported | Not Reported | 3.2 km NE of Davis | 27 birds (3-4/sampling time) | 0.22 kg DDT/ha | TOX-EXP IND - accumulation | 1 application | experimental application | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|---|
DIELDRIN | increased at 1 mg/kg | latency to formation of natural prey killing behaviors | Not Reported | Juvenile | collected in San Diego County, CA | 10-11/dose | 0, 1 mg/kg bw/d (87% active ingredient) | TOX-Non-Repro-Sublethal - behavioral effects | until death (max. 103 d) | gavage | Toxicity Factor Datasets |
DIELDRIN | increased at 1, 2, 4, 8 mg/kg/d | rate of mortality compared with controls | Not Reported | Juvenile | collected in San Diego County, CA | 10-11/dose | 0, 1, 2, 4, 8 mg/kg bw/d (87% active ingredient) | TOX-MORT - dose-response data | until death (max. 103 d) | gavage | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|---|
DDE (4,4'-) | 3.09 (0.09 SE) ppm, wet wt | concentration in eggs | Not Reported | Embryo | southern IL | 20 clutches, 104 eggs | 21.04 (3.51 SE) ppm in fat of adult females | TOX-EXP IND - accumulation | NR | parental transfer | Toxicity Factor Datasets |
DDE (4,4'-) | decreased | eggshell thickness index compared with reference samples collected in 1875-95 | Not Reported | Embryo | southern IL | 20 clutches, 104 eggs | 21.04 (3.51 SE) ppm in fat of adult females | TOX-REPRO - physiology | NR | parental transfer | Toxicity Factor Datasets |
DDE (4,4'-) | y = 92.610 - 2.412 log x | linear negative correlation of egg DDE concentration and shell thickness | Not Reported | Embryo | southern IL | 20 clutches, 104 eggs | 21.04 (3.51 SE) ppm in fat of adult females | TOX-REPRO - physiology | NR | parental transfer | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|---|
AMMONIUM NITRATE | significantly increased (138.5% +/- 86.1 SD) | percent increase in breeding territory size post-spray vs. unsprayed controls | Both Male and Female | Both Adults and Juveniles | MacArthur Agroecology Research Center, Archbold Biological Station | 4 control, 8 treatment territories | 54 kg/ha application rate | TOX-Non-Repro-Sublethal - indirect effects | approx. 1 month | application to habitat | Toxicity Factor Datasets |
AMMONIUM NITRATE | significantly earlier | timing of nesting season termination in pairs post-spray vs. unsprayed controls | Both Male and Female | Both Adults and Juveniles | MacArthur Agroecology Research Center, Archbold Biological Station | 4 control, 8 treatment territories | 54 kg/ha application rate | TOX-Non-Repro-Sublethal - indirect effects | approx. 1 month | application to habitat | Toxicity Factor Datasets |
AMMONIUM NITRATE | increased | loss of eggs, nestlings, fledglings and adults post-spray vs. unsprayed controls | Both Male and Female | Both Adults and Juveniles | MacArthur Agroecology Research Center, Archbold Biological Station | 4 control, 8 treatment territories | 54 kg/ha application rate | TOX-Non-Repro-Sublethal - indirect effects | approx. 1 month | application to habitat | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|---|
DIMETHOATE | 34% (27% SD) | mean reduction in blood serum cholinesterase activity compared to untreated | Male | Adult | Christmas tree farms; Sherbrooke, Quebec | 15-20 sparrows | 480 g active ingredient/litre | TOX-EXP IND - biomarkers | single | field application | Toxicity Factor Datasets |
DIAZINON | 27% (43% SD) | % reduction of blood serum cholinesterase compared to untreated | Not Reported | Not Reported | Christmas tree farms; Sherbrooke, Quebec | 20-29 sparrows | 500 g active ingredient/litre | TOX-EXP IND - biomarkers | single | field application | Toxicity Factor Datasets |
DIAZINON | 38% | mortality of eggs and nestlings (control 21 %) | Not Reported | Embryo, Nestling | Sherbrooke, Quebec | 9 nests | 500 g active ingred/litre | TOX-MORT - mortality in the field | single | field application | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|---|
DIMETHOATE | significant reduction of mean daily activity levels (perch hopping) | Not Reported | Not Reported | 7 treated; 7 control | average food intake 2.14 g (0.48SE)/d ; 0.24 g Dimethoate sprayed over 1 m2 seeds; | TOX-Non-Repro-Sublethal - behavioral effects | single; (1 seed lot0 | diet | Toxicity Factor Datasets | ||
DIMETHOATE | 3.4 | weight loss (3.4 g over experiment period; controls gained 0.43 g) | g | Not Reported | Not Reported | 7 treated; 7 control | 0.24 g Dimethoate sprayed over 1 m2 seeds | TOX-Non-Repro-Sublethal - indirect effects | single; (1 seed lot0 | diet | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|---|
FONOFOS, TERBUFOS | no effect | reproductive parameters (reproductive success, clutch size, number of unhatched eggs, number of young fledged/nest) of nests located on edges of sprayed fields | Both Male and Female | Both Adults and Juveniles | southwestern Ontario | 60 treatment, 32 control nests | 6 fields treated with fonofos; 5 fields treated with terbufos (application rates were according to recommended guidelines, Ontario Ministry of Agriculture and Food) | TOX-REPRO - reproductive success | NR | field application | Toxicity Factor Datasets |
FONOFOS, TERBUFOS | no effect | survival of banded individuals, pre- versus post-application, up to 50 days post-application | Both Male and Female | Adult | southwestern Ontario | 88 males, 44 females (treatment); 69 males, 27 females (control) | 6 fields treated with fonofos; 5 fields treated with terbufos (application rates were according to recommended guidelines, Ontario Ministry of Agriculture and Food) | TOX-MORT - mortality in the field | NR | field application | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|---|
DIBENZ[A]ANTHRACENE (1,2,5,6-) | 5 | description | Both Male and Female | Adult | location | sample size | exposure | TOX-MORT - toxicity benchmarks | duration | route | Toxicity Factor Datasets |