LEAD (elemental)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries | Lab |
---|---|---|---|---|---|---|---|---|---|
LEAD (elemental) | Increased | Heart blood clot concentration | NR | Not Reported | 8 | Toxicity Factor Datasets | USA | ||
LEAD (elemental) | See citation | Blood concentration | Not Reported | 12 | Toxicity Factor Datasets | USA | Laboratory | ||
LEAD (elemental) | 0.02 ± 0.02 µg/g ww | Blood concentration | B | Both Adults and Juveniles | 3 | Samandağ & Dörtyol | Toxicity Factor Datasets | TURKEY | |
LEAD (elemental) | Decreased | Body weight | NR | Not Reported | 8 | Toxicity Factor Datasets | USA | ||
LEAD (elemental) | No effect | Liver concentration | Not Reported | 1 | Toxicity Factor Datasets | USA | Laboratory | ||
LEAD (elemental) | 0.03 ± 0.01 µg/g ww | Kidney concentration | B | Both Adults and Juveniles | 3 | Samandağ & Dörtyol | Toxicity Factor Datasets | TURKEY | |
LEAD (elemental) | Increased | Blood concentration | NR | Not Reported | 8 | Toxicity Factor Datasets | USA | ||
LEAD (elemental) | 0.04 µg/g dw | Liver concentration | NR | Hatchling | 4 | Hamilton Harbour, Western Lake Ontario | Toxicity Factor Datasets | CANADA | Laboratory |
LEAD (elemental) | 0.03 ± 0.02 µg/g ww | Liver concentration | B | Both Adults and Juveniles | 3 | Samandağ & Dörtyol | Toxicity Factor Datasets | TURKEY | |
LEAD (elemental) | See citation Figure 3 | Delta-aminolevulinic acid dehydratase activity | NR | Not Reported | 8 | Toxicity Factor Datasets | USA | ||
LEAD (elemental) | 0.03 µg/g dw | Liver concentration | NR | Hatchling | 4 | Snake and Pigeon Islands, Eastern Lake Ontario | Toxicity Factor Datasets | CANADA | |
LEAD (elemental) | Median: 279.6, geometric mean: 1116.6 ng/g | Feather concentration | NR | Nestling | 21 | Birama Swamp | Toxicity Factor Datasets | CUBA | |
LEAD (elemental) | See citation Figure 3 | Erythrocyte protoporphryin activity | NR | Not Reported | 8 | Toxicity Factor Datasets | USA | ||
LEAD (elemental) | 41.2 ppb dw ± 40.9 | Egg concentration | Embryo | 2 | Agassiz National Wildlife Refuge | Toxicity Factor Datasets | USA | ||
LEAD (elemental) | 0.26 µg/g ww | Liver concentration | NR | Nestling | 5 | Mangrove estuary, west coast of Everglades National Park | Toxicity Factor Datasets | USA | |
LEAD (elemental) | See citation Figure 3 | Hematocrit | NR | Not Reported | 8 | Toxicity Factor Datasets | USA | ||
LEAD (elemental) | 4481 ppb dw ± 741 | Feather concentration | Both Adults and Juveniles | 5 | Agassiz National Wildlife Refuge | Toxicity Factor Datasets | USA | ||
LEAD (elemental) | 23.02 mg/kg | Femur concentration | NR | Not Reported | 10 | Chesterfield County | Toxicity Factor Datasets | USA | |
LEAD (elemental) | San Pedro: <0.5, Roosevelt: <0.5, Alamo: <0.5 µg/g dw | Egg concentration | San Pedro: 5, Roosevelt: 2, Alamo: 1 | Toxicity Factor Datasets | |||||
LEAD (elemental) | 0.55 mg/kg | Liver concentration | NR | Not Reported | 10 | Chesterfield County | Toxicity Factor Datasets | USA | |
LEAD (elemental) | See citation Table 1 | Hair concentration | B | Pup | 199 | Gulf of California | Toxicity Factor Datasets | MEXICO | |
LEAD (elemental) | 23.21 mg/kg | Femur concentration | NR | Not Reported | 10 | Chesterfield County | Toxicity Factor Datasets | USA | |
LEAD (elemental) | Review | Blood concentration | Canary Islands | Toxicity Factor Datasets | SPAIN | ||||
LEAD (elemental) | 0.50 mg/kg | Liver concentration | NR | Not Reported | 10 | Chesterfield County | Toxicity Factor Datasets | USA | |
LEAD (elemental) | 0.006 ± 0.0008 µg/g ww | Eggshell concentration | NR | Embryo | 12 | Guadeloupe, French West Indies | Toxicity Factor Datasets | ||
LEAD (elemental) | 0.58 mg/kg | Kidney concentration | NR | Not Reported | 10 | Chesterfield County | Toxicity Factor Datasets | USA | |
LEAD (elemental) | 88.8 ± 15.1 ppb | Blood concentration of live-captured | 29 | Pine Barrens | Toxicity Factor Datasets | USA | Laboratory | ||
LEAD (elemental) | Review | Eggshell concentration | NR | Embryo | 2 | Haha-Jimma Island | Toxicity Factor Datasets | JAPAN | |
LEAD (elemental) | 0.11 mg/kg | Thigh muscle concentration | NR | Not Reported | 10 | Chesterfield County | Toxicity Factor Datasets | USA |
Pacific Green Turtle (Chelonia mydas)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties | Countries |
---|---|---|---|---|---|---|---|---|---|
LEAD (elemental) | 0.013 ± 0.0012 µg/g ww | Egg concentration | Not Reported | Embryo | 12 | Guadeloupe, French West Indies | Toxicity Factor Datasets | ||
LEAD (elemental) | Blood concentration | Not Reported | Not Reported | Toxicity Factor Datasets | |||||
LEAD (elemental) | Review | Egg concentration | Not Reported | Embryo | 55 | Peninsular Malaysia | Toxicity Factor Datasets | MALAYSIA | |
LEAD (elemental) | Kidney concentration | Not Reported | Not Reported | Toxicity Factor Datasets | JAPAN | ||||
LEAD (elemental) | 0.006 ± 0.0008 µg/g ww | Eggshell concentration | Not Reported | Embryo | 12 | Guadeloupe, French West Indies | Toxicity Factor Datasets | ||
LEAD (elemental) | Liver concentration | Not Reported | Not Reported | Toxicity Factor Datasets | JAPAN | ||||
LEAD (elemental) | Review | Eggshell concentration | Not Reported | Embryo | 2 | Haha-Jimma Island | Toxicity Factor Datasets | JAPAN | |
LEAD (elemental) | Review | Eggshell concentration | Not Reported | Embryo | 30 | Hong Kong | Toxicity Factor Datasets | CHINA | |
LEAD (elemental) | 0.03 µg/g dw, 0.006 ww | Plasma concentration | Not Reported | 9 | Big Bend, Citrus County | Toxicity Factor Datasets | USA | ||
LEAD (elemental) | 1.11 ± 0.06 µg/g | Blood concentration | Both Male and Female | Juvenile | 7 | Bahia Salado | Toxicity Factor Datasets | CHILE | |
LEAD (elemental) | 0.003 ± 0.002 µg/g ww | Egg concentration | Both Male and Female | Embryo | 11 | Pacific Coast | Toxicity Factor Datasets | PANAMA | |
LEAD (elemental) | Review | Blood concentration | Antofogasta region | Toxicity Factor Datasets | CHILE | ||||
LEAD (elemental) | 3.31 ± 0.65 µg/g ww | Yolk concentration | Both Male and Female | Embryo | 48 eggs, 12 nests | Chabahar Beach | Toxicity Factor Datasets | IRAN | |
LEAD (elemental) | Review | Blood concentration | San Diego Bay | Toxicity Factor Datasets | San Diego | USA | |||
LEAD (elemental) | 3.02 ± 0.97 µg/g ww | Albumen concentration | Both Male and Female | Embryo | 48 eggs, 12 nests | Chabahar Beach | Toxicity Factor Datasets | IRAN | |
LEAD (elemental) | Review | Blood concentration | Queensland | Toxicity Factor Datasets | AUSTRALIA | ||||
LEAD (elemental) | 4.25 ± 0.56 µg/g ww | Eggshell concentration | Both Male and Female | Embryo | 48 eggs, 12 nests | Chabahar Beach | Toxicity Factor Datasets | IRAN | |
LEAD (elemental) | Review | Blood concentration | Canary Islands | Toxicity Factor Datasets | SPAIN | ||||
LEAD (elemental) | 0.77 ± 0.20 µg/g ww | Blood concentration | Both Male and Female | Embryo | 48 eggs, 12 nests | Chabahar Beach | Toxicity Factor Datasets | IRAN | |
LEAD (elemental) | Tumor score 0: 4.77, score 1: 3.77, score 2: 7.76, score 3: 11.15 µg/g dw | Blood concentration | Female | Juvenile | Tumor score 0: 13, score 1: 4, score 2: 4, score 3: 6 | Sao Paulo | Toxicity Factor Datasets | BRAZIL | |
LEAD (elemental) | Reference intervals for blood concentration | Both Male and Female | Both Adults and Juveniles | 49 | Howick Group of Islands | Toxicity Factor Datasets | AUSTRALIA |
American Kestrel (Falco sparverius)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
LEAD (elemental) | increase at 50 ppm 1.3 ppm (1.00 SD) males; 2.4 ppm (1.40 SD) females |
mean lead concentration in liver | Both Male and Female | Adult | 16 pairs/group | Toxicity Factor Datasets | Laboratory | |
LEAD (elemental) | no effect | mean organ and carcass weights | Both Male and Female | Adult | 16 pairs/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
LEAD (elemental) | 31% decrease at 625 mg/kg bw 14% decrease at 125 mg/kg bw |
hematocrit | Both Male and Female | Nestling | 10/group | Toxicity Factor Datasets | Laboratory | |
LEAD (elemental) | 48% decrease at 625 mg/kg bw 27% decrease at 125 mg/kg bw 12% decrease at 25 mg/kg bw |
red blood cell hemoglobin content | Both Male and Female | Nestling | 10/group | Toxicity Factor Datasets | Laboratory | |
LEAD (elemental) | decrease at all doses (45-59%) | red blood cell delta aminolevulinic acid dehydratase | Both Male and Female | Nestling | 10/group | Toxicity Factor Datasets | Laboratory | |
LEAD (elemental) | 30% decrease at 625 mg/kg bw 25% decrease at 125 mg/kg bw |
plasma creatine phosphokinase | Both Male and Female | Nestling | 10/group | Toxicity Factor Datasets | Laboratory | |
LEAD (elemental) | decrease at 125, 625 mg/kg bw (47-57%) | brain delta aminolevulinic acid dehydratase activity | Both Male and Female | Nestling | 10/group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
LEAD (elemental) | no effect | eggshell thickness | Female | Adult | 16 pairs/group | Toxicity Factor Datasets | Laboratory | |
LEAD (elemental) | no effect | lead concentration in eggshell | Female | Adult | 16 pairs/group | Toxicity Factor Datasets | Laboratory | |
LEAD (elemental) | 62.0 ppm tibia, 13.5 ppm humeri at 50 ppm | lead concentrations in bones | Female | Adult | 16 pairs/group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
LEAD (elemental) | 0.367 (0.129 SE) ppm at 49 mg/d | mean lead concentration (wet wt) in liver | Female | Adult | 3/group | Toxicity Factor Datasets | Laboratory | |
LEAD (elemental) | 28.70 (2.6 SE) ppm at 49 mg/d | mean lead concentration (wet wt) in bone | Female | Adult | 3/group | Toxicity Factor Datasets | Laboratory |
Mourning Dove (Zenaida macroura)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Error | Lab |
---|---|---|---|---|---|---|---|---|---|
LEAD (elemental) | no effect | body weight at hatch | Not Reported | Hatchling | 25 birds/dose | Toxicity Factor Datasets | Laboratory | ||
LEAD (elemental) | no effect | mortality | Female | Adult | 25 birds/dose | Toxicity Factor Datasets | Laboratory | ||
LEAD (elemental) | 169.2 ug/g, dry wt. | lead concentration in bone | Not Reported | Adult | 10 birds | Toxicity Factor Datasets | 33.9 SE | Laboratory | |
LEAD (elemental) | 198.2 ug/g, dry wt | lead concentration in bone | Not Reported | Adult | 10 birds | Toxicity Factor Datasets | 39.9 SE | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
LEAD (elemental) | decreased at all doses | delta-aminolevulinic acid dehydratase (ALAD)activity in blood | Both Male and Female | Adult | 10 birds/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
LEAD (elemental) | no effect | post-dosing survival of free-ranging radio-transmittered birds | Not Reported | Both Adults and Juveniles | 26 treated birds, 29 control birds | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
LEAD (elemental) | decreased | blood delta-aminolevulinic acid dehydratase activity | Not Reported | Not Reported | 5 birds | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
LEAD (elemental) | light lesions present | histological exam of acid-fast intranuclear inclusions of cells of kidney proximal convoluted tubules | Not Reported | Not Reported | 2 | Toxicity Factor Datasets | Laboratory |
Mallard duck (Anas platyrhynchos)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | California Counties | Lab |
---|---|---|---|---|---|---|---|---|---|---|
LEAD (elemental) | decreased @ 2 #four shot | spleen plaque forming cell counts, % packed cell volume versus controls | Both Male and Female | Adult | 16 (2 #four shot) 63 (field exposure) |
Sacramento National Wildlife Refuge | Toxicity Factor Datasets | 1 yr | Sacramento | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
LEAD (elemental) | lead only: 3.53 (+/- 1.43); lead-iron: 1.42 (+/- 0.65) ppm, wet wt | lead concentration in kidneys (mean +/- SE) | Female | Adult | control=2 F, 4 M; treatment=6 M-F pairs/group | Toxicity Factor Datasets | 6 mos | Laboratory | |
LEAD (elemental) | lead only: 1.02 (+/- 0.22); lead-iron: 0.75 (+/- 0.10) ppm, wet wt | lead concentration in kidneys (mean +/- SE) | Male | Adult | control=2 F, 4 M; treatment=6 M-F pairs/group | Toxicity Factor Datasets | 6 mos | Laboratory | |
LEAD (elemental) | lead only: 1.15 (+/- 0.29); lead-iron: 0.32 (+/- 0.05) ppm, wet wt | lead concentration in liver (mean +/- SE) | Female | Adult | control=2 F, 4 M; treatment=6 M-F pairs/group | Toxicity Factor Datasets | 6 mos | Laboratory | |
LEAD (elemental) | lead only: 0.58 (+/- 0.19); lead-iron: 0.25 (+/- 0.02) ppm, wet wt | lead concentration in liver (mean +/- SE) | Male | Adult | control=2 F, 4 M; treatment=6 M-F pairs/group | Toxicity Factor Datasets | 6 mos | Laboratory | |
LEAD (elemental) | decreased with increasing lead in bone | number of eggs laid | Female | Adult | control=2 F, 4 M; treatment=6 M-F pairs/group | Toxicity Factor Datasets | 6 mos | Laboratory | |
LEAD (elemental) | increased with lead shot (egg contents: 0.50 +/-0.06; egg shell: 2.80 +/-0.25 ppm, wet wt) and lead-iron shot (egg shell: 1.42 +/-0.26 ppm, wet wt) | lead in egg contents and shell (mean +/- SE) versus controls | Female | Adult | control=10 eggs; treatment=20 eggs | Toxicity Factor Datasets | 6 mos | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
LEAD (elemental), STEEL COMPOUNDS, TUNGSTEN COMPOUNDS | increased for lead shot | mortality rate versus all other groups | Both Male and Female | Adult | 16/treatment | Toxicity Factor Datasets | 6 mo | Laboratory | |
LEAD (elemental), STEEL COMPOUNDS, TUNGSTEN COMPOUNDS | increased for lead shot | incidence of clinical signs versus other groups | Both Male and Female | Adult | 16/treatment | Toxicity Factor Datasets | 6 mo | Laboratory | |
LEAD (elemental), STEEL COMPOUNDS, TUNGSTEN COMPOUNDS | 10.3(0.7) ppm in femur, 14.1(0.6) ppm in liver, 6.8(0.2) in kidneys | mean(SE) dry wt tungsten concentrations in tissues of tungsten-iron-dosed birds | Both Male and Female | Adult | 16/treatment | Toxicity Factor Datasets | 6 mo | Laboratory | |
LEAD (elemental), STEEL COMPOUNDS, TUNGSTEN COMPOUNDS | reduced for lead shot | body weight versus all other groups | Both Male and Female | Adult | 16/treatment | Toxicity Factor Datasets | 6 mo | Laboratory | |
LEAD (elemental), STEEL COMPOUNDS, TUNGSTEN COMPOUNDS | 4.3(0.7) ppm in femur, non-detect. in liver, 2.4(0.2) in kidneys | mean(SE) dry wt tungsten concentrations in tissues of tungsten-polymer-dosed birds | Both Male and Female | Adult | 16/treatment | Toxicity Factor Datasets | 6 mo | Laboratory | |
LEAD (elemental), STEEL COMPOUNDS, TUNGSTEN COMPOUNDS | reduced for lead shot | hematocrit and hemoglobin concentrations versus all other groups | Both Male and Female | Adult | 16/treatment | Toxicity Factor Datasets | 6 mo | Laboratory | |
LEAD (elemental), STEEL COMPOUNDS, TUNGSTEN COMPOUNDS | increased for lead shot | plasma activities of alanine aminotransferase, creatine phosphokinase, aspartate aminotransferase, lactate dehydrogenase versus control group | Both Male and Female | Adult | 16/treatment | Toxicity Factor Datasets | 6 mo | Laboratory | |
LEAD (elemental), STEEL COMPOUNDS, TUNGSTEN COMPOUNDS | increased for lead shot | relative kidney weights versus controls | Both Male and Female | Adult | 16/treatment | Toxicity Factor Datasets | 6 mo | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
BISMUTH COMPOUNDS, IRON COMPOUNDS, LEAD (elemental) | decreased with Bi | weight of hatchlings versus controls | Both Male and Female | Juvenile | 18 pairs/group (control, Fe, Bi); 6 pairs/Pb group | Toxicity Factor Datasets | 6-8 mo | Laboratory | |
BISMUTH COMPOUNDS, IRON COMPOUNDS, LEAD (elemental) | no effect with Fe or Bi | survival to 7 d, organ histopathology, hematocrit, sex ratios, kidney or liver weights of ducklings versus controls | Both Male and Female | Juvenile | 18 pairs/group (control, Fe, Bi); 6 pairs/Pb group | Toxicity Factor Datasets | 6-8 mo | Laboratory | |
BISMUTH COMPOUNDS, IRON COMPOUNDS, LEAD (elemental) | no effect with Fe or Bi | egg weight, eggshell thickness, fertility, hatchability versus controls | Both Male and Female | Adult | 18 pairs/group (control, Fe, Bi); 6 pairs/Pb group | Toxicity Factor Datasets | 6-8 mo | Laboratory | |
BISMUTH COMPOUNDS, IRON COMPOUNDS, LEAD (elemental) | no effect with Fe or Bi | histopathology of kidney, liver, testis, heart, lung versus controls | Both Male and Female | Adult | 18 pairs/group (control, Fe, Bi); 6 pairs/Pb group | Toxicity Factor Datasets | 6-8 mo | Laboratory | |
BISMUTH COMPOUNDS, IRON COMPOUNDS, LEAD (elemental) | 213(27.1) ppm, kidney; 91(4.55) ppm, liver; 9.8(3.22) ppm, ovary; 3.49(0.61) ppm, testis | mean(SE) wet wt concentrations of Pb in Pb-dosed birds | Both Male and Female | Adult | 18 pairs/group (control, Fe, Bi); 6 pairs/Pb group | Toxicity Factor Datasets | 6-8 mo | Laboratory | |
BISMUTH COMPOUNDS, IRON COMPOUNDS, LEAD (elemental) | 237(17.2) ppm, kidney; 1936(233) ppm, liver; 90.6(6.85) ppm, ovary; 13.1(1.29) ppm, testis | mean(SE) wet wt concentrations of Fe in Fe-dosed birds | Both Male and Female | Adult | 18 pairs/group (control, Fe, Bi); 6 pairs/Pb group | Toxicity Factor Datasets | 6-8 mo | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
LEAD (elemental) | 5.7 ppm (whole blood); 6.2 ppm (liver); 2.4 ppm (spleen) @ 300 mg/kg body weight | lead concentrations in tissues, 96 hr after exposure to lead in ducklings receiving vitamin E | Not Reported | Juvenile | 5/dose | Toxicity Factor Datasets | 1 d | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
IRON (elemental), LEAD (elemental) | increased @ 8 #four iron shot | serum glutamic pyruvic transaminase activity vs controls | Female | Adult | 8/group | Toxicity Factor Datasets | Laboratory | |
IRON (elemental), LEAD (elemental) | increased with all treatments | incidence of hemosiderosis in liver vs controls | Female | Adult | 8/group | Toxicity Factor Datasets | Laboratory | |
IRON (elemental), LEAD (elemental) | increased @ 8 #four iron shot | incidence of inclusion bodies in kidney vs controls | Female | Adult | 8/group | Toxicity Factor Datasets | Laboratory | |
IRON (elemental), LEAD (elemental) | no effect | serum enzyme levels versus controls (at 30 or 60 d post dose) | Male | Adult | 2/group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
BISMUTH COMPOUNDS, IRON COMPOUNDS, LEAD (elemental) | no differences | mean survival times compared among lead, iron and bismuth dosed birds | Both Male and Female | Adult | 5 males, 5 females per group | Toxicity Factor Datasets | 6-8 mo | Laboratory | |
BISMUTH COMPOUNDS, IRON COMPOUNDS, LEAD (elemental) | no differences | mean body weight and organ weights compared among lead, iron and bismuth dosed birds | Both Male and Female | Adult | 5 males, 5 females per group | Toxicity Factor Datasets | 6-8 mo | Laboratory | |
BISMUTH COMPOUNDS, IRON COMPOUNDS, LEAD (elemental) | no differences | mean hematocrit values compared among lead, iron and bismuth dosed birds | Both Male and Female | Adult | 5 males, 5 females per group | Toxicity Factor Datasets | 6-8 mo | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
LEAD (elemental) | decreased @ > 60 ug/dl blood | delta-aminolevulinic acid dehydratase activity | Both Male and Female | Not Reported | 21 birds | World Wildlife Fund Refuge, Tuscany | Toxicity Factor Datasets | ITALY |