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Air Quality Criteria for Lead Volume II of II - (NEPIS)(EPA) - US ...

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AX5-43<br />

Citation<br />

Ronis et al.<br />

(1998c)<br />

Ronis et al.<br />

(2001) †<br />

Sant'Ana et al.<br />

(2001)<br />

Singh et al.<br />

(1993b)<br />

Watson et al.<br />

(1997)<br />

Table AX5-4.1 (cont’d). Effect <strong>of</strong> <strong>Lead</strong> on Reproduction and Development in Mammals Effects on Offspring<br />

Species/<br />

Strain/Age<br />

Rat/Sprague-<br />

Dawley, adult<br />

Rat/Sprague-<br />

Dawley,<br />

neonate, male<br />

(100 days) and<br />

female pup<br />

Rat/Wistar,<br />

90 days old<br />

Rat/ITRC,<br />

albino (NOS),<br />

6 wks old<br />

Rat/Sprague-<br />

Dawley, adult<br />

Dose/Route/<br />

Form/Duration Endpoint<br />

Pb acetate 0.05, 0.15, or<br />

0.45% in drinking water<br />

beginning GD 5 continuing<br />

until PND 21, 35, 55, or 85;<br />

5 control litters (0%),<br />

10 low-dose litters (0.05%),<br />

8 mid-dose litters (0.15%),<br />

9 high-dose litters (0.45%);<br />

4 male and 4 female pups<br />

per litter<br />

Pb acetate in drinking water<br />

to 825 or 2475 ppm ad<br />

libitum from G'D 4 to GD 55<br />

postpartum; 1 male and<br />

female pup/litter (5 litters per<br />

group) control group, 1 male<br />

and female pup/litter (5 litters<br />

per group) 825 ppm Pb<br />

acetate group, 1 male and<br />

female pup/litter (5 litters per<br />

group) 2475 ppm Pb acetate<br />

group<br />

0.1 and 1% Pb in drinking<br />

water<br />

7 days<br />

250, 500, 1000, and 2000<br />

ppm Pb nitrate in drinking<br />

water from GD 6 to GD 14<br />

Pb in drinking water at<br />

34 ppm from weaning <strong>of</strong><br />

mothers through gestation<br />

and weaning <strong>of</strong> <strong>of</strong>fspring<br />

until birth; 6 pups control<br />

group, 6 pups experimental<br />

group<br />

Dose-responsive decrease in birth weight (p < 0.05), and crown-to-rump length<br />

(p < 0.05); dose-responsive delay in sexual maturity in male (p < 0.05) and female<br />

(p < 0.05); neonatal decrease in sex steroids (p < 0.05); pubertal decrease in<br />

testosterone (male) (p < 0.05) and E2 (female) (p < 0.05); decrease estrous cyclicity at<br />

high dose (p < 0.05).<br />

Dose-dependent decrease <strong>of</strong> the load <strong>of</strong> failure in male (p < 0.05); no difference in<br />

plasma levels <strong>of</strong> vitamin D metabolites; reduced somatic growth (p < 0.05),<br />

longitudinal bone growth (p < 0.05), and bone strength during the pubertal period<br />

(p < 0.05); sex steroid replacement did not restore skeletal parameters in Pb exposed<br />

rats; L-Dopa increased plasma IGF1 concentrations, rates <strong>of</strong> bone growth, and bone<br />

strength measures in controls while having no effect in Pb exposed groups; DO gap xray<br />

density and proximal new endostreal bone <strong>for</strong>mation were decreased in the<br />

distration gaps <strong>of</strong> the Pb-treated animals (p < 0.01); distraction initiated at 0.2 mm 30 to<br />

60 days <strong>of</strong> age.<br />

1% Pb exposure reduced <strong>of</strong>fspring body weight during treatment, no changes observed<br />

after 0.1% exposure; no altered <strong>of</strong>fspring sexual maturation, higher Pb improved sexual<br />

behavior, while 0.1% reduced it; 0.1% Pb caused decrease in testis weight, an increase<br />

in seminal vesicle weight, and no changes in plasma testosterone levels, hypothalamic<br />

VMA levels were increased compared to control group; reduced birth weight and<br />

growth rates.<br />

Significantly reduced litter size, reduced fetal weight, and a reduced crown-to-rump<br />

length, increased resorption and a higher blood-Pb uptake in those groups receiving<br />

1000 and 2000 ppm Pb; these also had a higher placental uptake; however the level was<br />

the same in both groups; fetal Pb uptake remained the same whether or not 2000 ppm<br />

Pb was given to an iron-deficient or normal iron groups <strong>of</strong> mothers.<br />

Reduced body weight (p = 0.04); parotid function was decreased by nearly 30%<br />

(p = 0.30); higher mean caries scores than the control pups (p = 0.005); pre- and<br />

perinatal Pb exposure had significantly increased susceptibility to dental caries<br />

(p = 0.015).<br />

Blood <strong>Lead</strong> Concentration<br />

(PbB)<br />

Dams: 0, 48, 88, or 181 µg/dL<br />

Pups PND 1: 120 µg/dL<br />

Pups PND 21: 50, >160, or<br />

~237 µg/dL<br />

Pups PND 35: 70, or<br />

>278 µg/dL<br />

Pups PND 55: 68, >137, or<br />

~380 µg/dL<br />

Pups PND 85: 43, >122, or<br />

>214 µg/dL<br />

PbB at 825 ppm was 67–<br />

192 µg/dL<br />

PbB at 2475 ppm was 120–<br />

388 µg/dL<br />

PbB 36.12 — 9.49 µg/dL or<br />

13.08 ± 9.42 µg/dL<br />

PbB not reported<br />

PbB 48 ± 13 µg/dL

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