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

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AX5-53<br />

Table AX5-4.2 (cont’d). Effect <strong>of</strong> <strong>Lead</strong> on Reproduction and Development in Mammals Effects on Males<br />

Citation Species/Strain/Age Dose/Route/ Form/Duration Endpoint<br />

Saxena et al.<br />

(1990)<br />

Singh et al.<br />

(1993a)<br />

ITRC albino,<br />

(NOS), adult<br />

Monkey/<br />

Cynomolgus, birth<br />

Birth:<br />

300 days:<br />

Sokol (1987) Rat/Wistar, 52 days<br />

old<br />

Sokol (1989) Rat/Wistar, 27 days<br />

old<br />

8 mg/kg/d Pb acetate <strong>for</strong><br />

45 days<br />

0–1500 µg Pb acetate/kg-d in<br />

gelatin capsules <strong>for</strong> various<br />

durations: 3 control<br />

monkeys, 4 monkeys in<br />

infancy group (exposure first<br />

400 days), 5 in post-infancy<br />

group (exposure 300 days to<br />

9 yrs <strong>of</strong> age), 4 in lifetime<br />

group (exposure from birth<br />

until 9 yrs)<br />

0–0.3% Pb acetate in<br />

drinking water <strong>for</strong> 30 days<br />

0–0.6% Pb acetate in<br />

drinking water <strong>for</strong> 30 days +<br />

30 days recovery<br />

52 days old 0–0.6% Pb acetate in<br />

drinking water <strong>for</strong> 30 days +<br />

30 days recovery<br />

Sokol (1990) Rat/Wistar, 52 days<br />

old<br />

Sokol and<br />

Berman<br />

(1991)<br />

0–0.6% Pb acetate in<br />

drinking water <strong>for</strong> 7, 14, 30,<br />

60 days<br />

Rat/Wistar, NOS 0, 0.1, or 0.3% Pb acetate in<br />

drinking water <strong>for</strong> 30 days<br />

beginning at 42, 52, or<br />

70 days old; 8–11 control rats<br />

<strong>for</strong> each age, 8–11 rats <strong>for</strong><br />

each age in 0.1% group, 8–<br />

11 rats <strong>for</strong> each age in 0.3%<br />

group<br />

Alterations in SDH, G6PDH activity, cholesterol, and ascorbic acid contents and<br />

reduced sperm counts associated with marked pathological changes in the testis,<br />

after combined treatment with Pb and immobilization stress in comparison to either<br />

alone.<br />

Degeneration <strong>of</strong> seminiferous epithelium in all exposed groups (frequency not<br />

specified); ultrastructural alterations in seminal vesicles, most prominent in infancy<br />

and post-infancy groups (frequency not specified).<br />

Hyper-responsiveness to stimulation with both GnRH and LH (10); blunted<br />

response to naloxone stimulation (10).<br />

Suppressed intratesticular sperm counts, sperm production rate, and serum<br />

testosterone in both Pb treated groups (10–10); sperm parameters and serum<br />

testosterone normalized at the end <strong>of</strong> the recovery period in the pre-pubertal animals<br />

(27 days at start) (10) but not in the pubertal animals (52 days at start) (5).<br />

Decreased sperm concentration, sperm production rate and suppressed serum<br />

testosterone concentrations after 14 days <strong>of</strong> exposure; not dose related (NS).<br />

Dose-related suppression <strong>of</strong> spermatogenesis (decreased sperm count and sperm<br />

production rate) in the exposed rats <strong>of</strong> the two highest age groups (p < 0.05); doserelated<br />

suppression <strong>of</strong> serum testosterone in 52-day old rats (p = 0.04) and in 70-day<br />

old rats (p < 0.003).<br />

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

(PbB)<br />

PbB >200 µg/dL<br />

Chronic PbB

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