13.02.2013 Views

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

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

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

SHOW MORE
SHOW LESS

You also want an ePaper? Increase the reach of your titles

YUMPU automatically turns print PDFs into web optimized ePapers that Google loves.

AX5-54<br />

Citation<br />

Sokol et al.<br />

(1985) †<br />

Sokol et al.<br />

(1994)<br />

Sokol et al.<br />

(2002)<br />

Thoreux-<br />

Manlay et al.<br />

(1995a)<br />

Thoreux-<br />

Manlay et al.<br />

(1995b)<br />

Wadi and<br />

Ahmad (1999)<br />

Wenda-<br />

Rózewicka<br />

et al. (1996)<br />

Yu et al.<br />

(1996)<br />

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

Species/<br />

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

Rat/Wistar,<br />

52 days old<br />

Rat/Sprague-<br />

Dawley,<br />

100 days old<br />

Rat/Sprague-<br />

Dawley, adult<br />

Rat/Sprague-<br />

Dawley, 97 days<br />

old<br />

Rat/Sprague-<br />

Dawley, adult<br />

Mouse/CF-1,<br />

adult<br />

Rat/Wistar,<br />

adult<br />

Rat/Sprague-<br />

Dawley,<br />

neonates<br />

0.1 or 0.3% Pb acetate in<br />

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

0.3% Pb acetate in drinking<br />

water <strong>for</strong> 14, 30, or 60 days<br />

Negative correlations between PbB levels and serum and intratesticular testosterone<br />

values; dose-dependent reduction in intratesticular sperm count; FSH values were<br />

suppressed; no change in LH; decrease in ventral prostatic weight; no difference in<br />

testicular or seminal vesicle weights.<br />

Pb exposed fertilized fewer eggs; increased duration <strong>of</strong> exposure did not result in more<br />

significant percentage <strong>of</strong> eggs not fertilized; no ultrastructural changes were noted in<br />

the spermatozoa <strong>of</strong> animals; no difference in histogram patterns <strong>of</strong> testicular cells.<br />

Pb acetate in water <strong>for</strong> 1 wk Dose-related increase in gonadotropin-releasing hormone (GnRH) mRNA; no effect<br />

on the serum concentrations <strong>of</strong> hypothalamic gonadotropin-releasing hormone (GnRH)<br />

or LH.<br />

0–8 mg Pb acetate/kg i.p. <strong>for</strong><br />

5 days/wk, 35 days<br />

8 mg/kg-d Pb <strong>for</strong> 5 days/wk,<br />

35 days<br />

0.25 and 0.5% Pb acetate in<br />

drinking water <strong>for</strong> 6 wks<br />

1% aqueous solution <strong>of</strong> Pb<br />

acetate <strong>for</strong> 9 mo<br />

Neonatal and lactational<br />

exposure to 0.3% Pb acetate<br />

in drinking water beginning<br />

PND 1 to PND 21<br />

*Not including effects on the nervous or immune systems.<br />

† Candidate key study.<br />

No effects on spermatogenesis; decreased plasma and testicular testosterone by 80%;<br />

decreased plasma LH by 32%, indications <strong>for</strong> impaired Leydig cell function, no effects<br />

on fertility.<br />

Germ cells and Sertoli cells were not major target <strong>of</strong> Pb, accessory sex glands were<br />

target; epididymal function was unchanged; plasma and testicular testosterone dropped<br />

about 80%, plasma LH only dropped 32%.<br />

Low dose significantly reduced number <strong>of</strong> sperm within epididymis; high dose reduced<br />

both the sperm count and percentage <strong>of</strong> motile sperm and increased the percentage <strong>of</strong><br />

abnormal sperm within the epididymis; no significant effect on testis weight, high dose<br />

significantly decreased the epididymis and seminal vesicles weights as well as overall<br />

body weight gain; LH, FSH, and testosterone were not affected.<br />

Electron microscopic studies did not reveal any ultrastructural changes in the<br />

semiferous epithelium or in Sertoli cells; macrophages <strong>of</strong> testicular interstitial tissue<br />

contained (electron dense) Pb-loaded inclusions, usually located inside phagolisosomelike<br />

vacuoles; x-ray micro-analysis revealed that the inclusions contained Pb.<br />

Neonatal exposure to Pb decreased cold-water swimming endurance (a standard test <strong>for</strong><br />

stress endurance) and delayed onset <strong>of</strong> puberty in males and female <strong>of</strong>fspring, which<br />

was exacerbated by swimming stress.<br />

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

(PbB)<br />

PbB 34 ± 3 µg/dL or<br />

PbB 60 ± 4 µg/dL<br />

PbB ~40 µg/dL<br />

PbB 12–28 µg/dL<br />

PbB not reported<br />

PbB 1700 µg/dL<br />

PbB not reported<br />

PbB not reported<br />

PbB 70 µg/dL<br />

3ß-HSD, 3ß-hydroxysteriod dehydrogenase; dbcAMP, dibutyryl cyclic adenosine-3',5'-monophosphate; DTT, dithiothreitol; FSH, follicle stimulating hormone; G6PDH, glucose-6-phosphate<br />

dehydrogenase; GD, gestational day; GnRH, gonadotropin releasing hormone; hCG, human chorionic gonadotropin; IGF1, insulin-like growth factor 1; i.p., intraperitoneal; LDH, lactate<br />

dehydrogenase; LH, luteinizing hormone; LHRH, luteinizing hormone releasing hormone; LPP, lipid peroxidation potential; NCD, nuclear chromatin decondensation rate; NOS, not otherwise<br />

specified; PbB, blood lead concentration; PND, post-natal day; p.o., per os (oral administration); ROS, reactive oxygen species; SDH, succinic acid dehydrogenase; SOPR, sperm-oocyte penetration<br />

rate; StAR, steroidogenic acute regulatory protein; VC, vitamin C; VE, vitamin E; VMA, vanilmandelic acid

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!