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

Create successful ePaper yourself

Turn your PDF publications into a flip-book with our unique Google optimized e-Paper software.

AX5-46<br />

Citation<br />

Chowdhuri<br />

et al. (2001)<br />

Chowdhury<br />

et al. (1984)<br />

Chowdhury<br />

et al. (1986)<br />

Chowdhury<br />

et al. (1987)<br />

C<strong>of</strong>figny et al.<br />

(1994) †<br />

Corpas et al.<br />

(1995)<br />

Corpas et al.<br />

(2002a)<br />

Corpas et al.<br />

(2002b)<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 />

Mouse/<br />

BALB/c,<br />

3 mo old<br />

Rat/Albino,<br />

(NOS), adult<br />

0.0, 0.2, 0.5, 1.0, 2.0 µg/mL<br />

Pb acetate in culture medium<br />

<strong>for</strong> 2 hr (superovulated ova<br />

and sperm)<br />

Dietary concentrations <strong>of</strong><br />

0.25, 0.50, or 1.0 g/L Pb<br />

acetate <strong>for</strong> 60 days<br />

Rat/NOS, adult 0, 1, 2, 4, 6 mg Pb<br />

acetate/kg-d i.p.<br />

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

Rat/Charles<br />

Foster,<br />

150 ± 5 g<br />

Rat/Sprague-<br />

Dawley, adult<br />

Rat/Wistar,<br />

adult<br />

Rat/Wistar,<br />

adult<br />

Rat/Wistar,<br />

adult<br />

0, 1, 2, 4, 6 mg Pb<br />

acetate/kg-d/i.p.<br />

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

Inhalation exposure to<br />

5 mg/m 3 Pb oxide daily <strong>for</strong><br />

13 days during gestation<br />

(GD 2, 3, 6–10, 13–17, 20)<br />

300 mg/L Pb acetate via<br />

drinking water beginning GD<br />

1 through 5 days postnatal or<br />

throughout gestation and<br />

early lactation<br />

300 mg/L acetate Pb in<br />

drinking water beginning at<br />

mating until PND 12 and 21<br />

300 mg/L acetate Pb in<br />

drinking water beginning at<br />

mating until PND 12 and 21<br />

Significant dose dependent decrease in the number <strong>of</strong> sperm attaching to the ova in both<br />

exposed groups; decrease in the incorporation <strong>of</strong> radio-labeled thymdine, uridine, and<br />

methionine.<br />

Testicular atrophy along with cellular degeneration was conspicuous at 1 g/L; high<br />

cholesterol concentration and significantly low ascorbic acid concentration were found<br />

in the testes at 1 g/L; lowest dose (0.25 g/L) had no significant morphological and<br />

biochemical alterations, whereas as 0.5 g/L resulted in partial inhibition <strong>of</strong><br />

spermatogenesis.<br />

Dose-related decrease <strong>of</strong> testis weight; at 187 µg/dL: degenerative changes in testicular<br />

tissues; at 325 µg/dL: degenerative changes and inquiry <strong>of</strong> spermatogenetic cells;<br />

edematous dissociation in interstitial tissue.<br />

Dose related decrease <strong>of</strong> testis weight at 56 µg <strong>of</strong> spermatoids; at 91 µg/dL: inhibition<br />

<strong>of</strong> post-meiotic spermatogenic cell; at 196 µg/dL: decreased spermatogenic cell count<br />

(6), detachment <strong>of</strong> germinal call layers; at 332 µg/dL: Decreased spermatogenic cell<br />

count, degenerative changes, Interstitial edema, and atrophy <strong>of</strong> Leydig cells.<br />

Adult male <strong>of</strong>fspring exhibit no change in sperm parameters or sex hormones T, FSH,<br />

and LH (because <strong>of</strong> duration or timing).<br />

Testicular weight and gross testicular structure were not altered; seminiferous tubule<br />

diameter and the number <strong>of</strong> prospermatogonia were reduced; total DNA, RNA, and<br />

protein content <strong>of</strong> the testes in treated rats was significantly reduced, DNA:RNA ratio<br />

remained unaltered.<br />

Neither abnormalities in the liver structure nor depositions <strong>of</strong> Pb, toxicant produced<br />

biochemical alterations; pups exhibited decrease in hemoglobin, iron and alkaline, and<br />

acid phosphatase levels and an increase in Pb content; protein, DNA, and lipid total<br />

amounts were reduced, and hepatic glycogen content was diminished at 12 and 21 PN,<br />

with a higher dose <strong>of</strong> glucose in blood; decrease in alkaline phosphatase in liver <strong>of</strong> pups<br />

at day 21 PN, but acid phosphatase was unaltered.<br />

Neither abnormalities in the liver structure nor depositions <strong>of</strong> Pb, toxicant produced<br />

biochemical alterations; pups exhibited decrease in hemoglobin, iron and alkaline, and<br />

acid phosphatase levels and an increase in Pb content; protein, DNA, and lipid total<br />

amounts were reduced, and hepatic glycogen content was diminished at 12 and 21 PN,<br />

with a higher dose <strong>of</strong> glucose in blood; decrease in alkaline phosphatase in liver <strong>of</strong> pups<br />

at day 21 PN, but acid phosphatase was unaltered.<br />

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

(PbB)<br />

PbB not applicable–in vitro study<br />

PbB 54–143 µg/dL<br />

PbB 20, 62, 87, 187, or<br />

325 µg/dL<br />

PbB 56–3332 µg/dL<br />

PbB 71.1 µg/dL (dam)<br />

PbB 83.2 µg/dL (fetal)<br />

PbB 14 µg/dL<br />

PbB 22 µg/dL<br />

PbB 22 µg/dL

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

Saved successfully!

Ooh no, something went wrong!