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MERCURY A-8<br />

APPENDIX A<br />

MINIMAL RISK LEVEL (MRL) WORKSHEET<br />

Chemical name(s): Mercury (inorganic)<br />

CAS number(s): 7439-97-6<br />

Date: June 15, 2001<br />

Profile status: Final Draft<br />

Route: [ ] Inhalation [X] Oral<br />

Duration: [ ] Acute [ X ] Intermediate [ ] Chronic<br />

Key to figure: 17<br />

Species: Rat<br />

Minimal Risk Level: 0.002 [ X ] mg/kg/day [ ] ppm<br />

Reference: NTP. 1993. NTP technical report on the toxicology <strong>and</strong> carcinogenesis studies of mercuric<br />

chloride (CAS no. 7487-94-7) in F344/N rats <strong>and</strong> B6C3F 1 mice (gavage studies). NTP TR408.<br />

Experimental design: Fischer 344 rats (10/sex/group) were administered 0, 0.23, 0.46, 0.93, 1.9, or 3.7 mg<br />

Hg/kg/day as mercuric chloride in deionized water by oral gavage once daily 5 days per week <strong>for</strong> 26 weeks.<br />

Body weights were recorded weekly. Surviving animals were sacrificed <strong>and</strong> necropsied. Organ weights<br />

were determined <strong>for</strong> the brain, heart, liver, lung, kidney, thymus, <strong>and</strong> testes. Histopathological<br />

examinations were per<strong>for</strong>med.<br />

Effects noted in study <strong>and</strong> corresponding doses: The relative <strong>and</strong> absolute kidney weights were<br />

significantly increased <strong>for</strong> dosed males <strong>and</strong> <strong>for</strong> females exposed to at least 0.46 mg/kg/day. At the two<br />

low-dose groups <strong>and</strong> the control group, minimal nephropathy was observed in nearly all the males. At 0.93<br />

mg/kg/day level, renal tubule necrosis became more severe (moderate) <strong>and</strong> was statistically significant <strong>and</strong><br />

remained at this severity at the higher dose groups. The female rats had a significant increased incidence at<br />

the high dose only, <strong>and</strong> severity was minimal. Nephropathy was characterized by foci of tubular<br />

regeneration, thickened tubular basement membrane, <strong>and</strong> scattered dilated tubules containing hyaline casts.<br />

Macroscopic changes included granular kidneys in dosed males. After 4 months of exposure, urinary levels<br />

of alkaline phosphatase, aspartate aminotransferase, lactate dehydrogenase, <strong>and</strong> gamma-glutamyl<br />

transferase were significantly elevated in both sexes at 3.7 mg Hg/kg/day, but at 6 months control levels had<br />

increased such that enzyme levels in males were no longer statistically significant <strong>and</strong> only levels of<br />

alkaline phosphatase <strong>and</strong> gamma-glutamyl transferase were significantly elevated in females.<br />

Dose end point used <strong>for</strong> MRL derivation: 0.23 mg Hg/kg/day; no renal effects<br />

[X ] NOAEL [ ]LOAEL<br />

Uncertainty <strong>and</strong> modifying factors used in MRL derivation: 100<br />

[ ] 1 [ ] 3 [ ] 10 (<strong>for</strong> use of a LOAEL)<br />

[ ] 1 [ ] 3 [ X ] 10 (<strong>for</strong> extrapolation from animals to humans)<br />

[ ] 1 [ ] 3 [ X ] 10 (<strong>for</strong> human variability)<br />

Was a conversion factor used from ppm in food or water to a mg/body weight dose?<br />

If so explain: No conversion factor used.<br />

Was a conversion used from intermittent to continuous exposure?

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