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Appendix D Food Codes for NHANES - OEHHA

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SRP Review Draft Version 2 June, 2012<br />

Table I.8. BAFs <strong>for</strong> Lead in Muscle Tissue of Fish from Lentic Ecosystems<br />

Location Species Lake Pb Water Pb Muscle BAF<br />

pH Concentration Concentration<br />

Darts Lake (1)<br />

Acidic water bodies<br />

White sucker 4.9-5.4 3.0 µg/L 0.13 µg/g 43<br />

Darts Lake (1) Yellow perch 4.9-5.4 3.0 µg/L 0.058 19<br />

Darts Lake (2) White sucker 4.9-5.4 1.5 0.13 87<br />

Darts Lake (2) Yellow perch 4.9-5.4 1.5 0.055 37<br />

Acidic lakes &<br />

ponds, NJ (3)<br />

Yellow perch 3.7-4.6 0.8 – 3.6 0.067 – 0.11 40<br />

Variable and circumneutral water bodies<br />

Rondaxe Lake<br />

(1)<br />

White sucker 5.8-6.7 2.0 0.048 24<br />

Rondaxe Lake<br />

(1)<br />

Yellow perch 5.8-6.7 2.0 0.058 29<br />

Rondaxe Lake<br />

(2)<br />

White sucker 5.8-6.7 2.3 0.050 22<br />

Rondaxe Lake<br />

(2)<br />

Yellow perch 5.8-6.7 2.3 0.050 22<br />

Moss Lake (1) White sucker 6.5-6.8 2.5 0.031 12<br />

Moss Lake (1) Yellow perch 6.5-6.8 2.5 0.024 10<br />

Witbank Dam,<br />

South Africa (4)<br />

Moggel ND* 140 2.00 14<br />

Sources: (1) Stripp et al. (1990), (2) Heit et al. (1989), (3) Sprenger et. al. (1988), (4) Nussey et<br />

al. (2000)<br />

* No data<br />

The field data indicate higher muscle BAFs in fish from highly acidified lakes (Table I.8).<br />

Cali<strong>for</strong>nia generally does not have the acidification problem that exists in the<br />

northeastern U.S. Thus, a BAF point estimate <strong>for</strong> Pb was based on fish from the<br />

variable pH and circumneutral lakes. The BAF data from Nussey et al. (2000) was also<br />

included, although water pH data were not provided in the report. We calculate an<br />

arithmetic average BAF of 19 combining all fish species (white sucker, yellow perch and<br />

moggel) from these lakes and recommend this value as the Pb BAF point estimate.<br />

I.2.2.6 Mercury (inorganic) and Methylmercury<br />

Mercury, like other metals deposited into water, can occur in a number of physical and<br />

chemical <strong>for</strong>ms. Physically, mercury can be freely dissolved or bound to organic matter<br />

or particles suspended in water. Mercury can be found as elemental mercury (Hg 0 ),<br />

inorganic ionic mercury (primarily Hg ++ ), or organic mercury (e.g., methylmercury<br />

(MeHg) or dimethylmercury).<br />

Mercury (Hg) enters aquatic ecosystems primarily as inorganic Hg, but MeHg is the<br />

dominant <strong>for</strong>m of Hg found in muscle tissue of freshwater fish (Spry and Wiener, 1991).<br />

MeHg has been shown to constitute virtually all, about 99% or greater, of the total Hg in<br />

I-24

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