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41

The minimum numbers shown in Table 3 indicate that thousands

of UK children from the shooting community may have gamebird

meal intakes exceeding those required to be at potential risk from

incurring the critical responses for IQ and SATs scores. Maximum

numbers of adults from the shooting community estimated to exceed

threshold intake rates for potential risk from incurring cardiovascular,

nephrotoxicity and spontaneous abortion critical responses tended to

be much smaller, ranging between zero and hundreds or thousands.

As was the case for the maxima in Table 2, the exception was for the

chronic kidney disease critical response from the dose-response

model used by EFSA (2010). The same comment applies to this result

as was made for the maxima.

CONCLUSIONS

People in the UK can be exposed to lead from ammunition principally

by ingestion of dietary lead derived from small fragments of lead shot

or bullets in game meat and the absorption of lead in the alimentary

tract. Mean lead concentrations inmeat fromboth large and small game

animals shot with lead ammunition are often elevated, and frequently

considerably elevated above the levels considered acceptable for

meat derived from the muscle tissue of non-game animals. Some

ammunition-derived dietary lead from the tissues of game animals

ingested by humans is absorbed in the alimentary tract and enters the

bloodstream. The absolute bioavailability of ammunition-derived lead

may be lower than that of lead in the general diet, but the extent to

which this is the case is unclear. However, the minimum plausible value

of absolute bioavailability of ammunition-derived lead is substantial

and capable of causing elevation of blood lead concentrations thorough

absorption of ammunition-derived dietary lead.

At least one million people in the UK consume wild game at least once

per year and surveys indicate that at least tens of thousands of people

from the shooting community are high-level consumers of wild-shot

game. The mean frequency of consumption of game meat by these

high-level consumers may exceed one game meat meal per week,

averaged over a whole year. There may be some high-level consumers

outside the shooting community who are not included in these

estimates. Many more people consume game less frequently.

There is no known requirement for lead by humans and no evidence for

a threshold of exposure such as dietary intake rate or of blood lead level

below which lead-induced negative health effects, such as increased

systolic blood pressure, risk of chronic kidney disease and reduction in

IQ score, can be considered to be completely absent.

Our calculations of minimum and maximum numbers of people in the

UK exceeding threshold intake rates of gamebird meat required to be

at potential risk of incurring the critical health effects identified by EFSA

(2010) and Green and Pain (2012) indicate that children are likely to be

the most numerous group vulnerable to negative effects on cognitive

development fromexposure to ammunition-derived lead. It is estimated

that thousands of children in the UK (calculated to be in the range 4,000

- 48,000) could be at potential risk of incurring a one point or more

reduction in IQ as a result of current levels of exposure to ammunition-

derived dietary lead. Numbers of adults potentially vulnerable to critical

health effects appear to be smaller, but the available data are too sparse

to be certain.

In accord with these conclusions, the UK Food Standards Agency

(FSA 2012) have advised that frequent consumers of game shot with

lead ammunition should eat less of this type of meat, and that this is

especially important in the case of toddlers and children, pregnant

women andwomen trying for a baby, because of the harm that lead can

cause to the brain and developing nervous system. This is consistent

with recent advice given following risk assessments by equivalent

agencies in a range of other European countries who consider that

these most vulnerable groups should eat little or no game shot with

lead ammunition (Germany, Spain, Sweden and Norway, see Knutsen

et al.

2015).

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UK human health risks from ammunition-derived lead