Previous Page  31 / 156 Next Page
Information
Show Menu
Previous Page 31 / 156 Next Page
Page Background

29

0

0.01

0.02

0.03

0.04

0.05

0

10 20 30 40 50 60 70 80

Proportion

Age (years)

Figure 1:

Proportion of individuals who consumed gamebird meat

during a 4-day diet diary survey conducted as part of the UK

National Diet and Nutrition Survey in the years 2008/09 - 2011/12

in relation to age.

Each symbol represents the proportion for a group of

individuals in an age class that included at least 200 subjects. The thick

curve shows the asymptotic relationship P

g

= exp(-3.459-1.668 exp(-0.073

Age)) fitted to the disaggregated data by a maximum-likelihood method.

The thin curves show bootstrap 95% confidence limits. Results are shown

for both sexes combined because there was no indication of a significant

difference between the sexes.

We next multiplied the number of people estimated to be in

each year class of age in the UK (in mid-2013, from Office of

National Statistics 2014) by the estimated proportion of people

consuming gamebird meat for that age class from the analysis

reported above. Uncertainty in these estimates of proportions

was taken into account by the bootstrap method, but UK

population totals were taken to have been estimated without

error. The total number of people estimated to consume

gamebird meat in a typical 4-day period was 1,613,341 (95%

C.L. 1,293,414 – 1,931,975), which represents 2.52% of the UK

population (95% C.L. 2.02 – 3.01). Equivalent estimates were

made for sub-groups based on age. The estimated number of

children up to the age of 8.0 years that ate gamebird meat is

49,576 (95% C.L. 29,083 – 87,870). The estimated number of

children between 8.0 and 18.0 years that ate gamebird meat is

119,780 (95% C.L. 77,530 – 178,574). The estimated number of

adults that ate gamebird meat is 1,443,984 (95% C.L. 1,091,320

– 1,741,397). It should be noted that these are estimates of

numbers of people eating gamebird meat in a typical four day

period. They are likely to be representative of the situation

for any time of year because proportions of people eating

gamebirdmeat have previously been found to be similar within

and outside the shooting season (Taylor

et al.

2014). However,

the numbers of people eating gamebird meat over a longer

period, such as a year, would be larger than this unless people

are completely consistent from one 4-day period to another

in whether they eat game or not. Hence, these estimates are

minimum numbers of consumers of gamebird meat.

We analysed the NDNS data on the mean quantity of gamebird

meat eaten per day using polynomial ordinary least squares

regression of log-transformed values. This analysis included

data only from the 87 subjects who consumed gamebird

meat. We fitted the first-, second-, third-, fourth- and fifth

order polynomial regressions on the age class midpoint in

years. In none of these regression models did the effect of

age on daily gamebird meat consumption rate approach

statistical significance (P always > 0.50). Similarly, the effect of

sex did not approach statistical significance in any model (P

always ≈ 0.50). Visual inspection of the data (Figure 2) similarly

confirmed no sign of consistent effects of age or sex. We

therefore used a single log-normal distribution with no effects

of age or sex to describe the distribution of values. We used

bootstrap resampling of the 87 subjects, with replacement,

to obtain confidence intervals of parameter estimates. We

performed 1,000 bootstrap replicates and took the bounds

defined by the central 950 bootstrap estimates to represent

the 95% confidence limits. The mean of the log

e

-transformed

daily consumption rate in g/d was 2.511 (95% C.L. 2.294

- 2.725), which is equivalent to a geometric mean of 12.3

g/d (95% C.L. 9.9 – 15.3). The standard deviation of the log-

normal distribution was 1.044 (95% C.L. 0.896 – 1.160). The

arithmetic mean daily consumption rate was 19.1 g/d (95%

C.L. 15.5 – 22.6). Although these data derive from 4-day diet

diary periods, the arithmetic mean daily consumption rates for

those who eat gamebird meat are likely to apply to the whole

year, because sampling was representative of the whole year.

We estimated the total mass of gamebird meat eaten per year

by the whole UK population by multiplying the estimated

numbers of consumers by the arithmetic mean amount eaten

per day and the number of days in a year, with uncertainty

in numbers of people and consumption rates accounted for

using the bootstrap method. The total mass of gamebird meat

eaten per year by the whole UK population was estimated to

be 11,232 tonnes (95% C.L. 9,162 – 16,251).

UK human health risks from ammunition-derived lead