Table 18.
Comparison of estimated ZEN exposure levels and NOAELs/LOAELs for different farm and companion animal species
Estimated exposure (μg ZEN/kg bw per day)a | Estimated exposure, % of NOAEL or LOAEL | |||||
---|---|---|---|---|---|---|
NOAEL (μg ZEN/kg bw) | LOAEL (μg ZEN/kg bw) | P95 (UB) | mean (UB) | P95 (UB) | mean (UB) | |
Sheep | 28 | 56 | 4.32 | 0.89 | 15.4 | 3.2 |
Gilts | 40 | 200 | 3.17 | 1.16 | 7.9 | 2.9 |
Piglets | 10.4 (NOEL) | 17.6 (LOEL) | 2.20 | 0.94 | 21.1 | 9 |
Chickenb | 7,500 | 30,000 | 16.1 | 4.66 | 0.22 | 0.062 |
Turkeys (fattening)c | 9,100 | 19,000 | c | 1.24 | c | 0.014 |
Fish (carp) | 9 | 18 | 2.18 | 0.55 | 24.2 | 6.11 |
Dogs | – | 25 | 0.70 | 0.25 | 2.8 (LOAEL) | 1 (LOAEL) |
bw: body weight; ZEN: zearalenone; NOAEL: no observed adverse effect level; LOAEL: lowest observed adverse effect level; UB: upper bound.
Exposures have been calculated from dietary concentrations expressed on a fresh weight (88% dry matter) basis to make them comparable with the data from which NOAELS/LOAELS have been derived.
Exposure have been calculated for chicken of the age as reported by Chi et al. (1980a,b) to allow comparison with the NOAEL
Insufficient samples were provided to allow reliable 95th percentile estimates of exposure to be made.