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. 2006 Dec 19;64(6):380–388. doi: 10.1136/oem.2006.026781

Table 2 Sensitivity of the model to changes in model input parameters: average mercury concentration over the whole modelled area, percentage change in concentration (compared with best estimate (model output B)), correlation between modelled mercury concentrations (compared with best estimate (model output B)), estimate of the population exposed to >10 ng/m3 mercury, and population‐weighted average exposure for those classified as exposed to >10 ng/m3 mercury.

Model parameters* Average mercury (ng/m3) Percentage change from model B Correlation with model B† Population exposed >10 ng/m3 Population‐weighted exposure‡ (ng/m3)
(B) Speke meteorological data (using Ringway TCA data) 4.29 Reference Reference 5490 22.75
(C) Ringway meteorological data 4.31 +0.5 0.940 10 190 19.48
(D) Crosby meteorological data 3.65 −14.9 0.986 3152 26.29
(E) Speke meteorological data (using Crosby TCA data) 4.26 −0.7 1.000 5544 22.56
(F) Speke meteorological data; no topography data 4.29 +/−0.0 0.996 4773 24.07
(G) Speke meteorological data; release temperature for chlor alkali plant 10.2°C 4.53 +5.9 0.998 6329 23.81
(H) Speke meteorological data; release temperature for chlor alkali plant 25°C 3.98 −7.2 0.999 4052 23.07
(I) Speke meteorological data; surface roughness 0.2 m 4.64 +8.2 0.995 7472 20.22
(J) Speke meteorological data; surface roughness 1.0 m 3.97 −7.5 0.995 4152 25.33
(K) Speke meteorological data; deposition velocity 0.47 cm/s 4.29 +/−0.0 1.000 5556 22.60

TCA, total cloud amount.

Model outputs B–F are also shown in fig 1.

*All models used emissions data and meteorological data for 2000.

†Two‐tailed p values all <0.01.

‡Population‐weighted average exposure for those classified as exposed to >10 ng/m3 mercury.