%0 Journal Article
%9 ACL : Articles dans des revues avec comité de lecture répertoriées par l'AERES
%A Ghorbel, M.
%A Munoz, Marguerite
%A Solmon, F.
%T Health hazard prospecting by modeling wind transfer of metal-bearing dust from mining waste dumps : application to Jebel Ressas Pb-Zn-Cd abandoned mining site (Tunisia)
%D 2014
%L fdi:010062561
%G ENG
%J Environmental Geochemistry and Health
%@ 0269-4042
%K Dust ; Metals ; Mining wastes ; Transfer modeling ; Air quality ; Health hazard
%K TUNISIE
%M ISI:000342088900010
%N 5
%P 935-951
%R 10.1007/s10653-014-9610-y
%U https://www.documentation.ird.fr/hor/fdi:010062561
%> https://www.documentation.ird.fr/intranet/publi/2014/10/010062561.pdf
%V 36
%W Horizon (IRD)
%X This work presents a modeling approach to simulate spatial distribution of metal contamination in aerosols with evaluation of health hazard. This approach offers the advantage to be non-intrusive, less expensive than sampling and laboratory analyses. It was applied to assess the impact of metal-bearing dust from mining wastes on air quality for a nearby community and agricultural lands in Jebel Ressas (Tunisia) locality. Dust emission rates were calculated using existing parameterization adapted to the contamination source composed of mining wastes. Metal concentrations were predicted using a Gaussian model (fugitive dust model) with, as input: emission rates, dump physical parameters and meteorological data measured in situ for 30 days in summertime. Metal concentration maps were built from calculated PM10 particle concentrations. They evidence the areas where Pb and Cd concentrations exceeded WHO guidelines (0.5 and 0.005 A mu g/m(3), respectively). Maximum concentrations of Pb and Cd in PM10 are, respectively, of 5.74 and 0.0768 A mu g/m(3) for measured wind speed values up to 22 m/s. Preferential areas of contamination were determined in agricultural lands to the NW from the source dump where Pb and Cd exceeded guidelines up to a distance of 1,200 m. The secondary spreading directions were SW and E, toward the village. Health hazard prospecting shown that a major part of the village was exposed to contaminated dust and that daily hazard quotient (HQ) values reached locally 118 and 158, respectively, for Pb and Cd during the study period. However, HQ variations in the village are high, both temporally and geographically.
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