2017
DOI: 10.1007/s10653-017-0016-5
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Spatial distribution and human health risk assessment of mercury in street dust resulting from various land-use in Ahvaz, Iran

Abstract: Mercury as a toxic element and its associated health hazard has been an important topic of research for urban pollution for many years. In this paper, the spatial distribution, pollution assessment, and health risk associated with Hg in roadside dust 96 street dust samples, representing differing land uses have been investigated. Land uses included residential areas (RA), industrial areas (IA), public gardens (PG), roadside areas (RS) and suburban areas (SA) in the city of Ahvaz, Iran were investigated. Compar… Show more

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Cited by 40 publications
(21 citation statements)
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“…RfD value for ingestion is 3.0•10 -4 (we used RfD for inorganic mercury (RAIS 2018), as in soil, water and sediments inorganic mercury salts are prevalent (Lymberidi 2005)). RfD values for skin absorption and inhalation are 2.10•10 -5 and 8.57•10 -5 , respectively (Nazarpour et al 2017); HQ<1 denotes the absence of noncarcinogenic risk, whereas HQ>1 means a hazardous effect to human health (US EPA 2002a;RAIS 2018) where CDI is daily intake from i -route: the sum of HQ value calculated for each of three routes represents HI -a hazard index, HI = ∑HQ (US EPA 1989).…”
Section: Non-carcinogenic Risk Assessmentmentioning
confidence: 99%
“…RfD value for ingestion is 3.0•10 -4 (we used RfD for inorganic mercury (RAIS 2018), as in soil, water and sediments inorganic mercury salts are prevalent (Lymberidi 2005)). RfD values for skin absorption and inhalation are 2.10•10 -5 and 8.57•10 -5 , respectively (Nazarpour et al 2017); HQ<1 denotes the absence of noncarcinogenic risk, whereas HQ>1 means a hazardous effect to human health (US EPA 2002a;RAIS 2018) where CDI is daily intake from i -route: the sum of HQ value calculated for each of three routes represents HI -a hazard index, HI = ∑HQ (US EPA 1989).…”
Section: Non-carcinogenic Risk Assessmentmentioning
confidence: 99%
“…Emissions from activities relating to rapid urbanisation, industrial plants and vehicular traffic in megacities provide challenges for urban and residential environments. Urban street dust particles are one of the indices for monitoring environmental urban contaminants (Brown and Peake, 2006;Nazarpour et al, 2017b;Babaei et al, 2018), such as toxic metals and polycyclic aromatic hydrocarbons (PAHs) that present potential harm to community health (Tang et al, 2013, Saeedi et al, 2012Soltani et al, 2015). Dermal and hand to mouth contact can result in direct exposure to such contaminated dust particles, especially in the case of children in school grounds, parks and city side roads (Ghanavati et al, 2018).…”
Section: Introductionmentioning
confidence: 99%
“…Dermal and hand to mouth contact can result in direct exposure to such contaminated dust particles, especially in the case of children in school grounds, parks and city side roads (Ghanavati et al, 2018). The source of toxic metals in street dust can be petroleum, industrial sources, vehicle emissions and geogenic/geochemical routes, such as weathering of parent materials, construction, roadside and atmospheric dust accumulation (Gunawardana et al, 2012, Nazarpour et al, 2017b. Toxic elements are not decomposable and reside in the soil/dust environment for a long time or can be resuspended into the atmosphere, presenting a potential hazard to human health (Cook et al, 2005, Zarasvandi et al, 2011Ghanavati., 2018).…”
Section: Introductionmentioning
confidence: 99%
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“…Industrial development as well as increasing population and number of vehicles in Ahvaz increased heavy metals deposition in street dust particles. Ahvaz city was one of those cities heavily polluted in the world (13). However, it is still not clear about the spatial distribution patterns and contamination levels of heavy metals in street dust in the industrial zones of Ahvaz.…”
Section: Introductionmentioning
confidence: 99%