Abstract

The paper analyzed the concentrations of trace metals in fine and respirable particulates (fine-PM1 and PM2.5; respirable-PM10) to determine baseline concentrations in the ambient air and the factors impacting its distribution such as land use and time of year when levels may be concerning to public health. Measurements of particulates along with meteorological parameters were made at four sites over the heavily populated west coast of Trinidad (10&#17632'N, 61&#17618'W) during March ’15-May ’16, representing rural, urban, mixed background and industrial land uses. The study found mean levels of trace metals to be highest at the industrial and urban stations. Public health exceedances (referenced to the Canadian AAQ public health standards (Ontario-MoE, 2012)) were measured for beryllium, cadmium, chromium, iron, manganese and nickel (in PM10). Iron, manganese and nickel, most associated with particulates at the industrial station, were in frequent exceedance. Beryllium—concentrated in coarse PM (PM2.5-10) with only a single measured exceedance at the mixed background station likely poses minimal threat to the health of the nearby population. Cadmium—concentrated in fine PM which peaked once only at the rural station was likely due to an irregular event within a narrow timeframe during the time of sampling. Iron and manganese were frequently above the Canadian public health threshold, but predominated in the coarse PM fraction, suggesting localised sources. Nickel, concentrated in the fine PM fraction, was frequently in exceedance particularly at the industrial station. Cadmium and nickel are genotoxic and should be regulated in order to reduce the burden of toxic carcinogens to which the population can be exposed.

Highlights

  • Ambient air particulates can act as a medium of transport for a myriad of adsorbed organic and inorganic chemicals, trace metals, microscopic biologicals and viruses from various sources

  • The paper analyzed the concentrations of trace metals in fine and respirable particulates to determine baseline concentrations in the ambient air and the factors impacting its distribution such as land use and time of year when levels may be concerning to public health

  • The concentrations of trace metals measured in this study were analysed to determine baseline concentrations in the ambient air and the factors impacting their distribution e.g. particular land uses, time of year and/or geographical areas where levels pose a threat to public health

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Summary

Introduction

Ambient air particulates can act as a medium of transport for a myriad of adsorbed organic and inorganic chemicals, trace metals, microscopic biologicals and viruses from various sources. In Trinidad and Tobago (T&T), high levels of Al, Fe, and Zn have been found in the coastal and marine sediments off Port-of Spain (Al-39420 μg/g; Fe-45640 μg/g; Zn-245 μg/g), Point Lisas (Al-11936 μg/g; Fe-30171 μg/g; Zn-69 μg/g) and Caroni (Al-0400 μg/g; Fe-19000 μg/g; Zn-32 μg/g) (Mohammed et al, 2011). As air pollution can effectively be controlled at the point of emission (European Commission, 2001), the regulation of the concentration of respirable particulates and contaminants contained in them (e.g. trace metals) is a common feature in the pollution regulation and legislative arsenal of many states and pollution control agencies, including Trinidad and Tobago. The concentrations of trace metals measured in this study were analysed to determine baseline concentrations in the ambient air and the factors impacting their distribution e.g. particular land uses, time of year and/or geographical areas where levels pose a threat to public health. Exceedance levels, are defined as the frequency of sampled trace metals levels in PM10 (measured over hrs) exceeding the local standards (Environmental Management Authority of Trinidad and Tobago, 2014) and/or international guidelines (Ontario-MoE, 2012) identified for protection of public health

Literature Review
Methods and Procedures
Results and Discussion
Statistics
Wind and Precipitation
Public Health Impact
Conclusion
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