Elsevier

Science of The Total Environment

Volume 553, 15 May 2016, Pages 636-642
Science of The Total Environment

Heavy metal accumulation related to population density in road dust samples taken from urban sites under different land uses

https://doi.org/10.1016/j.scitotenv.2016.02.101Get rights and content

Highlights

  • Road dust increased along with city growth and its dynamics.

  • The commercial sector showed the highest concentrations of heavy metals.

  • The presence of Zn, Pb and Cu in the three sectors is noteworthy.

  • Road dust might cause a number of negative environmental impacts.

Abstract

Soil pollution is a key component of the land degradation process, but little is known about the impact of soil pollution on human health in the urban environment. The heavy metals Pb, Zn, Cu, Cr, Cd and Ni were analyzed by acid digestion (method EPA 3050B) and a total of 15 dust samples were collected from streets of three sectors of the city with different land uses; commercial, residential and a highway. The purpose was to measure the concentrations of heavy metals in road sediment samples taken from urban sites under different land uses, and to assess pollution through pollution indices, namely the ecological risk index and geoaccumulation index. Heavy metals concentrations (mg/kg) followed the following sequences for each sector: commercial sector Pb (1289.4) > Cu (490.2) > Zn (387.6) > Cr (60.2) > Ni (54.3); highway Zn (133.3) > Cu (126.3) > Pb (87.5) > Cr (9.4) > Ni (5.3); residential sector Zn (108.3) > Pb (26.0) > Cu (23.7) > Cr (7.3) > Ni (7.2). The geoaccumulation index indicated that the commercial sector was moderately to strongly polluted while the other sectors fell into the unpolluted category. Similarly, using the ecological risk index the commercial sector fell into the considerable category while the other sectors classified as low risk. Road dust increased along with city growth and its dynamics, additionally, road dust might cause a number of negative environmental impacts, therefore the monitoring this dust is crucial.

Introduction

Land degradation is a worldwide process affecting the Earth system due to human use and abuse of natural resources (Brevik et al., 2015, Ibáñez et al., 2015). Degradation of soils has been accelerated due to the growth of urban populations and has resulted in soil sealing, changes in albedo, in the hydrological cycle and reduced or eliminated the ecosystem services and natural resources that humankind receives from soils (Feller et al., 2015, Zornoza et al., 2015).

Road dusts accumulated in urban zones contain a diversity of materials that ranges from mineral compounds to organic and inorganic materials of anthropogenic origin that may deposit on the impermeable surfaces of cities such as roads and roofs (Shi et al., 2010). This is one part of creating the environmental problems that are triggered by the development of cities and roads, others include the increase of water and soil losses due to sealing of soils (Cerdà, 2007, Cheng et al., 2015, Seutloali and Beckedahl, 2015), and the development of increased connectivity of sediments and water (Baartman et al., 2013, Bochet, 2015, Marchamalo et al., 2015).

The heavy metal content of surface soil and street dust are good indicators of environmental accumulation of heavy metals as they act as sinks of the pollutants (Sezgin et al., 2004). Davis and Birch (2010) estimate that in urbanized basins roads may constitute 22% of the area and contribute 26% of the runoff. In our opinion even this is a conservative number, because on roads the rainfall runoff coefficient would be close to 100%. While an unsealed soil would have a rainfall runoff coefficient of about 1–30% (Okoński, 2007) when under natural forest; it can be to up to 80% when soils are heavily compacted or badland areas have developed (Cerdà, 1999). Road and road embankments can generate high to very high runoff volumes (Pereira et al., 2015).

Sartor et al. (1974) determined that the pollutant load in storm runoff from urban areas is significantly higher than in rural runoff. This, in combination with the observation that roads provide a large amount of storm runoff in urban areas, indicates that most of the pollution in urban water sources and adjacent soils may be related to road input (Vaze and Chiew, 2002). Rissler et al. (2012) found that the main pollutants associated with urbanized basins are copper (Cu), lead (Pb) and zinc (Zn); together with these nickel (Ni), cadmium (Cd) and chromium (Cr) can also be found, which come from industrial activities (García-Martínez and Poleto, 2014). Most heavy metals are poorly soluble, and therefore are transported through the catchment bonded to sediment particles (Loganathan et al., 2013, Morgan, 2013). Therefore, our level of understanding of the fate of the sediment associated pollutants in a catchment is highly dependent on the how well we understand the transport processes of sediment in these catchments (Rossi et al., 2013). Practices like use of vegetation buffers, storage dams, and establishment of riparian vegetation along small streams within catchments are elements that impact the cascade of sediment and can partition the amount sediment with its associated pollutants (Keesstra et al., 2012, Keesstra et al., 2014, Mekonnen et al., 2015a). Sediment transport in urban catchments is highly complex and difficult to measure and predict with modelling because of non-linear processes and bypassing of the natural system with drainage and sewer pipes (Fletcher et al., 2013, Franz et al., 2014).

Urban sediment accumulated on roads is a sink of pollutants from cities, such as heavy metals, where contact and ingestion of particles derived from these might represent serious issues for human health (Brevik, 2009, Zheng et al., 2010, Acosta et al., 2014, Brevik and Sauer, 2015). Pollutants affect human health in many ways; one of them is the production of quality food in the area surrounding cities as well as within cities (Roy and McDonald, 2015, Beniston et al., 2015, Brevik et al., 2016).

Based on the above, surveillance of roads that show high traffic flow and that are also in industrial areas should be a primary task for public health and risk management programs (Nazzal et al., 2014, Neff et al., 2013), as remediation of health hazards and preventing exposure to health risks are major goals of public health officials (Neff et al., 2013). Common sources of metal contaminants like Pb, Cu, Cd and Zn include the use of gasoline type fuels, tire and brake pad wear, oils, lubricants, and grease (Christoforidis and Stamatis, 2009); while Cr and Ni come from the wear of metallic parts and chrome accessories (Al-Shayep and Seaward, 2001). Road sweeping and cleaning systems have been implemented in several cities around the world to mitigate the effects of rainwater runoff on urban water systems (Brinkmann and Tobin, 2001, Tobin and Brinkmann, 2002). Road cleaning is a suitable mechanism for the management of urban pollutants. According to Calvillo et al. (2015), little research has been done on the comparison of quantitative data about the efficacy of various road sediment cleaning and sweeping methods.

There is a lack of data for this region, and in general metals data and funding to conduct such work in developing countries is not abundant. Keeping in mind that new data for regions that are data deficient provides new knowledge and carries with it a certain level of uniqueness, the main goals of this study were to 1) assess the levels of select heavy metals: Cu, Pb, Ni, Zn and Cr, in dust taken from urban sites with different land uses 2) investigate the differences between geochemical background values and metal levels, and 3) calculate pollution indices to assess the level of pollution as a tool for urban sanitation decision-making.

Section snippets

Study area

The study took place in the urban area of the city of Villavicencio, located in mid-eastern Colombia (Fig. 1). Its coordinates are 4°15′48″N – 73°65′49″W, its annual average temperature is 25.6 °C, annual average rainfall is 3700 mm, and mean elevation is 467 m.a.s.l. Villavicencio is one of the cities with the highest urban growth rate over the last decade in the country, with an estimated population in 2014 of 473,718 inhabitants (DANE, 2010). The of population growth rate in the city of

Metal concentrations

Heavy metal concentrations and summary statistics for the studied sectors are shown in Table 3. It has been pointed out that road dust resuspension contributes significantly to heavy metal concentration levels in urban areas (Karanasiou et al., 2009, Athanasopoulou et al., 2010). The commercial sector showed the highest concentrations of all the heavy metals sampled during this research. Based on the concentration of metals in each sector, they can be classified as follows; commercial sector ˃ 

Conclusions

Road dusts are a problem that increases with the growth and the dynamics of cities, and may account for many environmental impacts. In the city of Villavicencio, Colombia, it was found that the highest concentrations of heavy metals were in the commercial sector where “rudimentary” auto-repair activities take place and little regulation regarding waste management is implemented. Heavy metal road dust content in these areas exceeded background values of heavy metals. According to the

Acknowledgements

The authors wish to acknowledge the financial support given by Ecopetrol SA, by the alliance with Universidad de los Llanos, N° 5211592, “Proyecto Cuencas”, and to the staff of the Instituto de Ciencias Ambientales de la Orinoquia Colombiana-ICAOC (Universidad de los Llanos).

References (76)

  • N. Guvenç et al.

    Investigation of soil multi-element composition in Antalya, Turkey

    Environ. Int.

    (2003)
  • L. Hakanson

    An ecological risk index for aquatic pollution control. A sedimentological approach

    Water Res.

    (1980)
  • L. Han et al.

    Characteristics of re-suspended road dust and its impact on the atmospheric environment in Beijing

    Atmos. Environ.

    (2007)
  • A.A. Karanasiou et al.

    Assessment of source apportionment by positive matrix factorization analysis on fine and coarse urban aerosol size fractions

    Atmos. Environ.

    (2009)
  • S.D. Keesstra et al.

    Soil as a filter for groundwater quality

    Curr. Opin. Environ. Sustain.

    (2012)
  • S. Keesstra et al.

    Evaluating the hydrological component of the new catchment-scale sediment delivery model LAPSUS-D

    Geomorphology

    (2014)
  • D. McCarthy et al.

    Intra-event variability of Escherichia coli and total suspended solids in urban stormwater runoff

    Water Res.

    (2012)
  • J. Rissler et al.

    Experimental determination of deposition of diesel exhaust particles in the human respiratory tract

    J. Aerosol Sci.

    (2012)
  • L. Rossi et al.

    Sediment contamination assessment in urban areas based on total suspended solids

    Water Res.

    (2013)
  • M. Saeedi et al.

    Heavy metals and polycyclic aromatic hydrocarbons: pollution and ecological risk assessment in street dust of Tehran

    J. Hazard. Mater.

    (2012)
  • N. Sezgin et al.

    Determination of heavy metal concentration in street dust in Istambul E-5 highway

    Environ. Int.

    (2004)
  • G. Shi et al.

    Comprehensive assessment of toxic metals in urban and suburban street deposited sediments (SDSs) in the biggest metropolitan area of China

    Environ. Pollut.

    (2010)
  • J. Vaze et al.

    Experimental study of pollutant accumulation on an urban road surface

    Urban Water

    (2002)
  • B. Wei et al.

    A review of heavy metal contaminations in urban soils, urban road dusts and agricultural soils from China

    Microchem. J.

    (2010)
  • N. Zheng et al.

    Health risk assessment of heavy metal exposure to street dust in the zinc smelting district, Northeast of China

    Sci. Total Environ.

    (2010)
  • S.M. Al-Shayep et al.

    Heavy metal content of roadside soils along ring road in Riyadh (Saudi Arabia)

    Asian J. Chem.

    (2001)
  • E. Athanasopoulou et al.

    Implementation of road and soil dust emission parameterizations in the aerosol model CAMx: applications over the greater Athens urban area affected by natural sources

    J. Geophys. Res.

    (2010)
  • M.S. Atiemo et al.

    Contamination assessment of heavy metals in road dust from selected roads in Accra, Ghana

    Res. J. Environ. Earth Sci.

    (2011)
  • J.E.M. Baartman et al.

    Linking landscape morphological complexity and sediment connectivity

    Earth Surf. Process. Landf.

    (2013)
  • J.W. Beniston et al.

    Assessing and managing soil quality for urban agriculture in a degraded vacant lot soil

    Land Degrad. Dev.

    (2015)
  • E. Bochet

    The fate of seeds in the soil: a review of the influence of overland flow on seed removal and its consequences for the vegetation of arid and semiarid patchy ecosystems

    Soil

    (2015)
  • N.B. Bonumá et al.

    Simulating landscape sediment transport capacity by using a modified SWAT model

    J. Environ. Qual.

    (2014)
  • E.C. Brevik

    Soil, food security, and human health

  • E.C. Brevik et al.

    The past, present, and future of soils and human health studies

    SOIL

    (2015)
  • E.C. Brevik et al.

    The interdisciplinary nature of SOIL

    Soil

    (2015)
  • R. Brinkmann et al.

    Clean streets—Clean waterways: street sweeping, storm water, and pollution reduction

  • S.J. Calvillo et al.

    Street dust: implications for stormwater and air quality, and environmental management through street sweeping

  • A. Cerdà

    Seasonal and spatial variations in infiltration rates in badland surfaces under Mediterranean climatic conditions

    Water Resour. Res.

    (1999)
  • Cited by (290)

    View all citing articles on Scopus
    View full text