Contaminant Elements in Roadside Dust and Soil

A special issue of Environments (ISSN 2076-3298).

Deadline for manuscript submissions: closed (31 July 2020) | Viewed by 6534

Special Issue Editor


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Guest Editor
Bio Forschung Austria, 1220 Vienna, Austria
Interests: trace elements (heavy metals, platinum metals, rare earths); phosphorus; iodine—occurrence and analysis; environmental mobility and speciation
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Special Issue Information

Dear Colleagues,

The intended Special Issue should cover a data compilation of roadside dusts and urban soils. Air quality monitoring often refers to concentrations in m³ of air, but atmospheric deposition data and concentrations in dust are not so often reported. Further, the sampling strategy is of great influence upon the data and their interpretation, whether the mere dust is taken with a brush or a vacuum cleaner, or roadside soil cores are taken.

  1. Origin and sampling

Data can only be compared if the same sampling depth has been used, which is found in the Material and Methods section of the respective paper. Datasets of roadside dust only of 0–2, 0–10, or 0–20 cm exist in the literature, the data of which should not be mixed. Roadside dust gets diluted with the adjacent soil at various amounts. Mapping or at least description of the sampling sites is essential. Various sources of input have been assigned, often from principal component analysis, which is per definition limited to linear dependencies.

  1. Physical properties and minerals

Sealing and compaction impose great changes to hydraulic properties and soil gas transport, which can be monitored by electrical conductivity. Combustion processes cause inputs of magnetic particles. Radioactivity measurements in urban soil are still scarce.

Some minerals are indicative of human settlements, like glasses and bricks.

Physical changes remain for a long time and are indicative for excavations of historic settlement sites.

Because nanoparticles largely act as catalytic surfaces or can more easily enter living cells, information about nanoparticles is also welcome.

  1. Chemical properties

Metal pollution, particularly so-called “heavy metals”, semimetals (e.g., As, Sb), and platinum group metals, have been often the subject of health concerns. Apart from total element contents, mobile soil fractions and adsorption studies have to be considered as well. As most urban green plants are not directly used for human or animal consumption, soil to plant transfer pathways are less important than in agricultural or forest areas.

In addition to metals, nonmetals like P, S, and Cl have to be considered as well.

Contamination levels have been classified by comparison with threshold levels for individuals, and as a combination of several parameters as the geoaccumulation index, the pollution index, and the contamination index.

  1. Input to roadside soils

Atmospheric deposition sources are traffic, combustion processes, and abrasion from buildings, together with long-range transport. Changing technologies in industrial countries have reduced Pb and carbon soot and increased platinum group metals and CeO2 from automotive catalysts. Washout from industrial emissions has been reduced through the purification of flue gases. There is still the input of de-icing salts, ashes and slags, and wastes from building and construction sites.

  1. Output from roadside soils

To achieve optimization of green energy, green plants grown in parks and residential areas can be used as compost if the collection sites have been thoroughly selected for low contaminations. Others have to go to waste incineration.

The run-off from sealed plots enters adjacent urban soils and may be hazardous to urban trees. Urban run-off can be easily detected in stream sediments nearby.

  1. Transformations

The levels of contamination usually decrease from roadside soils and industrial soils to parks, residential soil, and riverside areas, wetlands, and forests nearby.

Fires, floodings, and former industrial sites can be detected by changes of soil composition, as well as historic roads and railways, and fireplaces back to prehistoric times.

Worldwide, increasing population and global warming will necessitate developing remediation strategies for contaminated sites, to increase the areas of agricultural production and recreational forests, which is currently in progress.

Dr. Manfred Sager
Guest Editor

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Published Papers (1 paper)

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65 pages, 795 KiB  
Review
Urban Soils and Road Dust—Civilization Effects and Metal Pollution—A Review
by Manfred Sager
Environments 2020, 7(11), 98; https://doi.org/10.3390/environments7110098 - 04 Nov 2020
Cited by 30 | Viewed by 6066
Abstract
Urban soils have been changed much by human impacts in terms of structure, composition and use. This review paper gives a general introduction into changes from compaction, mixing, water retention, nutrient inputs, sealing, gardening, and pollution. Because pollutions in particular have caused concerns [...] Read more.
Urban soils have been changed much by human impacts in terms of structure, composition and use. This review paper gives a general introduction into changes from compaction, mixing, water retention, nutrient inputs, sealing, gardening, and pollution. Because pollutions in particular have caused concerns in the past, metal pollutions and platinum group metal inputs have been treated in more detail. Though it is not possible to cover the entire literature done on this field, it has been tried to give examples from all continents, regarding geochemical background levels. Urban metal soil pollution depends on the age of the settlement, current emissions from traffic and industry, and washout. It seems that in regions of high precipitation, pollutants are swept away to the watershed, leaving the soils less polluted than in Europe. Health hazards, however, are caused by ingestion and inhalation, which are higher in 3rd world countries, and not by concentrations met in urban soils as such; these are not treated within this paper in detail. With respect to pollutants, this paper is focused on metals. Contrary to many reviews of the past, which mix all data into one column, like sampling depth, sieved grain sizes, digestion and determination methods, these have been considered, because this might lead to considerable interpretation changes. Because many datasets are not Gaussian distributed, medians and concentration ranges are given, wherever possible. Urban dust contains about two to three fold the hazardous metal concentrations met in urban soils. Some data about metal mobilities obtained from selective and sequential leaching procedures, are also added. Soil compaction, pollution, sealings and run-offs cause stress situations for green plants growing at roadside locations, which is discussed in the Section 5. Environmental protection measures have led to decrease metal pollutions within the last decade in many places. Full article
(This article belongs to the Special Issue Contaminant Elements in Roadside Dust and Soil)
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