Urban soil is generally contaminated to a variable degree depending on its proximity to contamination sources. Traffic is one of the main sources of urban contamination; lead (Pb) from the use of leaded petrol, zinc (Zn) and cadmium (Cd) from tyre wear, antimony (Sb) from break pads, and the platinum group elements (PGEs) from the wear of catalytic converters, are some typical elements that often reach high concentrations in the urban environment. Lead was also a key ingredient in white paint, and in towns with a high proportion of white wooden houses very high concentrations were found in soil. Crematoria can or have emitted mercury (Hg). Coal and heavy oil fired municipal power and heating stations emit sulphur (S), silver (Ag), vanadium (V), bromine (Br) and barium (Ba). The use of impregnated wood may have resulted in high concentrations of arsenic (As), especially in kindergartens (nursery schools) and playgrounds. Building materials (plaster and paint) may also contain high concentrations of organic contaminants, especially polychlorinated biphenyls (PCBs), which again end up in urban soil. Coal and wood burning, the use of diesel fuel, and the production of coke, all lead to the emission of polycyclic aromatic hydrocarbons (PAHs). There exist countless other sources of local contamination in towns, and there is thus every reason to be concerned about the quality of the urban environment, and the suitability of soil for sensitive land uses, such as schools, playgrounds, parks and vegetable gardens. Contaminated urban soil may contaminate indoor dust and, therefore, to an increased human exposure to toxic chemicals. Consequently, the distribution of toxic contaminants in urban soil needs to be documented and known by city administration to avoid costly mistakes in land use planning, and further spreading of highly contaminated materials. The EuroGeoSurveys ‘Geochemistry’ Expert Group during the compilation of a proposal to the Directors for a European wide urban geochemistry project, using a harmonised sampling and analytical methodology, it discovered that many urban geochemical studies have been performed in Europe by National Geological Surveys, which are not known to the wider geoscientific community. Since, the results of these studies are directly related to our quality of life, the EuroGeoSurveys ‘Geo chemistry’ Expert Group decided to publish at least one case study from each country in a book,which will be available in the second half of 2010. A concise description of some of these studies will be given in this paper.

URBAN GEOCHEMICAL STUDIES IN EUROPE

DINELLI, ENRICO;
2010

Abstract

Urban soil is generally contaminated to a variable degree depending on its proximity to contamination sources. Traffic is one of the main sources of urban contamination; lead (Pb) from the use of leaded petrol, zinc (Zn) and cadmium (Cd) from tyre wear, antimony (Sb) from break pads, and the platinum group elements (PGEs) from the wear of catalytic converters, are some typical elements that often reach high concentrations in the urban environment. Lead was also a key ingredient in white paint, and in towns with a high proportion of white wooden houses very high concentrations were found in soil. Crematoria can or have emitted mercury (Hg). Coal and heavy oil fired municipal power and heating stations emit sulphur (S), silver (Ag), vanadium (V), bromine (Br) and barium (Ba). The use of impregnated wood may have resulted in high concentrations of arsenic (As), especially in kindergartens (nursery schools) and playgrounds. Building materials (plaster and paint) may also contain high concentrations of organic contaminants, especially polychlorinated biphenyls (PCBs), which again end up in urban soil. Coal and wood burning, the use of diesel fuel, and the production of coke, all lead to the emission of polycyclic aromatic hydrocarbons (PAHs). There exist countless other sources of local contamination in towns, and there is thus every reason to be concerned about the quality of the urban environment, and the suitability of soil for sensitive land uses, such as schools, playgrounds, parks and vegetable gardens. Contaminated urban soil may contaminate indoor dust and, therefore, to an increased human exposure to toxic chemicals. Consequently, the distribution of toxic contaminants in urban soil needs to be documented and known by city administration to avoid costly mistakes in land use planning, and further spreading of highly contaminated materials. The EuroGeoSurveys ‘Geochemistry’ Expert Group during the compilation of a proposal to the Directors for a European wide urban geochemistry project, using a harmonised sampling and analytical methodology, it discovered that many urban geochemical studies have been performed in Europe by National Geological Surveys, which are not known to the wider geoscientific community. Since, the results of these studies are directly related to our quality of life, the EuroGeoSurveys ‘Geo chemistry’ Expert Group decided to publish at least one case study from each country in a book,which will be available in the second half of 2010. A concise description of some of these studies will be given in this paper.
2010
Demetriades A., Birke M., Locutura J., Bel-lan A.B., Duris M. and EuroGeoSurveys Geochemistry Expert Group. members of the EuroGeoSurveys Geochemistry Expert Group, Austria: Albert Schedl, Heinz Reitner, Edith Haslinger, Peter Filzmoser; Belgium: Walter De Vos; Bosnia & Herzegovina: Hazim Hrvatovic; Neven Miosic, Ferid Skopljak, Natalija Samardzic; Bulgaria: Valeri Trendavilov; Croatia: Josip Halamić, Ajka Šorša, Stjepan Husnjak; Czech Republic: Miloslav Duris; Cyprus: Zomenia Zomeni; Denmark: Vibeke Ernstsen; Estonia: Jaan Kivisilla, Walter Petersell; Finland: Timo Tarvainen, Mikael Eklund; France: Ignace Salpeteur; F.Y.R.O.M.: Trajce Stafilov; Germany: Manfred Birke, Rainer Hoffmann, Jens Utermann; Hellas: Alecos Demetriades; Hungary: Gyozo Jordan, Ubul Fugedi, Laszlo Kuti; Ireland: Patrick O’Connor, Fionnuala Ni Mhairtin, Vincent Gallagher; Italy: Benedetto De Vivo, Annamaria Lima, Stefano Albanese, Enrico Dinelli, Domenico Cicchella, Paolo Valera; Latvia: Aivars Gilucis; Lithuania: Virgilija Gregorauskiene; Luxembourg: Robert Maquil; Netherlands, The: Gerben Mol; Norway: Clemens Reimann, Rolf Tore Ottesen, Tore Volden, Ola A. Eggen, Arnold Arnoldussen; Poland: Anna Pasieczna, Aleksandra Dusza, Paweł Kwecko; Portugal: Maria Joao Batista, Cátia Prazeres; Serbia: Aleksandra Gulan, Dragana Vidojević; Slovakia: Igor Slaninka, Peter Sefcik, Daniela Mackovych, Silvester Pramuka; Slovenia: Mateja Gosar; Spain: Juan Locutura, Alejandro Bel-lan; Sweden: Madelen Andersson, Kaj Lax; Switzerland: Peter Hayoz, Reto Giulio Meuli; Ukraine: Boris I. Malyuk, Volodymyr Klos; United Kingdom: Dee Flight, Andreas Scheib, Mick Strutt, Paul McDonnell.
File in questo prodotto:
Eventuali allegati, non sono esposti

I documenti in IRIS sono protetti da copyright e tutti i diritti sono riservati, salvo diversa indicazione.

Utilizza questo identificativo per citare o creare un link a questo documento: https://hdl.handle.net/11585/142648
 Attenzione

Attenzione! I dati visualizzati non sono stati sottoposti a validazione da parte dell'ateneo

Citazioni
  • ???jsp.display-item.citation.pmc??? ND
  • Scopus ND
  • ???jsp.display-item.citation.isi??? ND
social impact