dc.contributor.author | Massas, I | en |
dc.contributor.author | Ehaliotis, C | en |
dc.contributor.author | Kalivas, D | en |
dc.contributor.author | Panagopoulou, G | en |
dc.date.accessioned | 2014-06-06T06:50:08Z | |
dc.date.available | 2014-06-06T06:50:08Z | |
dc.date.issued | 2010 | en |
dc.identifier.issn | 00496979 | en |
dc.identifier.uri | http://dx.doi.org/10.1007/s11270-009-0321-4 | en |
dc.identifier.uri | http://62.217.125.90/xmlui/handle/123456789/4973 | |
dc.subject | Enrichment factor | en |
dc.subject | Heavy metals | en |
dc.subject | Metal availability | en |
dc.subject | Metal pollution | en |
dc.subject | Playgrounds | en |
dc.subject | Urban soils | en |
dc.subject.other | Aqua regia | en |
dc.subject.other | Bioavailable fraction | en |
dc.subject.other | Enrichment factors | en |
dc.subject.other | GIS software | en |
dc.subject.other | Mean values | en |
dc.subject.other | Metal concentrations | en |
dc.subject.other | Metal pollution | en |
dc.subject.other | Playgrounds | en |
dc.subject.other | Site-specific | en |
dc.subject.other | Spatial distribution | en |
dc.subject.other | Surface soil | en |
dc.subject.other | Urban soils | en |
dc.subject.other | Young children | en |
dc.subject.other | Acids | en |
dc.subject.other | Chromium | en |
dc.subject.other | Concentration (process) | en |
dc.subject.other | Copper | en |
dc.subject.other | Lead | en |
dc.subject.other | Manganese | en |
dc.subject.other | Manganese compounds | en |
dc.subject.other | Metals | en |
dc.subject.other | Soils | en |
dc.subject.other | Soil pollution | en |
dc.subject.other | chromium | en |
dc.subject.other | cobalt | en |
dc.subject.other | copper | en |
dc.subject.other | heavy metal | en |
dc.subject.other | iron | en |
dc.subject.other | lead | en |
dc.subject.other | manganese | en |
dc.subject.other | nickel | en |
dc.subject.other | pentetic acid | en |
dc.subject.other | zinc | en |
dc.subject.other | bioavailability | en |
dc.subject.other | heavy metal | en |
dc.subject.other | soil pollution | en |
dc.subject.other | urban area | en |
dc.subject.other | urban pollution | en |
dc.subject.other | article | en |
dc.subject.other | chemical analysis | en |
dc.subject.other | city | en |
dc.subject.other | concentration (parameters) | en |
dc.subject.other | controlled study | en |
dc.subject.other | data analysis software | en |
dc.subject.other | Greece | en |
dc.subject.other | metal extraction | en |
dc.subject.other | play | en |
dc.subject.other | pollution monitoring | en |
dc.subject.other | quantitative analysis | en |
dc.subject.other | soil analysis | en |
dc.subject.other | soil pollution | en |
dc.subject.other | soil pollution indicator | en |
dc.subject.other | Athens [Attica] | en |
dc.subject.other | Attica | en |
dc.subject.other | Greece | en |
dc.title | Concentrations and availability indicators of soil heavy metals; The case of children's playgrounds in the city of Athens (Greece) | en |
heal.type | journalArticle | en |
heal.identifier.primary | 10.1007/s11270-009-0321-4 | en |
heal.publicationDate | 2010 | en |
heal.abstract | This study reports on the concentrations, distribution, and availability of heavy metals in the children's playground soils of Athens. Playgrounds were chosen because they are open city areas; they show relatively even spatial distribution within the district of Athens and are used by a great number of young children and their escorts on a regular basis. Samples were collected from 70 playground surface soils, representing more than 70% of the city's playgrounds. Cu, Zn, Pb, Cr, Ni, Co, Mn, and Fe were extracted by aqua regia and by diethylene triamine pentaacetic acid (DTPA) to estimate total and available metal forms, respectively. Their mean total concentrations were 43, 174, 110, 80, 82, 22, 312, and 17×103mg kg-1, respectively. The DTPA-extracted fraction showed much lower values, with means of 2.5, 7.8, 5.8, 1.5, 1.3, 0.4, 8.4, and 2.0 mg kg-1 respectively, which, however, should be carefully monitored since they relate directly to the bioavailable fraction of heavy metals. Though mean values of metal concentrations are not particularly high, the calculated enrichment factors indicate site-specific cases of high enrichment with heavy metals. Considering that the bioavailable fraction of a metal is possibly a more appropriate indicator for the recent soil pollution history, availability ratios were calculated and their distribution was visualized over the entire city profile using the appropriate GIS software. It was shown that recent metal pollution events appear to have affected mostly playground sites in the southern and eastern part of the municipality. © 2010 Springer Science+Business Media B.V. | en |
heal.journalName | Water, Air, and Soil Pollution | en |
dc.identifier.issue | 1-4 | en |
dc.identifier.volume | 212 | en |
dc.identifier.doi | 10.1007/s11270-009-0321-4 | en |
dc.identifier.spage | 51 | en |
dc.identifier.epage | 63 | en |
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