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http://hdl.handle.net/20.500.12188/15959
DC Field | Value | Language |
---|---|---|
dc.contributor.author | Harmens, H | en_US |
dc.contributor.author | Norris, D A | en_US |
dc.contributor.author | Sharps, K | en_US |
dc.contributor.author | Mills, G | en_US |
dc.contributor.author | Alber, R | en_US |
dc.contributor.author | Aleksiayenak, Y | en_US |
dc.contributor.author | Blum, O | en_US |
dc.contributor.author | Cucu-Man, S-M | en_US |
dc.contributor.author | Dam, M | en_US |
dc.contributor.author | De Temmerman, L | en_US |
dc.contributor.author | Ene, A | en_US |
dc.contributor.author | Fernández, J A | en_US |
dc.contributor.author | Martinez-Abaigar, J | en_US |
dc.contributor.author | Frontasyeva, M | en_US |
dc.contributor.author | Godzik, B | en_US |
dc.contributor.author | Jeran, Z | en_US |
dc.contributor.author | Lazo, P | en_US |
dc.contributor.author | Leblond, S | en_US |
dc.contributor.author | Liiv, S | en_US |
dc.contributor.author | Magnússon, S H | en_US |
dc.contributor.author | Maňkovská, B | en_US |
dc.contributor.author | Karlsson, G Pihl | en_US |
dc.contributor.author | Piispanen, J | en_US |
dc.contributor.author | Poikolainen, J | en_US |
dc.contributor.author | Santamaria, J M | en_US |
dc.contributor.author | Skudnik, M | en_US |
dc.contributor.author | Spiric, Z | en_US |
dc.contributor.author | Stafilov, T | en_US |
dc.contributor.author | Steinnes, E | en_US |
dc.contributor.author | Stihi, C | en_US |
dc.contributor.author | Suchara, I | en_US |
dc.contributor.author | Thöni, L | en_US |
dc.contributor.author | Todoran, R | en_US |
dc.contributor.author | Yurukova, L | en_US |
dc.contributor.author | Zechmeister, H G | en_US |
dc.date.accessioned | 2021-12-30T08:27:31Z | - |
dc.date.available | 2021-12-30T08:27:31Z | - |
dc.date.issued | 2015-05 | - |
dc.identifier.uri | http://hdl.handle.net/20.500.12188/15959 | - |
dc.description.abstract | In recent decades, naturally growing mosses have been used successfully as biomonitors of atmospheric deposition of heavy metals and nitrogen. Since 1990, the European moss survey has been repeated at five-yearly intervals. In 2010, the lowest concentrations of metals and nitrogen in mosses were generally found in northern Europe, whereas the highest concentrations were observed in (south-)eastern Europe for metals and the central belt for nitrogen. Averaged across Europe, since 1990, the median concentration in mosses has declined the most for lead (77%), followed by vanadium (55%), cadmium (51%), chromium (43%), zinc (34%), nickel (33%), iron (27%), arsenic (21%, since 1995), mercury (14%, since 1995) and copper (11%). Between 2005 and 2010, the decline ranged from 6% for copper to 36% for lead; for nitrogen the decline was 5%. Despite the Europe-wide decline, no changes or increases have been observed between 2005 and 2010 in some (regions of) countries. | en_US |
dc.language.iso | en | en_US |
dc.relation.ispartof | Environmental pollution (Barking, Essex : 1987) | en_US |
dc.title | Heavy metal and nitrogen concentrations in mosses are declining across Europe whilst some "hotspots" remain in 2010 | en_US |
dc.identifier.doi | 10.1016/j.envpol.2015.01.036 | - |
dc.identifier.volume | 200 | - |
item.grantfulltext | none | - |
item.fulltext | No Fulltext | - |
Appears in Collections: | Faculty of Natural Sciences and Mathematics: Journal Articles |
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