Levels and spatial and temporal trends of contaminants in Greenland biota: an updated review

被引:89
作者
Riget, F
Dietz, R
Vorkamp, K
Johansen, P
Muir, D
机构
[1] Natl Environm Res Inst, DK-4000 Roskilde, Denmark
[2] Natl Water Res Inst Branch, Burlington, ON L7R 4A6, Canada
关键词
organochlorines; heavy metals; spatial and temporal trends; biota; Greenland;
D O I
10.1016/j.scitotenv.2004.03.022
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Knowledge of contaminant levels in Greenland biota has increased substantially in recent years, particularly for persistent organic pollutants. This paper reviews and updates knowledge of spatial and temporal trends of Cd, Hg and organochlorines (PCBs, DDTs, HCHs, HCB and chlordane-related compounds) in Greenland terrestrial, freshwater and marine biota. The most comprehensive studies of spatial trends of Cd and Hg in the terrestrial ecosystem concern lichens, with relatively complete coverage, and caribou (Rangifer tarandus), with coverage mainly in different regions of central West Greenland and Southwest Greenland. The Arctic char (Salvelinus alpinus) is the only freshwater organism for which studies of spatial trends of Hg levels have been completed. Information on spatial trends of Cd and Hg in the marine environment is available from studies of fish, seabirds, ringed seals (Phoca hispida) and polar bears (Ursus maritimus). Geographical patterns of Cd and Hg in Greenland biota were not always consistent among different species or different studies. In landlocked Arctic char the concentrations of Hg decreased from south to north. In marine animals levels of Hg tended to be higher in East Greenland than in West Greenland and Cd levels were highest in biota from Disko Island in central West Greenland. The observed regional differences are difficult to explain but in most cases the causes appear to be natural rather than anthropogenic. Only a few time series covering the last 20 years exist for Cd and Hg. The one time series indicating a temporal change is for ringed seals in Northwest Greenland, which shows an increasing trend of Hg and a decreasing trend of Cd since 1984. Whether the changes reflect anthropogenic inputs, seal behaviour or other environmental factors is unknown. The most significant new insights have concerned organochlorines. In general, levels of these compounds were very low in terrestrial biota compared to marine species. Concentrations in landlocked Arctic char were highest in Southeast Greenland and lowest in Northwest and Northeast Greenland. Marine species from East Greenland had consistently higher levels of IPCB, IDDT and SigmaHCH than marine species from West Greenland. Very few data exist to evaluate temporal changes of organochlorine levels in Greenland biota, and this is the most significant knowledge gap at present. The most pronounced change observed was a decrease of 78% in SigmaPCB levels in polar bears from East Greenland from 1990 to 2000. Levels of SigmaHCH in shorthorn sculpins (Myoxocephalus scorpius) and seals from both central West Greenland and central East Greenland appear to have decreased since 1994. Increasing trends of SigmaDDT from 1994 until now were found in both sexes of seals as well as in male sculpins from central West Greenland. (C) 2004 Elsevier B.V. All rights reserved.
引用
收藏
页码:29 / 52
页数:24
相关论文
共 50 条
[31]   Temporal trends of organochlorine contaminants in burbot and lake trout from three selected Yukon lakes [J].
Ryan, MJ ;
Stern, GA ;
Diamond, M ;
Croft, MV ;
Roach, P ;
Kidd, K .
SCIENCE OF THE TOTAL ENVIRONMENT, 2005, 351 :501-522
[32]   Temporal and spatial variabilities in surface mass balance at the EGRIP site, Greenland from 2009 to 2017 [J].
Komuro, Yuki ;
Nakazawa, Fumio ;
Hirabayashi, Motohiro ;
Goto-Azuma, Kumiko ;
Nagatsuka, Naoko ;
Shigeyama, Wataru ;
Matoba, Sumito ;
Homma, Tomoyuki ;
Steffensen, Jorgen Peder ;
Dahl-Jensen, Dorthe .
POLAR SCIENCE, 2021, 27
[33]   Monitoring temporal and spatial trends of legacy and emerging contaminants in marine environment: Results from the environmental specimen bank (es-BANK) of Ehime University, Japan [J].
Tanabe, Shinsuke ;
Ramu, Karri .
MARINE POLLUTION BULLETIN, 2012, 64 (07) :1459-1474
[34]   Chemically modified clay for adsorption of contaminants: trends, advantages and limitations - a concise review [J].
Alomari, Asma Dhahawi Ahmad .
INTERNATIONAL JOURNAL OF ENVIRONMENTAL ANALYTICAL CHEMISTRY, 2024,
[35]   Temporal Trends of Hexabromocyclododecane, Polybrominated Diphenyl Ethers and Polychlorinated Biphenyls in Ringed Seals from East Greenland [J].
Vorkamp, Katrin ;
Riget, Frank F. ;
Bossi, Rossana ;
Dietz, Rune .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 2011, 45 (04) :1243-1249
[36]   Temporal trends and variability in a high-arctic ecosystem in Greenland: multidimensional analyses of limnic and terrestrial ecosystems [J].
Lars O. Mortensen ;
Erik Jeppesen ;
Niels Martin Schmidt ;
Kirsten S. Christoffersen ;
Mikkel P. Tamstorf ;
Mads C. Forchhammer .
Polar Biology, 2014, 37 :1073-1082
[37]   Temporal trends and variability in a high-arctic ecosystem in Greenland: multidimensional analyses of limnic and terrestrial ecosystems [J].
Mortensen, Lars O. ;
Jeppesen, Erik ;
Schmidt, Niels Martin ;
Christoffersen, Kirsten S. ;
Tamstorf, Mikkel P. ;
Forchhammer, Mads C. .
POLAR BIOLOGY, 2014, 37 (08) :1073-1082
[38]   Heavy metals in northern Chilean rivers: Spatial variation and temporal trends [J].
Pizarro, Jaime ;
Vergara, Pablo M. ;
Rodriguez, Jose A. ;
Valenzuela, Alejandra M. .
JOURNAL OF HAZARDOUS MATERIALS, 2010, 181 (1-3) :747-754
[39]   Fish contamination in Lake Erie: An examination of temporal trends of organochlorine contaminants and a Bayesian approach to consumption advisories [J].
Mahmood, Maryam ;
Bhavsar, Satyendra P. ;
Arhonditsis, George B. .
ECOLOGICAL INFORMATICS, 2013, 18 :131-148
[40]   Status of Organochlorine Contaminants in the Different Environmental Compartments of Pakistan: A Review on Occurrence and Levels [J].
Eqani, Syed Ali-Musstjab-Akber-Shah ;
Malik, Riffat Naseem ;
Alamdar, Ambreen ;
Faheem, Hina .
BULLETIN OF ENVIRONMENTAL CONTAMINATION AND TOXICOLOGY, 2012, 88 (03) :303-310