Atmospheric concentrations of organic pollutants in the Arctic between 1993-2006


Autoria(s): Hung, Hayley; Kallenborn, Roland; Breivik, Knut; Su, Yushan; Brorström-Lundén, Eva; Olafsdottir, Kristin; Thorlacius, Johanna M; Leppänen, Sirkka; Bossi, Rossana; Skov, Henrik; Manø, Stein; Patton, Gregory W; Stern, Gary A; Sverko, Ed; Fellin, Phil
Cobertura

MEDIAN LATITUDE: 72.043022 * MEDIAN LONGITUDE: -35.404999 * SOUTH-BOUND LATITUDE: 60.333330 * WEST-BOUND LONGITUDE: -159.666666 * NORTH-BOUND LATITUDE: 82.500000 * EAST-BOUND LONGITUDE: 124.500000 * DATE/TIME START: 1993-01-01T00:00:00 * DATE/TIME END: 2006-01-01T00:00:00

Data(s)

01/08/2010

Resumo

Continuous and comparable atmospheric monitoring programs to study the transport and occurrence of persistent organic pollutants (POPs) in the atmosphere of remote regions is essential to better understand the global movement of these chemicals and to evaluate the effectiveness of international control measures. Key results from four main Arctic research stations, Alert (Canada), Pallas (Finland), Storhofdi (Iceland) and Zeppelin (Svalbard/Norway), where long-term monitoring have been carried out since the early 1990s, are summarized. We have also included a discussion of main results from various Arctic satellite stations in Canada, Russia, US (Alaska) and Greenland which have been operational for shorter time periods. Using the Digital Filtration temporal trend development technique, it was found that while some POPs showed more or less consistent declines during the 1990s, this reduction is less apparent in recent years at some sites. In contrast, polybrominated diphenyl ethers (PBDEs) were still found to be increasing by 2005 at Alert with doubling times of 3.5 years in the case of deca-BDE. Levels and patterns of most POPs in Arctic air are also showing spatial variability, which is typically explained by differences in proximity to suspected key source regions and long-range atmospheric transport potentials. Furthermore, increase in worldwide usage of certain pesticides, e.g. chlorothalonil and quintozene, which are contaminated with hexachlorobenzene (HCB), may result in an increase in Arctic air concentration of HCB. The results combined also indicate that both temporal and spatial patterns of POPs in Arctic air may be affected by various processes driven by climate change, such as reduced ice cover, increasing seawater temperatures and an increase in biomass burning in boreal regions as exemplified by the data from the Zeppelin and Alert stations. Further research and continued air monitoring are needed to better understand these processes and its future impact on the Arctic environment.

Formato

application/zip, 4 datasets

Identificador

https://doi.pangaea.de/10.1594/PANGAEA.786757

doi:10.1594/PANGAEA.786757

Idioma(s)

en

Publicador

PANGAEA

Direitos

CC-BY: Creative Commons Attribution 3.0 Unported

Access constraints: unrestricted

Fonte

Supplement to: Hung, Hayley; Kallenborn, Roland; Breivik, Knut; Su, Yushan; Brorström-Lundén, Eva; Olafsdottir, Kristin; Thorlacius, Johanna M; Leppänen, Sirkka; Bossi, Rossana; Skov, Henrik; Manø, Stein; Patton, Gregory W; Stern, Gary A; Sverko, Ed; Fellin, Phil (2010): Atmospheric monitoring of organic pollutants in the Arctic under the Arctic Monitoring and Assessment Programme (AMAP): 1993-2006. Science of the Total Environment, 408(15), 2854-2873, doi:10.1016/j.scitotenv.2009.10.044

Palavras-Chave #-; 7 PCBs include PCB 28,52,101,118,138,153 and 180; 10 PCBs additionally include PCB 31,105 and 156; a-HCH; alpha/gamma -HCH; alpha/gamma -HCH max; alpha/gamma -HCH min; alpha-Hexachlorocyclohexane in air; BDE-100; BDE-138; BDE-153; BDE-154; BDE-17; BDE-183; BDE-190; BDE-209; BDE-28; BDE-28/33; BDE-47; BDE-66; BDE-85; BDE-99; CHL; Chlordane, standard deviation; Chlordane in air; CHL std dev; cis-CHL; cis-Chlordane in air; Coverage; Date/Time; DATE/TIME; DDD std dev; DDE std dev; DDT; DDT std dev; Dichlorodiphenyldichloroethane, standard deviation; Dichlorodiphenyldichloroethylene, standard deviation; Dichlorodiphenyltrichloroethane, standard deviation; Dichlorodiphenyltrichloroethane in air; Dieldrin, standard deviation; Dieldrin in air; Dieldrin std dev; Endosulfan; Endosulfan in air; Event; gamma-Hexachlorocyclohexane in air; g-HCH; HCB; HCH std dev; Heptachlor exo-epoxide in air; HEPX; Hexachlorobenzene in air; Hexachlorocyclohexane, standard deviation; International Polar Year (2007-2008); ipy; IPY; mean; mean; calculated with 14 measured BDE for Alert and 11 measured BDE for Nuuk; mean; including BDE-33 for Alert samples; mean; sum of cis-CHL + trans-CHL + cis-Nonachlor + trans-Nonachlor; mean; sum of op-DDE, pp-DDE, op-DDD, pp-DDD, op-DDT and pp-DDT.; mean; sum of PCB 28, 31, 52, 101, 105, 118, 138, 153, 156 and 180; mean HCB; Method; Method comment; OCS; OCS in pg/m**3; OCS range max in pg/m**3; OCS range min in pg/m**3; op-DDD; op-DDE; op-DDT; ortho,para-Dichlorodiphenyldichloroethane in air; ortho,para-Dichlorodiphenyldichloroethylene in air; ortho,para-Dichlorodiphenyltrichloroethane in air; oxy-CHL; Oxychlordane in air; para,para-Dichlorodiphenyldichloroethane in air; para,para-Dichlorodiphenyldichloroethylene in air; para,para-Dichlorodiphenyltrichloroethane in air; PBDE; PBDE std dev; PCA; PCB; PCB std dev; Pentachloranisole in air; Polybrominated diphenyl ethers; Polybrominated diphenyl ethers, congener BDE-100; Polybrominated diphenyl ethers, congener BDE-138; Polybrominated diphenyl ethers, congener BDE-153; Polybrominated diphenyl ethers, congener BDE-154; Polybrominated diphenyl ethers, congener BDE-17; Polybrominated diphenyl ethers, congener BDE-183; Polybrominated diphenyl ethers, congener BDE-190; Polybrominated diphenyl ethers, congener BDE-209; Polybrominated diphenyl ethers, congener BDE-28; Polybrominated diphenyl ethers, congener BDE-47; Polybrominated diphenyl ethers, congener BDE-66; Polybrominated diphenyl ethers, congener BDE-85; Polybrominated diphenyl ethers, congener BDE-99; Polybrominated diphenyl ethers, standard deviation; Polychlorinated biphenyl, standard deviation; Polychlorinated biphenyl in air; pp-DDD; pp-DDE; pp-DDT; pp-DDT/pp-DDE; pp-DDT/pp-DDE max; pp-DDT/pp-DDE min; Range; range max; range maximum; range min; range minimum; Ratio; Samp com; Sample comment; Standard deviation; Std dev; sum; sum of 7 respectively 10 PCB congeners (see method comment); TeCV; TeCV in pg/m**3; TeCV range max in pg/m**3; TeCV range min in pg/m**3; Time coverage; t-Nonachlor; trans-CHL; trans-CHL/cis-CHL; trans-CHL/cis-CHL max; trans-CHL/cis-CHL min; trans-Chlordane in air; trans-Nonachlor; trans-Nonachlor in air
Tipo

Dataset