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Fant 9760 publikasjoner. Viser side 281 av 391:

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Polychlorinated naphthalenes in air and snow in the Norwegian Arctic: a local source or an Eastern Arctic phenomenon?

Herbert, B.M.J.; Halsall, C.J.; Villa, S.; Fitzpatrick, L.; Jones, K.C.; Lee, R.G.M.; Kallenborn, R.

2005

Polychloropinene - toxaphene analog produced in the USSR was non-racemic.

Nikiforov, V.; Kryuchkov, F.; Sandanger, T.; Kallenborn, R.; Jensen, E.

2009

Polycyclic aromatic hydrocarbons (PAHs), oxy- and nitro-PAHs in ambient air of the Arctic town Longyearbyen, Svalbard

Drotikova, Titiana; Ali, Aasim Musa Mohamed; Halse, Anne Karine; Reinardy, Helena; Kallenborn, Roland

Polycyclic aromatic hydrocarbons (PAHs) are not
declining in Arctic air despite reductions in their global emissions.
In Svalbard, the Longyearbyen coal-fired power plant
is considered to be one of the major local sources of PAHs.
Power plant stack emissions and ambient air samples, collected
simultaneously at 1 km (UNIS) and 6 km (Adventdalen)
transect distance, were analysed (gaseous and particulate
phases separately) for 22 nitro-PAHs, 8 oxy-PAHs,
and 16 parent PAHs by gas chromatography in combination
with single quadrupole electron capture negative ionization
mass spectrometry (GC-ECNI-MS) and gas chromatography
in combination with triple quadrupole electron ionization
mass spectrometry (GC-EI-MS/MS). Results confirm low
levels of PAH emissions (Sum 16 PAHs D 1:5 μg/kg coal)
from the power plant. Phenanthrene, 9,10-anthraquinone, 9-
fluorenone, fluorene, fluoranthene, and pyrene accounted for
85% of the plant emission (not including naphthalene). A dilution
effect was observed for the transect ambient air samples:
1.26+/- 0.16 and 0.63+/- 0.14 ng/m3 were the sum of all
47 PAH derivatives for UNIS and Adventdalen, respectively.
The PAH profile was homogeneous for these recipient stations
with phenanthrene and 9-fluorenone being most abundant.
Multivariate statistical analysis confirmed coal combustion
and vehicle and marine traffic as the predominant
sources of PAHs. Secondary atmospheric formation of 9-
nitroanthracene and 2C3-nitrofluoranthene was evaluated
and concluded. PAHs partitioning between gaseous and particulate
phases showed a strong dependence on ambient temperatures
and humidity. The present study contributes important
data which can be utilized to eliminate uncertainties in
model predictions that aim to assess the extent and impacts
of Arctic atmospheric contaminants.

2020

Polycyclic Aromatic Hydrocarbons Not Declining in Arctic Air Despite Global Emission Reduction

Yu, Yong; Katsoyiannis, Athanasios A.; Bohlin-Nizzetto, Pernilla; Brorström-Lundén, Eva; Ma, Jianmin; Zhao, Yuan; Wu, Zhiyong; Tych, Wlodzimierz; Mindham, David; Sverko, Ed; Barresi, Enzo; Dryfhout-Clark, Helena; Fellin, Phil; Hung, Hayley

Two decades of atmospheric measurements of polycyclic aromatic hydrocarbons (PAHs) were conducted at three Arctic sites, i.e., Alert, Canada; Zeppelin, Svalbard; and Pallas, Finland. PAH concentrations decrease with increasing latitude in the order of Pallas > Zeppelin > Alert. Forest fire was identified as an important contributing source. Three representative PAHs, phenanthrene (PHE), pyrene (PYR), and benzo[a]pyrene (BaP) were selected for the assessment of their long-term trends. Significant decline of these PAHs was not observed contradicting the expected decline due to PAH emission reductions. A global 3-D transport model was employed to simulate the concentrations of these three PAHs at the three sites. The model predicted that warming in the Arctic would cause the air concentrations of PHE and PYR to increase in the Arctic atmosphere, while that of BaP, which tends to be particle-bound, is less affected by temperature. The expected decline due to the reduction of global PAH emissions is offset by the increment of volatilization caused by warming. This work shows that this phenomenon may affect the environmental occurrence of other anthropogenic substances, such as more volatile flame retardants and pesticides.

2019

Polyklorerte alkaner (PCA) i innlandsfisk. NILU F

Borgen, A.R.; Schlabach, M.; Fjeld, E.; Knutzen, J.

2001

POP emission inventories on different scales and their future trends.

Theloke, J.; Breivik, K.; van der Gon, H.D.; Kugler, U.; Li, Y-F.; Pacyna, J.; Panasiuk, D.; Sundseth, K.; Sweetman, A.; Tao, S.

2010

POP model intercomparison study. Stage 1. Comparison of descriptions of main processes determining POP behaviour in various environmental compartments. EMEP MSC-E Technical Report, 1/2004

Shatalov, V.; Mantseva, E.; Baart, A.; Bartlett, P.; Breivik, K.; Christensen, J.; Dutchak, S.; Kallweit, D.; Farret, R.; Fedyunin, M.; Gong, S.; Hansen, K.M.; Holoubek, I.; Huang, P.; Jones, K.; Matthies, M.; Petersen, G.; Prevedouros, K.; Pudykiewicz, J.; Roemer, M.; Salzmann, M.; Scheringer, M.; Stocker, J.; Strukov, B.; Suzuki, N.; Sweetman, A.; van de Meent, D.; Wegmann, F.

2004

POP model intercomparison study. Stage II. Comparison of mass balance estimates and sensitivity studies. EMEP/MSC-E Technical Report, 5/2006

Shatalov, V.; Mantseva, E.; Baart, A.; Bartlett, P.; Breivik, K.; Christensen, J.; Dutchak, S.; Gong, S.; Gusev, A.; Hansen, K.M.; Hollander, A.; Huang, P.; Hungerbuhler, K.; Jones, K.; Petersen, G.; Roemer, M.; Scheringer, M.; Stocker, J.; Suzuki, N.; Sweetman, A.; van de Meent, D.; Wegmann, F.

2006

POP model intercomparison study. Stage II. Comparison of mass balance estimates and sensitivity studies. DRAFT. EMEP/MSC-E Technical Report, 4/2005

Shatalov, V.; Mantseva, E.; Baart, A.; Bartlett, P.; Breivik, K.; Christensen, J.; Dutchak, S.; Gong, S.; Gusev, A.; Hansen, K.M.; Hollander, A.; Huang, P.; Hungerbuhler, K.; Jones, K.; Petersen, G.; Roemer, M.; Scheringer, M.; Stocker, J.; Suzuki, N.; Sweetman, A.; van de Meent, D.; Wegmann, F.

2005

POP-monitoring in Europe. NILU F

Berg, T.

2001

POP's in krill from Antarctica. Report APN-430.1876

Carroll, J.L.; Götsch, A.; Evenset, A.; Berger, U.; Herzke, D.

2005

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