Umeå universitets logga

The pollution trend of polychlorinated dibenzo-p-dioxins and dibenzofurans (PCDD/Fs) in the Baltic Sea region was studied based on depth profiles of PCDD/Fs in sediment cores collected from six offshore areas, eight coastal sites impacted by industrial/urban emissions, and one coastal reference site. A general trend was observed for the offshore and coastal reference sites with substantial increase in PCDD/F concentrations in the mid-late 1970s and peak levels during 1985-2002. The overall peak year for PCDD/Fs in Baltic Sea offshore areas was estimated (using spline-fit modeling) to 1994 ± 5 years, and a half-life in sediments was estimated at 29 ± 11 years. For the industrial/urban impacted coastal sites, the temporal trend was more variable with peak years occurring 1-2 decades earlier compared to offshore areas. The substantial reductions from peak levels (38 ± 11% and 81 ± 12% in offshore and coastal areas, respectively) reflect domestic and international actions taken for reduction of the release of PCDD/Fs to the environment. The modeled overall half-life and reductions of PCDD/Fs in offshore Baltic Sea sediment correspond well to both PCDD/F trends in European lakes without any known direct PCDD/F sources (half-lives 30 and 32 years), and previously modeled reduction in atmospheric deposition of PCDD/Fs to the Baltic Sea since 1990. These observations support previous findings of a common diffuse source, such as long-range air transport of atmospheric emissions, as the prime source of PCDD/Fs to the Baltic Sea region. The half-life of PCDD/Fs in Baltic Sea offshore sediments was estimated to be approximately 2 and 4-6 times longer than in semirural and urban European air, respectively. This study highlights the need for further international actions to reduce the levels of PCDD/Fs in Baltic Sea air specifically and in European air in general.

Spatial and temporal trends of sources of polychlorinated dibenzo-p-dioxins and dibenzofurans (PCDD/Fs) in the Baltic Sea were evaluated by positive matrix factorization (PMF) and principal component analysis (PCA). Sediment cores were sampled at eight coastal, one coastal reference, and six offshore sites covering the northern to the southern Baltic Sea. The cores, which covered the period 1919-2010, were sliced into 2-3 cm disks among which 8-11 disks per core (in total 141 disks) were analyzed for all tetra- through octa-CDD/Fs. Identification and apportionment of PCDD/F sources was carried out using PMF. Five stable model PCDD/F congener patterns were identified, which could be associated with six historically important source types: (i) atmospheric background deposition (ABD), (ii) use and production of penta-chlorophenol (PCP), (iii) use and production of tetra-chlorophenol (TeCP), (iv) high temperature processes (Thermal), (v) hexa-CDD-related sources (HxCDD), and (vi) chlorine-related sources (Chl), all of which were still represented in the surface layers. Overall, the last four decades of the period 1920-2010 have had a substantial influence on the Baltic Sea PCDD/F pollution, with 88 ± 7% of the total amount accumulated during this time. The 1990s was the peak decade for all source types except TeCP, which peaked in the 1980s in the northern Baltic Sea and has still not peaked in the southern part. The combined impact of atmospheric-related emissions (ABD and Thermal) was dominant in the open sea system throughout the study period (1919-2010) and showed a decreasing south to north trend (always >80% in the south and >50% in the north). Accordingly, to further reduce levels of PCDD/Fs in the open Baltic Sea ecosystem, future actions should focus on reducing atmospheric emissions.

Levels of polychlorinated dibenzo-p-dioxins and dibenzofurans (PCDD/Fs, “dioxins”) in fatty fish of the Baltic Sea have remained high despite declines in environmental levels since the 1980s. This has raised human health concerns and restricted marketing of Baltic herring and salmon within the European Union. Thus, there is an urgent need to identify and control current PCDD/F emission sources. Analysis presented here explains why PCDD/Fs levels in fish have stopped declining or even increased in recent decades. We show that contributions of “thermal” sources (e.g., waste incineration) of PCDD/Fs to Baltic fish have declined since the 1990s, but not contributions of sources associated with the manufacture and use of chlorophenols (particularly tetrachlorophenol and pentachlorophenol, TCP and PCP, respectively). Moreover, the discrepancy between declines in levels of dioxins in abiotic compartments (e.g. sediments and air), and stable or increasing levels in biota can be explained by the persistently high bioavailability of PCDD/Fs associated with TCP and PCP type sources.

Atmospheric sources are major contributors of polychlorinated dibenzo-p-dioxins and dibenzofurans (PCDD/Fs) in the Baltic Sea environment. In this study, we investigated the potential of using trace metals along with PCDD/F levels and seasonal trends as markers of important source types for PCDD/Fs in air. Levels of PCDD/F congeners (n=17) and metals (n=16) were measured in summer and winter air using high volume sampling at a rural field station (Aspvreten, Sweden). During winter, levels were on average 20 times higher than in summer (5.1 ± 5.8 fg TEQ m^-3 and 0.26 ± 0.18 fg TEQ m^-3, respec- tively) mostly due to a higher fraction of PCDFs. The increased levels were pronounced in air masses from southern (S) and eastern (E) compass sectors. Most of the detected metals (n=12) were positively and significantly correlated with the PCDF congeners for all compass sectors (Cd, Co, Cu, Fe, K, Mn, Pb, Sb, and Zn) during winter season. The average correlation coefficient (r) value for the correlation between PCDF congeners and these metals was 0.85 and p values generally below <0.05. In contrast, polychlorinated biphenyls (PCBs) and hexachlorobenzene (HCB) showed no significant correlations with detected metals except for HCB and Cr (r=0.60 and p<0.01). The wide range of candidate metals as source markers for PCDD/F emissions, and the lack of an up-to-date extensive compilation of source characteristics for metal emission from various sources, limited the use of the metals as source markers in the current study. Although, the study was not able to pin-point primary PCDD/F sources for Baltic air, we demonstrated a promising approach for source tracing of PCDD/F in air.