Bignert A, Olsson M, Persson W, Jensen S, Zakrisson S, Litzén K, Eriksson U, Häggberg L, Alsberg T
Contaminant Research Group, Swedish Museum of Natural History Box 50007, SE-104 05 Stockholm, Sweden.
Environ Pollut. 1998;99(2):177-98. doi: 10.1016/s0269-7491(97)00191-7.
The time trend monitoring of organochlorine pollution was carried out in Sweden since the late 1960s. This report presents data on concentrations of DDT, PCB, HCHs and HCB in biota samples collected and analysed annually. All the matrices and compounds studied show a significant decrease over time. The data cover severely polluted Swedish marine and fresh water in southern Sweden as well as locally unpolluted waters in remote northern Arctic regions of Sweden. A total of 13 time series representing different locations and species are presented for the different pollutants. The period studied covers the time when pollution was serious as well as the time of recovery. All monitoring activities were carried out at the same laboratories over the entire study period, which means that comparability over time is good in the sets of data presented. The various time trends show a convincing agreement with trends and annual change over time, although the concentrations differ between the species and locations investigated, the highest concentrations being in the south. Since the annual changes are normally similar regardless of locations and species, spatial variations in concentrations remain over time, although concentrations are lower today. The onset of changes in concentrations over time can be related to international measures or other circumstances that lowered releases into the environment. Similarities in the annual changes, as well as the time when changes began, are discussed with respect to suggested hypotheses on the fate of the investigated organochlorines. It was not possible to verify that the oxygenation of anoxic sediments mobilised old pollution in Baltic sediments. Neither was it possible to conclude that eutrophication has caused a measurable effect on the rate and timing of the decreases. Finally, long-range transport to Arctic regions seems to be due more to a one step transport than to the 'Grass-hopper' effect. The comprehensive database used, clearly shows how important it is to have datasets big enough to describe between-year variation before attempting to evaluate the time trend. In addition, if between-year variation is not known, it is then also difficult to evaluate spatial variation on the basis of single year observations.
自20世纪60年代末以来,瑞典一直在对有机氯污染进行时间趋势监测。本报告提供了每年收集和分析的生物群样本中滴滴涕、多氯联苯、六氯环己烷和六氯苯浓度的数据。所有研究的基质和化合物随时间均呈现显著下降。数据涵盖了瑞典南部严重污染的海洋和淡水以及瑞典北极偏远北部地区局部未受污染的水域。针对不同污染物,共给出了代表不同地点和物种的13个时间序列。研究期涵盖了污染严重时期以及恢复时期。在整个研究期间,所有监测活动均在相同实验室进行,这意味着所呈现的数据集中随时间的可比性良好。尽管所调查的物种和地点之间浓度有所不同,最高浓度出现在南部,但各种时间趋势与随时间的趋势和年度变化呈现出令人信服的一致性。由于无论地点和物种,年度变化通常相似,尽管如今浓度较低,但浓度的空间变化随时间依然存在。浓度随时间变化的起始可与降低向环境排放的国际措施或其他情况相关。就所研究有机氯的归宿的假设而言,讨论了年度变化的相似性以及变化开始的时间。无法证实缺氧沉积物的氧化作用使波罗的海沉积物中的旧污染得以 mobilised。也无法得出富营养化对下降速率和时间产生可测量影响的结论。最后,向北极地区的长距离传输似乎更多是由于一步传输而非“蚱蜢”效应。所使用的综合数据库清楚地表明,在尝试评估时间趋势之前,拥有足够大的数据集以描述年际变化是多么重要。此外,如果不知道年际变化,那么基于单年观测来评估空间变化也很困难。 (注:“mobilised”此处可能有误,原文可能是“mobilize”,可结合上下文进一步确认准确含义)