Norwegian Institute for Water Research, 0349, Oslo, Norway.
Norwegian Institute for Water Research, 0349, Oslo, Norway.
Chemosphere. 2021 Feb;264(Pt 2):128544. doi: 10.1016/j.chemosphere.2020.128544. Epub 2020 Oct 7.
The Grenlandfjords in South East Norway are severely contaminated with dioxins from a magnesium smelter operated between 1950 and 2001. In 2009, the proposal of thin-layer capping as a potential mitigation method to reduce spreading of dioxins from the fjord sediments, resulted in the set-up of a large-scale field experiment in two fjord areas at 30 and 100 m depth. After capping, several investigations have been carried out to determine effects on benthic communities and bioavailability of dioxins. In this paper we present the results on uptake of dioxins and furans (PCDD/F) in passive samplers and two sediment-dwelling species exposed in boxcores collected from the test plots during four surveys between 2009 (after cap placement) and 2018. Sediment profile images (SPI) and analyses of dioxins revealed that the thin (1-5 cm) cap layers became buried beneath several centimeters of sediments resuspended from adjacent bottoms and deposited on the test plots after capping. Uptake reduction ratios (R) were calculated as dioxins accumulated in cores collected from capped sediments divided by dioxins accumulated in cores collected from uncapped reference sediments. Cap layers with dredged clay or crushed limestone had only short-term positive effect with R-values increasing to about 1.0 (no effect) 1-4 years after capping. In spite of the recontamination, cap layers with clay and activated carbon had significant long-term effects with R-values slowly increasing from 0.12-0.33 during the first three years to 0.39-0.46 in 2018, showing 54-61% reduced uptake of dioxins (PCDD/F-TE) nine years after capping with AC.
在东南挪威的格陵兰峡湾,由于一家镁冶炼厂在 1950 年至 2001 年期间运营,这里受到了二恶英的严重污染。2009 年,人们提出采用薄层覆盖作为一种潜在的缓解方法,以减少峡湾沉积物中二恶英的扩散,这导致在 30 米和 100 米深的两个峡湾地区进行了大规模的现场试验。覆盖之后,进行了几次调查,以确定对底栖生物群落和二恶英生物有效性的影响。本文介绍了在 2009 年(覆盖后)至 2018 年期间的四次调查中,从试验区采集的箱芯中使用被动采样器和两种底栖物种进行的二恶英和呋喃(PCDD/F)的吸收结果。沉积物剖面图像(SPI)和二恶英分析表明,薄层(1-5 厘米)覆盖层在覆盖后,被来自相邻底部的几厘米悬浮沉积物掩埋在试验区下。吸收减少比(R)的计算方法是,从覆盖有沉积物的芯样中积累的二恶英除以从未覆盖的参考沉积物中积累的二恶英。用疏浚粘土或粉碎的石灰石制成的覆盖层仅在覆盖后 1-4 年内具有短期的积极效果,R 值增加到约 1.0(无效果)。尽管受到再污染,但粘土和活性炭覆盖层仍具有显著的长期影响,在最初的三年中,R 值从 0.12-0.33 缓慢增加,到 2018 年达到 0.39-0.46,表明在覆盖活性炭九年后,二恶英(PCDD/F-TE)的吸收减少了 54-61%。