Stachel B, Christoph E H, Götz R, Herrmann T, Krüger F, Kühn T, Lay J, Löffler J, Päpke O, Reincke H, Schröter-Kermani C, Schwartz R, Steeg E, Stehr D, Uhlig S, Umlauf G
Wassergütestelle Elbe der Arbeitsgemeinschaft für die Reinhaltung der Elbe, Nessdeich 120-121, D-21129 Hamburg, Germany.
Sci Total Environ. 2006 Jul 1;364(1-3):96-112. doi: 10.1016/j.scitotenv.2005.07.004. Epub 2005 Sep 30.
Meadow soils, feeding-stuffs and foodstuffs from the alluvial plain of the river Elbe were analyzed in respect of PCDD/Fs, DL-PCBs and mercury with a view to assessing the consequences of the extreme flood of August 2002. The PCDD/F concentrations in the soils range from 3 to 2100 ng WHO-TEQ/kg dm, and for the DL-PCBs the range was 0.32 to 28 ng WHO-TEQ/kg dm. On the basis of established threshold values >40% of the areas are only fit for restricted usage. Mercury concentrations range from 0.11 to 17 mg/kg dm, whereby the action value of 2 mg/kg dm is exceeded in about 50% of the soil samples. A cumulative memory effect from past floods rather than a recent contamination from August 2002 is documented. Soils taken from behind broken dykes showed significantly lower concentrations. Grass, hay and grass silage originating from pasture land in Lower Saxony were taken before and immediately after the flooding. PCDD/Fs range from 0.29 to 16 ng WHO-TEQ/kg, the maximum permitted value of 0.75 ng WHO-TEQ/kg was exceeded in about 50% of the samples. Muscle-tissue from cattle, sheep, lamb and a roe deer as well as untreated milk from individual cows returned values ranging from 0.76 to 5.9 pg WHO-PCDD/F-TEQ/g fat, and 10% of the samples returned values higher than the permitted maximum of 3 pg WHO-PCDD/F-TEQ/g fat. The action value of 2 pg WHO-PCDD/F-TEQ/g fat was exceeded in 33% of the samples. No direct connection between these results and the effects of the flood could be established. A major input path for PCDD/Fs is the tributary Mulde, which discharges contaminated sediments from its catchment area into the Elbe.
对易北河冲积平原的草甸土壤、饲料和食品进行了二噁英/呋喃、二恶英类多氯联苯和汞的分析,以评估2002年8月特大洪水的影响。土壤中二噁英/呋喃的浓度范围为3至2100纳克世卫组织毒性当量/千克干物质,二恶英类多氯联苯的浓度范围为0.32至28纳克世卫组织毒性当量/千克干物质。根据既定的阈值,超过40%的区域仅适合有限使用。汞浓度范围为0.11至17毫克/千克干物质,约50%的土壤样品超过了2毫克/千克干物质的行动值。记录表明,这些结果是过去洪水的累积记忆效应,而非2002年8月最近的污染所致。从决堤后的区域采集的土壤浓度明显较低。在下萨克森州牧场土地洪水前后采集了草、干草和青贮饲料。二噁英/呋喃的浓度范围为0.29至16纳克世卫组织毒性当量/千克,约50%的样品超过了0.75纳克世卫组织毒性当量/千克的最大允许值。牛、羊、羔羊和一只狍子的肌肉组织以及个别奶牛的未加工牛奶的检测值范围为0.76至5.9皮克世卫组织二噁英/呋喃毒性当量/克脂肪,10%的样品检测值高于3皮克世卫组织二噁英/呋喃毒性当量/克脂肪的最大允许值。33%的样品超过了2皮克世卫组织二噁英/呋喃毒性当量/克脂肪的行动值。这些结果与洪水影响之间无法建立直接联系。二噁英/呋喃的一个主要输入途径是穆尔德河支流,该支流将其集水区受污染的沉积物排入易北河。