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Heavy metals content and distribution in the surface sediments of the Guangzhou section of the Pearl River, Southern China

机译:中国南方珠江广州段表层沉积物中重金属含量及其分布

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The long-term industrialization and urbanization of Guangzhou city may lead to heavy metal contamination of its aquatic sediment. Nevertheless, only few studies have been published on the distribution and contamination assessment of heavy metals in this urban river sediment. Thus, the major objective of this study was to quantitatively assess contamination of heavy metals and their chemical partitioning in the sediments of the Guangzhou section of the Pearl River (GSPR). Surface sediment samples were collected at 10 sites in the main river and 12 sites in the creeks of the GSPR. The total content of Cd was determined by graphite furnace atomic adsorption spectrometry (GF-AAS), and content of Cr, Cu, Pb and Zn was determined by inductively coupled plasma atomic emission spectrometry (ICP-AES). The chemical partitioning of these heavy metals in the sediments of the main river was determined by the sequential selective extraction (SSE) method. Results indicated that the average total concentrations of Cd, Cr, Pb, Cu and Zn in the sediments of the main river were 1.44, 63.7, 95.5, 253.6 and 370.0 mg/kg, respectively, whereas they were 2.10, 125.5, 110.1, 433.7 and 401.9 mg/kg in the sediments of the creeks. The sediment at M4 and C9 sites was heavily contaminated with about 8 and 11 of toxic unit, respectively. Cr, Cu, Pb and Zn were mostly bound to organic matter and in the residual phase, whereas Cd was mostly associated with the soluble and exchangeable phase and the residual phase. The mobility and bioavailability of Cd, Zn and Cr in the sediments of the main river were relatively higher than Cu and Pb, due to higher levels in the soluble and exchangeable fraction and the carbonate fraction. The potential acute toxicity in the sediments of the main river and creeks was mainly caused by Cu contamination, accounting for 21.7-37.1% and 16.9-46.3% of the total toxicity, respectively, followed by Zn and Pb. Adverse biological effects induced by heavy metals would be expected in the sediments of the GSPR. Therefore, the sediments of the GSPR, especially at M4 and C9 sites, need to be remediated to maintain aquatic ecosystem health.
机译:广州市的长期工业化和城市化可能导致其水生沉积物中重金属的污染。然而,关于城市河流沉积物中重金属的分布和污染评估的研究很少。因此,本研究的主要目的是定量评估珠江(GSPR)广州段沉积物中重金属的污染及其化学分配。在主要河流的10个地点和GSPR小河的12个地点收集了地表沉积物样本。用石墨炉原子吸收光谱法(GF-AAS)测定镉的总含量,用电感耦合等离子体原子发射光谱法(ICP-AES)测定铬,铜,铅和锌的含量。这些主要金属在主要河流沉积物中的化学分配通过顺序选择性萃取(SSE)方法确定。结果表明,主要河流沉积物中Cd,Cr,Pb,Cu和Zn的平均总浓度分别为1.44、63.7、95.5、253.6和370.0 mg / kg,而分别为2.10、125.5、110.1、433.7 / kg小溪的沉积物中含有401.9 mg / kg。 M4和C9站点的沉积物分别被约8和11个有毒单元严重污染。 Cr,Cu,Pb和Zn主要与有机物结合并存在于残留相中,而Cd主要与可溶性和可交换相及残留相相关。 Cd,Zn和Cr在主要河流沉积物中的迁移率和生物利用度相对高于Cu和Pb,这是由于可溶性和可交换馏分和碳酸盐馏分的含量较高。主要河流和小河沉积物中潜在的急性毒性主要是由铜污染引起的,分别占总毒性的21.7-37.1%和16.9-46.3%,其次是锌和铅。预计在GSPR的沉积物中会发生由重金属引起的不良生物效应。因此,需要对GSPR的沉积物,特别是M4和C9站点的沉积物进行修复,以维持水生生态系统的健康。

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