Key Laboratory of Freshwater Aquaculture and Enhancement of Anhui Province, Fisheries Research Institute, Anhui Academy of Agricultural Sciences, Hefei, 230031, China.
School of Resources and Environment, Anhui Agricultural University, Hefei, 230031, China.
Environ Sci Pollut Res Int. 2019 Oct;26(29):29585-29596. doi: 10.1007/s11356-019-06210-x. Epub 2019 Aug 22.
An exhaustive overview of heavy metal pollution in Chaohu Lake illustrating enrichment intensity, temporal and spatial distribution, chemical speciation, and ecological risk under natural and anthropogenic changes was conducted. Low concentrations of heavy metals excluding Hg were found in water whereas high Hg might be ascribed to surrounding coal-fired power plants. Copper, Pb, Zn, Cd, and Hg were enriched in sediment whereas Cr and Ni were comparable to background values. Besides, As demonstrated an equal accumulation from natural and anthropogenic fluxes. Heavy metals were at a low level prior to the 1950s; it increased gradually during the 1950s-1960s owing to population growth and agricultural expansion; then it displayed abrupt increase since the late 1970s due to rapid modern urbanization and industrialization and agricultural intensification. Spatial distribution of heavy metals was a good indicator of natural and anthropogenic changes, where higher enrichment was found in the western lake. Apart from fluvial input, anthropogenic disturbances such as land use changes, atmospheric deposition, and algae-derived organic matter, along with natural stressors including climate change, hydrological alteration, and soil erosion, made significant contribution to the biogeochemical cycle of heavy metals in the lake. Heavy metals mainly from anthropogenic sources were dominantly partitioned in non-residual fractions, whereas those mainly from natural sources were predominantly distributed in residual form. Mercury and Cd were below the threshold effect concentration (TEC) indicating that adverse effects were excluded. However, result of chemical speciation demonstrated Cd would pose a considerable potential ecological risk. Besides, most of the heavy metals were in the range of TEC-PEC suggesting possible toxicity.
对巢湖重金属污染进行了全面综述,说明了在自然和人为变化下,重金属的富集强度、时空分布、化学形态和生态风险。水中重金属(汞除外)浓度较低,而高汞可能归因于周围的燃煤电厂。铜、铅、锌、镉和汞在沉积物中富集,而铬和镍与背景值相当。此外,砷表现出与自然和人为通量相等的积累。重金属在 20 世纪 50 年代之前处于低水平;在 20 世纪 50 年代至 20 世纪 60 年代,由于人口增长和农业扩张,重金属含量逐渐增加;自 20 世纪 70 年代末以来,由于快速的城市化和工业化以及农业集约化,重金属含量急剧增加。重金属的空间分布是自然和人为变化的良好指标,西部湖泊的重金属富集程度更高。除河流输入外,土地利用变化、大气沉降和藻类衍生有机物质等人为干扰以及气候变化、水文变化和土壤侵蚀等自然胁迫因素对湖泊重金属的生物地球化学循环也有重要贡献。主要来自人为源的重金属主要分配在非残留部分,而主要来自自然源的重金属主要以残留形式分布。汞和镉低于阈值效应浓度(TEC),表明排除了不利影响。然而,化学形态的结果表明,镉将构成相当大的潜在生态风险。此外,大多数重金属处于 TEC-PEC 范围内,表明可能存在毒性。