水产养殖作为环境污染物的来源:土池与塑料池的比较

Benjamin A. Adegola, G. A. Idowu
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引用次数: 0

摘要

在撒哈拉以南非洲,小规模水产养殖系统(土池和塑料池)已成为流行的养鱼手段,既可维持生计,也可作为收入来源。然而,他们成功的做法涉及使用可能积聚在池塘水和沉积物中的有机和无机化学物质,当池塘最终被清空时,这些化学物质最终会进入更大的环境。这可能对环境产生重大影响,因为个别社区有数千个这样的小规模系统,而这些系统基本上不受管制。本研究对典型泥塘和塑料塘的理化特征及重金属组成进行了研究。理化分析的结果揭示了释放含碳有机物质的可能性,这些物质可能会耗尽天然水体中的氧气水平以进行分解。这些有机材料主要来自塑料池塘,因为塑料单体和添加剂浸出到池塘水中。研究表明,土池和塑料池都可能对环境造成重金属污染,尤其是铜(Cu)、锰(Mn)和锌(Zn)。每升泥塘水对铜、锰和锌含量的可能贡献分别为3.92毫克、2.68毫克和2.63毫克;每升排入环境的塑料池塘水分别为2.57毫克、1.94毫克和2.08毫克。土池塘和塑料池塘的沉积物/污泥有可能使环境中的铜含量分别增加5.27毫克和3.61毫克每公斤排放的沉积物。这项研究是对土塘和塑料塘水产养殖(关于化学污染物)的环境影响的初步调查,可以协助热带非洲当局制订政策,以确保自然环境的可持续性和质量不因重金属对植物物种、节肢动物和蚯蚓等动物群、微生物过程发展的小规模影响的扩散而受到损害。金属进入溶液的趋势,以及进入地下水和地表水的可能性。因此,高于MPC的值表明沉积物或土壤中的特定金属可能对环境构成危害。至于指定的重金属浓度,结果显示,在泥塘和塑料塘的沉积物中测量的金属浓度大多低于重金属浓度,这意味着泥塘或塑料塘的单一操作所产生的沉积物/污泥中的金属含量不会构成环境问题的来源。唯一的例外是铜,两种沉积物类型的MPC都超过了,即使在去掉土池土壤中的背景铜浓度后也是如此。对于两种情况下的池塘水,本研究表明,两种池塘类型的沉积物/污泥中的Cu浓度构成了这种金属污染环境的来源。
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Aquaculture as Source of Environmental Contaminants: A Study of Earthen Pond versus Plastic Pond
: In Sub-Sahara Africa, small-scale aquaculture systems (earthen ponds and plastic basin ponds) have become popular as means of fish cultivation, both for subsistence and as a source of income. Their successful practice, however, involves the use of organic and inorganic chemical substances which may accumulate in pond water and sediments, ultimately finding their ways into the larger environment when the ponds are eventually emptied. This may have significant impact on the environment, since individual communities have thousands of such small-scale systems which are largely unregulated. In this study, we investigated the physico-chemical characteristics and heavy metal composition of typical earthen and plastic ponds. Result of physicochemical analyses revealed the possibility of release of carbonaceous organic materials which may deplete the oxygen levels in natural waters for their decomposition. Such organic materials would come mainly from plastic ponds, as a result of leaching of the plastic monomers and additives into the pond water. The study indicated that both earthen and plastic ponds could contribute to the contamination of the environment by heavy metals, especially Copper (Cu), manganese (Mn) and Zinc (Zn). Possible contributions to Cu, Mn and Znlevels are 3.92 mg, 2.68 mg and 2.63 mgrespectively, per litre of earthen pond water; and 2.57 mg, 1.94 mg and 2.08 mgrespectively, per litre of plastic pond water discharged into the environment. Sediment/sludge of both earthen and plastic ponds have the potential to spike Cu levels in the environment by 5.27 mg and 3.61 mg per kg of sediment discharged, respectively. This study constitutes an initial investigation into the environmental impacts of earthen and plastic pond aquaculture (with respect to chemical contaminants) and could assist authorities in tropical Africa to formulate policies to ensure that the sustainability and quality of the natural environments are not compromised by the proliferation of small-scale effect of heavy metals on plant species, on fauna such as arthropods and earthworms, on the development of microbiological processes, the tendency of the metals to go into solution, and the possibility to enter ground and surface waters. Thus, values above the MPC suggest that the particular metals in the sediment or soil may constitute a hazard to the environment. For metals that the MPC are specified for, the results show that the concentration of metals measured in the earthen and plastic pond sediments are mostly below the MPC, implying that the levels of metals in sediment/sludge resulting from single operation of earthen or plastic pond do not constitute a source of environmental concern. The only exception is Cu, in which the MPC is exceeded in both sediment types, even after taking out the background Cu concentration in the soil for the earthen pond. As for the pond waters in both cases, this study reveals that Cu concentration in the sediments/sludge of both pond types constitute a source of contamination of the environment with this metal.
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