Effects of Spatial, temporal and pH changes on fractionated heavy metals in sediments of the Middleton River, Bayelsa State, Nigeria

Aigberua Ao
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引用次数: 9

Abstract

Any metallic element possessing relatively high density and toxicity even at lower concentrations is referred to as heavy metal.1 Heavy metals occur naturally as a composition of the earth’s crust and inundate the aquatic ecosystem via weathering and washing of bedrock and solid mineral materials, aerial downpour from volcanic discharge as well as anthropogenic inputs which include effluent discharges emanating from nearby industries, offshore equipment or installations and vehicular or boat transportation emissions). Heavy metals introduced in the marine ecosystem are mostly concentrated in coastal areas, near densely populated and industrialized regions. Heavy metals are usually associated to particles. These particles are often very small, and can therefore stay in solution for a very long time. Nevertheless they will end up in the sediments. Therefore concentrations in the sediments are often 10 to 100 times higher than those in solution. In the sediments, these particles may form important secondary source of contamination, even after the primary source has disappeared.2 Heavy metal fractionation is the identification of the volumetric amounts and specific species (or forms) which makes up an element within a given environment. Hence, heavy metal fractionation helps to identify the environmental toxicity potential of a metal on the basis of its biogeochemistry. The total metal concentration is usually measured to quantify the elemental burden in sediment and soils.3 Metal speciation includes the chemical form of the metal in the soil solution, either as a free ion or complexed to a ligand, in the gaseous phase and distributed amongst solid phases within the soil. However, the long-term bioavailability of metals to humans and other organisms is determined by the re-supply of the metal to the mobile pool (soil solution) from more stable phases (metals in and associated with solid species).4 It is extensively demonstrated that increasing heavy metal pollution from various industries constitutes environmental hazard for humans and other living things.5 A number of events affecting water quality have resulted in increased public concern about surface water quality.6 Such events as increased domestic wastes generation and indiscriminate disposal and discharge of untreated and poorly treated industrial wastes into surface water bodies impact negatively on water quality and lead to water quality deterioration.7,8 Heavy metals associated with crude oil include Pb, Cd, Cu, Zn, Ni, V and Cr amongst others.9 Diseases and pathological conditions related to heavy metal contaminants have been recently reviewed by Izah and Srivastav.6 The level of pH is a very important factor which determines how heavy metals are retained or released in an aquatic environment. Hydrogen ion possesses the tendency to be strongly attached to surface negative charges and possess the power to replace most other cations.10 Metal mobility tends to increase at lower pH and decreases at higher pH.11 Mobility of metals in soil with low pH has been reported to decrease in the order: Cd > Ni > Zn > Mn > Pb, even though the effect of pH on mobility of elements in soil is highly variable depending on the content and type of organic matter.12 The physicochemical properties of aquatic ecosystems are characterized by a number of independent parameters. Factors such as temperature, oxygen content and pH of a water body can alter the solubility of the salts in it, the forms of occurrence of particular species, as well as their bioavailability and toxicity. Thus, it is necessary to determine the various species of metals present in the different compartments of the aquatic ecosystem.13 pH is known to have significant effect on metal dynamics because it controls adsorption and precipitation, which are the main mechanism of metal retention in soils.14 Cd sorption by an acid sandy soil has been found to double for each 0.5 unit increase in
空间、时间和pH变化对尼日利亚巴耶尔萨州米德尔顿河沉积物中分馏重金属的影响
任何密度相对较高且即使在较低浓度下也具有毒性的金属元素都被称为重金属。1重金属作为地壳的一种成分自然存在,并通过风化和冲刷基岩和固体矿物材料淹没水生生态系统,火山排放的空中倾盆大雨以及人为输入,包括附近工业、海上设备或设施的污水排放以及车辆或船只运输的排放)。海洋生态系统中引入的重金属大多集中在沿海地区,靠近人口稠密和工业化地区。重金属通常与颗粒有关。这些颗粒通常非常小,因此可以在溶液中停留很长时间。尽管如此,它们最终还是会进入沉积物中。因此,沉积物中的浓度通常比溶液中的浓度高10到100倍。在沉积物中,即使在主要污染源消失后,这些颗粒也可能形成重要的二次污染源。2重金属分馏是指在给定环境中识别构成元素的体积量和特定物种(或形式)。因此,重金属分馏有助于在生物地球化学的基础上识别金属的环境毒性潜力。测量总金属浓度通常是为了量化沉积物和土壤中的元素负荷。3金属形态包括土壤溶液中金属的化学形式,可以是游离离子,也可以是与配体络合的,在气相中,分布在土壤中的固相中。然而金属对人类和其他生物的长期生物利用度取决于金属从更稳定的相(固体物质中的金属和与固体物质相关的金属)重新供应到移动池(土壤溶液)影响水质的事件增加了公众对地表水质量的关注。6生活垃圾产生量增加,未经处理和处理不力的工业废物被随意处理和排放到地表水体等事件对水质产生了负面影响,并导致水质恶化。7,8与原油有关的重金属包括Pb、Cd、Cu、Zn、Ni、V和Cr等。Izah和Srivastav最近对与重金属污染物有关的疾病和病理状况进行了综述。6 pH水平是决定重金属在水生环境中如何保留或释放的一个非常重要的因素。氢离子具有强烈附着在表面负电荷上的趋势,并具有取代大多数其他阳离子的能力。10金属迁移率在较低pH下趋于增加,在较高pH下趋于降低。11据报道,金属在低pH土壤中的迁移率按顺序降低:Cd>Ni>Zn>Mn>Pb,尽管pH值对土壤中元素迁移率的影响因有机物的含量和类型而异。12水生生态系统的物理化学性质由许多独立参数表征。水体的温度、含氧量和pH等因素会改变盐在其中的溶解度、特定物种的出现形式以及它们的生物利用度和毒性。因此,有必要确定水生生态系统不同隔间中存在的各种金属。13已知pH对金属动力学有显著影响,因为它控制着吸附和沉淀,而吸附和沉淀是金属在土壤中保留的主要机制
本文章由计算机程序翻译,如有差异,请以英文原文为准。
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