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Seaweeds as Biomonitoring System for Heavy Metal (HM) Accumulation and Contamination of Our Oceans

机译:海藻作为海洋中重金属(HM)积累和污染的生物监测系统

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This research manuscript reports the heavy metal accumulation in four marine seaweeds sp. 1)? Caulerpa sertlatioides (Cuba); 2) Caulerpa cf. brachypus ; (Bali, Indonesia); 3) Undaria pinnatifida (West-Donegal, Ireland); 4) Ulva lactuca (Easters-Scheldt, the Netherlands). Mechanical pressure at 10 bar of fresh seaweed fronds casu quo biomass in the laboratory delivered seaweed moisture which was analyzed by Inductively Coupled Plasma Spectroscopy (ICP)-techniques for heavy-metals = [HM], (Al, As, Cd, Co, Cr, Cu, Fe, Mo, Ni, Pb & Zn). Three important observations were made: 1) The [HM] in the seaweed moisture is higher than in the surrounding seawater which directs to mechanism(s) of bio-accumulation ; 2) The accumulation factor [AF] is varying per metallic-cation with an overall trend for our four seaweeds and sampling locations for [HM] are: As & Co & Cu: 5000 - 10,000 μg/l; Ni & Zn: 3000 - 5000 μg/l; Cd: 2000 - 3000 μg/l; Cr: 1000 - 2000 μg/l; Al: 200 - 1000 μg/l; Mo & Pb & Fe: 0 - 200 μg/l range. 3) Seaweed moisture detected that [HM]: Pb & Zn & Fe — which all three could not be detected in the seawater — supports the view that seaweeds have a preference in their bio-accumulation mechanism for these three HM. Major conclusion is in general that “overall” for the macro-elements Ca, Fe, K, Mg, Mn, Na, P & S in the moisture of the four seaweed species the concentration is lower in the seaweed species, or equals the concentration, in comparison to the surrounding sea water. For the HM (Al, As, Cd, Co, Cr, Cu, Mo, Ni, Pb & Zn) the opposite is the case species and is the concentration “overall” higher in the seaweed species in comparison to the surrounding sea water. Further topics addressed include strategies of irrigation of the Sahara desert with the moisture out of seaweeds under conditions of low anthropogenic influences.
机译:该研究手稿报告了四种海洋海藻 sp。中的重金属积累。 1)? 南美草(Caulerpa sertlatioides) (古巴); 2) Caulerpa参见。鸭嘴兽; (印度尼西亚巴厘岛); 3) Undaria pinnatifida (爱尔兰西邓加尔); 4) Ulva lactuca (荷兰,Easters-Scheldt)。在实验室中,在10 bar的新鲜海藻叶的机械压力下,海藻生物质传递的海藻水分通过电感耦合等离子体光谱(ICP)技术分析了重金属= [HM],(铝,砷,镉,钴,铬,铜,铁,钼,镍,铅和锌)。进行了三个重要的观察:1)海藻水分中的[HM]高于周围海水中的[HM],这直接导致了 生物蓄积的机制; 2)每种金属阳离子的累积因子[AF]随我们的四个海藻的总体趋势而变化,[HM]的采样位置为:As&Co&Cu:5000-10,000μg/ l; Ni&Zn:3000-5000μg/ l;镉:2000-3000μg/ l; Cr:1000-2000μg/ l;铝:200-1000μg/ l; Mo&Pb&Fe:0-200μg/ l范围。 3)海藻水分检测到[HM]:Pb&Zn&Fe(在海水中都无法检测到这三种物质)支持以下观点:海藻在其 生物蓄积机制中具有偏爱对于这三个HM。一般的主要结论是,四种海藻物种的水分中的常量元素Ca,Fe,K,Mg,Mn,Na,P和S的“总体”浓度在海藻物种中较低,或等于该浓度。 ,与周围的海水相比。对于HM(Al,As,Cd,Co,Cr,Cu,Mo,Ni,Pb和Zn)而言,情况恰恰相反,与周围的海水相比,海藻物种的“总体”浓度更高。涉及的其他主题包括在低人为影响的条件下用海藻中的水分灌溉撒哈拉沙漠的策略。

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