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Arsenic fractionation in soils using an improved sequential extraction procedure

机译:使用改进的连续萃取程序在土壤中进行砷分离

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lability and bioavailability in the soil. We developed and tested a sequential extraction procedure (SEP) for As by choosing extraction reagents commonly used for sequential extraction of metals, Se and P. Tests with alternative extractarits that have been used in SEPs for P and metals, including N~NO3, NaOAc, NH20H.HCl, EDTA, ~OH and ~F, were shown to either have only low extraction efficiency for As, or to be insufficiently selective or specific for the phases targeted. The final sequence obtained includes the following five extraction steps: (1) 0.05M (~)2S04, 20°C/4h; (2) 0.05M N~H2PO4, 20°C/16h; (3) 0.2M ~+ -oxalate buffer in the dark, pH 3.25, 20°C/4h; (4) 0.2M ~+ -oxalate buffer + ascorbic acid, pH 3.25, 96°C/0.5 h; (5) HNO3/H202 microwave digestion. Within the inherent limitations of chemical fractionation, these As fractions appear to be primarily associated with (1) non-specifically sorbed; (2) specifically-sorbed; (3) amorphous and poorly-crystalline hydrous oxides of Fe and A1; (4) well-crystallized hydrous oxides of Fe and Al; and (5) residual phases. This interpretation is supported by selectivity and specificity tests on soils and pure mineral phases, and by energy dispersive X-ray microanalysis (EDXMA) of As in selected soils. Partitioning of As among these five fractions in 20 soils was (%, medians and ranges): (1) 0.24 (0.02-3.8); (2) 9.5 (2.6-25); (3) 42.3 (12-73); (4) 29.2 (13-39); and (5) 17.5 (1.1-38). The modified SEP is easily adaptable in routine soil analysis, is dependable as indicated by repeatability (w ~ 0.98) and recovery tests. This SEP can be useful in predicting the changes in the lability of As in various solid phases as a result of soil remediation or alteration in environmental factors.
机译:土壤中的不稳定性和生物利用度。我们通过选择常用于金属,硒和磷的顺序萃取的萃取试剂,开发并测试了As的顺序萃取程序(SEP)。使用了在SEP中用于P和金属(包括N〜NO3,NaOAc)的替代萃取物进行的测试NH20H.HCl,EDTA,〜OH和〜F的砷萃取效率低,或者对目标相的选择性或特异性不足。获得的最终序列包括以下五个提取步骤:(1)0.05M(〜)2SO4,20°C / 4h; (2)0.05M N〜H2PO4,20°C / 16h; (3)0.2M〜+-草酸盐缓冲液,在黑暗中,pH 3.25,20°C / 4h; (4)0.2M〜+-草酸盐缓冲液+抗坏血酸,pH 3.25,96°C / 0.5 h; (5)HNO3 / H2O2微波消解。在化学分馏的固有限制内,这些As馏分似乎主要与(1)非特异性吸附有关; (2)专门吸附的; (3)Fe和Al的无定形和弱结晶的水合氧化物; (4)铁和铝的结晶良好的水合氧化物; (5)残留相。对土壤和纯矿物相的选择性和特异性测试,以及选定土壤中As的能量色散X射线微分析(EDXMA)支持了这种解释。在20个土壤中的这五个部分中,As的分配为(%,中位数和范围):(1)0.24(0.02-3.8); (2)9.5(2.6-25); (3)42.3(12-73); (4)29.2(13-39); (5)17.5(1.1-38)。改良的SEP很容易适应常规的土壤分析,并具有可重复性(w〜0.98)和恢复测试所表明的可靠性。该SEP可用于预测由于土壤修复或环境因素的改变而导致的各种固相中As的不稳定性变化。

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