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An analytical protocol for the determination of total mercury concentrations in solid peat samples

机译:测定固体泥炭样品中总汞浓度的分析规程

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Traditional peat sample preparation methods such as drying at high temperatures and milling may be unsuitable for Hg concentration determination in peats due to the possible presence of volatile Hg species, which could be lost during drying. Here, the effects of sample preparation and natural variation on measured Hg concentrations are investigated. Slight increases in mercury concentrations were observed in samples dried at room temperature and at 30℃ (6.7 and 2.48 ng kg~(-1) h~(-1), respectively), and slight decreases were observed in samples dried at 60, 90 and 105℃ (2.36, 3.12 and 8.52 ng kg~(-1) h~(-1), respectively). Fertilising the peat slightly increased Hg loss (3.08 ng kg~(-1) h~(-1) in NPK-fertilised peat compared to 0.28 ng kg~(-1) h~(-1) in unfertilised peat, when averaged over all temperatures used). Homogenising samples by grinding in a machine also caused a loss of Hg. A comparison of two Hg profiles from an Arctic peat core, measured in frozen samples and in air-dried samples, revealed that no Hg losses occurred upon air-drying. A comparison of Hg concentrations in several plant species that make up peat, showed that some species (Pinus mugo, Sphagnum recurvum and Pseudeuernia furfuracea) are particularly efficient Hg retainers. The disproportionally high Hg concentrations in these species can cause considerable variation in Hg concentrations within a peat slice. The variation of water content (1.6% throughout 17-cm core, 0.97% in a 10X 10 cm slice), bulk density (40% throughout 17-cm core, 15.6% in a 10X10 cm slice) and Hg concentration (20% in a 10X10 cm slice) in ombrotrophic peat were quantified in order to determine their relative importance as sources of analytical error. Experiments were carried out to determine a suitable peat analysis program using the Leco AMA 254, capable of determining mercury concentrations in solid samples. Finally, an analytical protocol for the determination of Hg concentrations in solid peat samples is proposed. This method allows correction for variation in factors such as vegetation type, bulk density, water content and Hg concentration in individual peat slices. Several subsamples from each peat slice are air dried, combined and measured for Hg using the AMA254, using a program of 30 s (drying), 125 s (decomposition) and 45 s (waiting). Bulk density and water content measurements are performed on every slice using separate subsamples.
机译:传统的泥炭样品制备方法(例如高温干燥和研磨)可能不适合测定泥炭中的Hg浓度,因为可能存在挥发性Hg物质,在干燥过程中可能会丢失。在这里,研究了样品制备和自然变化对测得的汞浓度的影响。在室温和30℃下干燥的样品中汞浓度略有增加(分别为6.7和2.48 ng kg〜(-1)h〜(-1)),在60、90和60℃下干燥的样品中汞含量略有下降。和105℃(分别为2.36、3.12和8.52 ng kg〜(-1)h〜(-1))。施肥泥炭时,汞的损失略有增加(NPK施肥的泥炭中的汞损失为3.08 ng kg〜(-1)h〜(-1),而未施肥的泥炭中的汞损失为0.28 ng kg〜(-1)h〜(-1),取平均值为所有温度)。通过在机器中研磨均质样品也会导致汞损失。在冷冻样品和风干样品中对来自北极泥炭芯的两个汞曲线进行比较后,发现风干时没有汞损失。比较组成泥炭的几种植物中的汞含量,结果表明某些物种(Pinus mugo,Sphagnum recurvum和Pseudeuernia furfuracea)是特别有效的Hg保持剂。在这些物种中,过高的汞浓度会导致泥炭切片中汞浓度的显着变化。水分的变化(在整个17厘米的岩心中为1.6%,在10X 10 cm的切片中为0.97%),堆积密度(在整个17厘米的岩心中为40%,在10X10 cm的切片中为15.6%)和汞浓度(在20x的10%中为了确定它们作为分析误差来源的相对重要性,对非营养性泥炭中的10X10 cm切片进行了定量。使用Leco AMA 254进行了实验,以确定合适的泥炭分析程序,该程序能够确定固体样品中的汞浓度。最后,提出了测定泥炭中汞含量的分析方案。该方法可以校正各个泥炭切片中诸如植被类型,堆积密度,水分和汞浓度等因素的变化。风干每个泥炭切片的几个子样本,合并,并使用AMA254、30 s(干燥),125 s(分解)和45 s(等待)的程序测量Hg含量。使用单独的子样本对每个切片进行体积密度和含水量测量。

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