School of Environmental Studies & State Key Laboratory of Biogeology and Environmental Geology, China University of Geosciences, Wuhan, 430074, China.
School of the Environment, State Key Laboratory of Pollution Control and Resource Reuse, Nanjing University, Nanjing, 210023, China.
Environ Pollut. 2020 Oct;265(Pt A):115002. doi: 10.1016/j.envpol.2020.115002. Epub 2020 Jun 12.
Mercury (Hg) is commonly extracted from solid phase samples using aqua regia for total Hg (tHg) analysis. However, uncertainties exist regarding the complete extraction of Hg by aqua regia, especially from carbonaceous materials. To investigate whether aqua regia can completely extract Hg from biochars, batch-style experiments were carried out to evaluate extraction efficiency of aqua regia with respect to Hg-loaded biochar and to characterize the residual Hg speciation and spatial distribution. Different types of biochars (raw, FeCl-modified, and FeSO-modified, prepared at different temperatures) were reacted with Hg-spiked solution before the digestion experiments. Adsorption analyses indicate the biochars were successfully loaded with Hg and that the Hg content was higher in biochars pyrolyzed at higher temperature (900 versus 300 or 600 °C). The results of digestion experiments indicate Hg could not be completely extracted from the biochars tested, with a greater percentage of residual Hg in biochars pyrolyzed at 600 (60 ± 15%) and 900 (75 ± 22%) than 300 °C (7 ± 2%). Furthermore, the fraction of residual Hg in FeSO-modified biochars after aqua regia digestion was significantly lower than in FeCl-modified and unmodified biochars. Confocal micro-X-ray fluorescence imaging (CMXRFI) showed residual Hg in biochars is concentrated on surfaces prior to digestion, but more homogeneously distributed after digestion, which indicates Hg on biochar surface is more easily digested. Hg extended X-ray absorption fine structure (EXAFS) spectra modelling showed residual Hg in biochars mainly exists as Hg(II)-Cl. These results indicate extra caution should be paid for tHg determinations using aqua regia digestion method in soil (especially in forest), sediment, and peat samples containing black carbon, activated carbon, or biochar.
汞(Hg)通常使用王水从固相样品中提取,用于总汞(tHg)分析。然而,王水完全提取 Hg 的过程存在不确定性,特别是从含碳材料中提取 Hg 时。为了研究王水是否能从生物炭中完全提取 Hg,进行了批式实验,以评估王水对负载 Hg 的生物炭的提取效率,并对残余 Hg 形态和空间分布进行了表征。不同类型的生物炭(原始、FeCl 改性和 FeSO 改性,在不同温度下制备)在消化实验前与 Hg 掺杂溶液反应。吸附分析表明生物炭成功负载了 Hg,并且在较高温度(900 与 300 或 600°C)下热解的生物炭中 Hg 含量更高。消化实验结果表明,测试的生物炭中 Hg 不能完全提取,在 600(60±15%)和 900(75±22%)热解的生物炭中残留 Hg 的比例高于 300°C(7±2%)。此外,在王水消化后,FeSO 改性生物炭中残留 Hg 的比例明显低于 FeCl 改性和未改性生物炭。共焦微 X 射线荧光成像(CMXRFI)显示,在消化前,生物炭中的残留 Hg 集中在表面,但在消化后分布更加均匀,这表明生物炭表面的 Hg 更容易被消化。Hg 扩展 X 射线吸收精细结构(EXAFS)光谱建模表明,生物炭中的残留 Hg 主要以 Hg(II)-Cl 的形式存在。这些结果表明,在含有黑碳、活性炭或生物炭的土壤(特别是森林)、沉积物和泥炭样品中,使用王水消化法测定 tHg 时应格外小心。