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汞的形态分析研究进展 总被引：3，自引：2，他引：1
《岩矿测试》1999,20(1):3
综述了自然界、特别是人体内汞的存在形态,讨论了汞形态分析中样品的预处理、分离富集、分析方法的研究现状和进展,指出了汞形态分析所面临的问题,对矿物药的药效研究及毒性和安全性评价具有一定指导意义。 相似文献
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汞矿区稻田土壤汞形态分布特征及对甲基化的影响 总被引：1，自引：0，他引：1
汞污染区稻米甲基汞超标现象普遍存在,汞在土壤中的形态分布被认为是影响甲基化过程的重要因素之一.本研究选取贵州省万山废弃汞矿区和土法炼汞区为研究区域,在水稻生长期间对稻田土壤剖面中总汞、甲基汞及形态汞进行测定,结合土壤环境因子指标,讨论土壤汞形态分布特征对甲基化的影响.研究表明,汞矿区稻田土壤中总汞和甲基汞均表现出随土壤... 相似文献
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离子色谱-电感耦合等离子体质谱法测定乳粉的汞形态 总被引：2，自引：1，他引：1
对于乳粉的汞形态分析,由于基质的复杂性,有机汞非常容易与样品中蛋白质上的巯基结合,形成稳定的络合物,在前处理过程中须保证各形态提取完全且各形态之间不会发生相互转化,因此样品前处理是汞形态分析的难点;同时乳粉中汞含量极低,对方法检出限提出了更高的要求。本文通过优化样品前处理过程,建立了离子色谱-电感耦合等离子体质谱测定乳粉中三种汞形态(二价汞、甲基汞、乙基汞)的方法。实验采用多种复合酶(蛋白酶、脂肪酶、淀粉酶)对乳粉基质中的蛋白、脂肪、淀粉进行解离,采用L-半胱氨酸-盐酸-甲醇的混合溶液作为提取剂进行超声提取,样品过RP固相萃取小柱去除杂质后用C18色谱柱(5μm,4.6 mm×150 mm)进行分离,流动相采用10 mmol/L乙酸铵-0.12%L-半胱氨酸-5%甲醇混合溶液进行淋洗,5 min内即可实现三种汞形态的基线分离。二价汞、甲基汞和乙基汞的加标回收率在79.9%~111.2%之间,检出限分别为0.5μg/kg、0.6μg/kg、0.9μg/kg。实际样品分析表明,汞总量很低的乳粉,汞各形态的提取率也能达到70%以上,能够满足检测要求。本方法在样品前处理过程中采用酶解的方式解离复杂基体中的汞形态,提高了提取率至80%以上;仪器分析方面采用甲醇作为增敏剂,提高了检测灵敏度,适用于乳粉样品中痕量汞形态的检测。 相似文献
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土壤／沉积物中汞污染地球化学及污染防治措施研究 总被引：4，自引：0，他引：4
本文综述了汞的来源,介绍了汞的形态及形态分析方法的研究进展,讨论了影响汞吸附和解吸的主要因素,比较了对土壤/沉积物中汞污染进行风险评价的方法,提出了生物修复、减少汞污染的排放等治理我国汞污染的有效措施。最后对汞在土壤/沉积物中的地球化学行为等研究方面进行了展望。 相似文献
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The release of mercury (Hg) from leaf tissue was compared between two dominant salt marsh macrophytes,Spartina alterniflora andPhragmites australis. Rates of Hg release were measured for individual leaves from late May to late July, along with concentrations of Hg in leaf tissue, rates of sodium (Na) release, and rates of transpiration. Leaves ofS. alterniflora consistently releasd 2–3 times more Hg than leaves ofP. australis. Leaves ofS. alterniflora also contained greater concentrations of Hg during these months. In contrast toP. australis leaves, rates of Na release were high forS. alterniflora and were correlated with rate of Hg release. Transpiration rates averaged 2.2 times greater forPhragmites as compared toS. alterniflora, and were not correlated with the other variables at the leaf level for either species. Leaf Hg concentration was highly correlated with Hg release for both species, but the slope was significantly greater forS. alterniflora. Monthly differences were profound for all climate and physiological variables measured, with high measurements in May, and lower measurements in June and July. For both species, the highest Hg content was found in lower leaves in May, followed by upper leaves in May. Hg accumulation in leaf tissue and release from both species appear to be greatest in the spring, although differences between the species persist throughout these peak months of the growing season. 相似文献
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R. Melamed R.C. Villas Bas G.O. Gonalves E.C. Paiva 《Journal of Geochemical Exploration》1997,58(2-3)
Mercury accumulation in the food chain, as a consequence of gold recovery in Brazil, has been an issue of concern. Reactions of Hg in the environment are quite complex, and can involve various Hg chemical species. Laboratory experiments were carried out on Hg0 solubility, Hg complexation and sorption on river sediments from a gold mining region in Brazil. The reactivity and the mobility of Hg species were considered. Results indicate that methyl mercury is more mobile than ionic mercury, and that the presence of humic acid enhances drastically the solubility of Hg0. The soluble complex formed has a relatively lower interaction at the sediment/water interface and is more prone to spread through the aquatic environment. 相似文献
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Reactive amendments such as Portland and super-sulfate cements offer a promising technology for immobilizing metalloid contaminants such as mercury (Hg) in soils and sediments through sequestration in less bioavailable solid forms. Tidal marsh sediments were reacted with dissolved Hg(II) in synthetic seawater and fresh water solutions, treated with Portland cement and FeSO4 amendment, and aged for up to 90 days. Reacted solids were analyzed with bulk sequential extraction methods and characterized by powder X-ray diffraction (XRD), electron microscopy, and synchrotron X-ray absorption spectroscopy at the Hg LIII- and S K-edge. In amended sediments, XRD, SEM and sulfur K-edge XANES indicated formation of gypsum in seawater experiments or ettringite-type (Ca6Al2(SO4)3(OH)12.26H2O) phases in fresh water experiments, depending on the final solution pH (seawater ∼8.5; freshwater ∼10.5). Analysis of Hg EXAFS spectra showed Cl and Hg ligands in the first- and second-coordination shells at distances characteristic of a polynuclear chloromercury(II) salt, perhaps as a nanoparticulate phase, in both seawater and fresh water experiments. In addition to the chloromercury species, a smaller fraction (∼20–25%) of Hg was bonded to O atoms in fresh water sample spectra, suggesting the presence of a minor sorbed Hg fraction. In the absence of amendment treatment, Hg sorption and resistance to extraction can be accounted for by relatively strong binding by reduced S species present in the marsh sediment detected by S XANES. Thermodynamic calculations predict stable aqueous Hg–Cl species at seawater final pH, but higher final pH in fresh water favors aqueous Hg-hydroxide species. The difference in Hg coordination between aqueous and solid phases suggests that the initial Hg–Cl coordination was stabilized in the cement hydration products and did not re-equilibrate with the bulk solution with aging. Collectively, results suggest physical encapsulation of Hg as a polynuclear chloromercury(II) salt as the primary immobilization mechanism. 相似文献
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Mercury speciation and distribution in Aha Reservoir which was contaminated by coal mining activities in Guiyang, Guizhou, China 总被引：6，自引：0，他引：6
Xinbin Feng Weiyang Bai Lihai ShangTianrong He Guangle QiuHaiyu Yan 《Applied Geochemistry》2011,26(2):213-221
Two sampling campaigns were carried out in March and August 2005 representing dry and wet seasons, respectively, to investigate the distribution patterns of Hg species in the water column and sediment profiles at two sampling stations in Aha Reservoir located in Guiyang, Southwestern China. Aha Reservoir has been contaminated by Hg due to small scale coal mining activities. Mercury concentrations in both water and sediment were elevated. A clearly seasonal variation of dissolved Hg (DHg), particulate Hg (PHg) and total Hg (THg) concentrations in the water column was observed. The concentrations of these Hg species in the wet season were significantly higher than in the dry season. Runoff input and diffusion of Hg from sediments could be the reasons for elevated concentrations of these Hg species in the wet season. The contaminated sediment is acting as a secondary contamination source for both inorganic Hg (IHg) and methylmercury (MeHg) to the overlying water. The cycling of Mn in the sediment governs the diffusion process of IHg to the water column. In the dry season (winter and spring), Mn occurs as MnO2 because the uppermost part of sediment is in an oxic condition and Hg ions are absorbed by MnO2. In the wet season (summer and fall), the uppermost part of the sediment profile is in a reduced condition because of stratification of the water column and MnO2 is reduced to Mn2+, which results in transformation of Hg2+ into porewater as Mn2+ became soluble. This causes a higher diffusive flux of IHg from sediment to overlying water in the wet season. Both sampling stations showed a consistent trend that THg concentrations decreased in the uppermost part of sediment cores. This demonstrated that the measures taken to reduce ADM contamination to Aha Reservoir also reduced Hg input to the reservoir. Methyl Hg diffusive fluxes from sediment to overlying water were higher in the wet season than the dry season demonstrating that high temperatures favor Hg methylation processes in sediment. 相似文献
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Mercury speciation and mobilization in contaminated soils of the Valle del Azogue Hg mine (SE,Spain) 总被引：1，自引：0，他引：1
Hg mobilization from contaminated soils and mine wastes was the source of environmental contamination in the Valle del Azogue
mining area. We researched solid-phase speciation and aqueous mobility of Hg through Scanning electron microscopy-energy dispersive
X-ray spectroscopy and electron probe microanalysis analysis, solid-phase-Hg-thermo-desorption (SPTD) and laboratory column
experiments. We found that in contaminated soils and mine wastes, the predominant Hg species was cinnabar (HgS), mainly formed
from the weathering of Hg-rich pyrite, and metallic Hg (0) in the matrix, whereas in calcines and tailings the dominant species
was metallic Hg (0). The mobilization of Hg in the aqueous phase seems to have originated from the dissolution of elemental
Hg (0) present in soils and wastes, reaching concentrations of up to 67 μg l−1, and showing a higher long-term environmental potential risk, in addition to atmospheric emissions. 相似文献
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Aaron J. Slowey 《Geochimica et cosmochimica acta》2010,74(16):4693-9187
Mercury is a global contaminant of concern due to its transformation by microorganisms to form methylmercury, a toxic species that accumulates in biological tissues. The effect of dissolved organic matter (DOM) isolated from natural waters on reactions between mercury(II) (Hg) and sulfide (S(-II)) to form HgS(s) nanoparticles across a range of Hg and S(-II) concentrations was investigated. Hg was equilibrated with DOM, after which S(-II) was added. Dissolved Hg (Hgaq) was periodically quantified using ultracentrifugation and chemical analysis following the addition of S(-II). Particle size and identity were determined using dynamic light scattering and X-ray absorption spectroscopy. S(-II) reacts with Hg to form 20 to 200 nm aggregates consisting of 1-2 nm HgS(s) subunits that are more structurally disordered than metacinnabar in the presence of 2 × 10−9 to 8 × 10−6 M Hg and 10 (mg C) L−1 DOM. Some of the HgS(s) nanoparticle aggregates are subsequently dissolved by DOM and (re)precipitated by S(-II) over periods of hours to days. At least three fractions of Hg-DOM species were observed with respect to reactivity toward S(-II): 0.3 μmol reactive Hg per mmol C (60 percent), 0.1 μmol per mmol C (20 percent) that are kinetically hindered, and another 0.1 μmol Hg per mmol C (20 percent) that are inert to reaction with S(-II). Following an initial S(-II)-driven precipitation of HgS(s), HgS(s) was dissolved by DOM or organic sulfur compounds. HgS(s) formation during this second phase was counterintuitively favored by lower S(-II) concentrations, suggesting surface association of DOM moieties that are less capable of dissolving HgS(s). DOM partially inhibits HgS(s) formation and mediates reactions between Hg and S(-II) such that HgS(s) is susceptible to dissolution. These findings indicate that Hg accessibility to microorganisms could be controlled by kinetic (intermediate) species in the presence of S(-II) and DOM, undermining the premise that equilibrium Hg species distributions should correlate to the extent or rate of Hg methylation in soils and sediments. 相似文献
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Jeroen E. Sonke 《Geochimica et cosmochimica acta》2011,75(16):4577-9916
Mass independent fractionation (MIF) of stable isotopes associated with terrestrial geochemical processes was first observed in the 1980s for oxygen and in the 1990s for sulfur isotopes. Recently mercury (Hg) was added to this shortlist when positive odd Hg isotope anomalies were observed in biological tissues. Experimental work identified photoreduction of aquatic inorganic divalent HgII and photodegradation of monomethylmercury species as plausible MIF inducing reactions. Observations of continental receptors of atmospheric Hg deposition such as peat, lichens, soils and, indirectly, coal have shown predominantly negative MIF. This has led to the suggestion that atmospheric Hg has negative MIF signatures and that these are the compliment of positive Hg MIF in the aquatic environment. Recent observations on atmospheric vapor phase Hg0 and HgII in wet precipitation reveal zero and positive Hg MIF respectively and are in contradiction with a simple aquatic HgII photoreduction scenario as the origin for global Hg MIF observations.This study presents a synthesis of all terrestrial Hg MIF observations, and these are integrated in a one-dimensional coupled continent-ocean-atmosphere model of the global Hg cycle. The model illustrates how Hg MIF signatures propagate through the various Earth surface reservoirs. The scenario in which marine photoreduction is the main MIF inducing process results in negative atmospheric Δ199Hg and positive ocean Δ199Hg of −0.5‰ and +0.25‰, yet does not explain atmospheric Hg0 and HgII wet precipitation observations. Alternative model scenarios that presume in-cloud aerosol HgII photoreduction and continental HgII photoreduction at soil, snow and vegetation surfaces to display MIF are necessary to explain the ensemble of natural observations. The model based approach is a first step in understanding Hg MIF at a global scale and the eventual incorporation of Hg stable isotope information in detailed global mercury chemistry and transport models. 相似文献
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Concentrations of mercury (Hg) in fish were compared between two Florida estuaries, the Indian River Lagoon and Florida Bay. The objective was to determine if differences in Hg concentration exist and to attempt to relate those differences to sources of Hg. Five hundred and thirteen estuarine fish were collected and analyzed for Hg concentration. Fish species collected were black drum, bluefish, bonnethead shark, common snook, crevalle jack, gafftopsail catfish, gray snapper, Mayan cichlid, pompano, red drum, sheepshead, southern flounder, spadefish, and spotted seatrout. Analysis of variance of species-specific Hg data among the three defined regions of eastern and western Florida Bay and the Indian River Lagoon substantiated regional differences. Proximity to known anthropogenic sources of Hg appeared to be a significant factor in the distribution of Hg concentration among the fish collected. Sufficient numbers of crevalle jack, gray snapper, and spotted seatrout were collected to permit statistical analysis among regions. Hg concentrations in all three of these species from eastern Florida Bay were higher than those collected in the other two areas. A major fraction of the estuarine fish collected in eastern Florida Bay exceeded one or more State of Florida or U.S. Food and Drug Administration fish consumption health advisory criteria. In general, fish from western Florida Bay contained less Hg than those from the Indian River Lagoon, and fish from the Indian River contained less Hg than those from eastern Florida Bay. Crevalle jack from all areas and spotted seatrout from Florida Bay were placed on a consumption advisory in Florida. Detailed study of Florida Bay food web dynamics and Hg biogeochemical cycling is recommended to better understand the processes underlying the elevated Hg levels in fish from eastern Florida Bay. This information may be vital in the formulation of appropriate strategies in the ongoing South Florida restoration process. 相似文献
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Zhi Zhang Yinglan Cao Jian Li Chao Cai Zhiyong Huang 《Environmental Earth Sciences》2014,72(5):1749-1758
The distribution and bioavailability of Hg in vegetable-growing soils collected from the estuary areas of Jiulong River, China, were studied. Concentrations of Hg in top-soils, soil profiles and plant samples were measured with the method of hydride generation atomic fluorescence spectrometry after microwave digestion. Mercury species in soils were determined with the sequential extraction procedures based on Kingston method. Results showed that Hg concentrations in top-soils ranged from 49.8 to 1,685 ng g?1, with an average of 510 ng g?1 which was more than twice higher than the mercury limit (250 ng g?1 at pH < 6.5) of soil quality set for edible agricultural products in China (HJ 332-2006). High levels of Hg were found to mainly distribute in the top-soils from the northern, western and southern part of the estuary areas. Hg concentrations decreased with the increases of profile depths, except for one sample (S15) in which Hg level in the depth of 0–20 cm was found lower than that in the 20–40 cm. Hg in most of soil samples in non-mobile forms accounted for 46–82 % of total Hg in soils, while Hg in the mobile forms only 0.6–8.7 %. No significant correlation of Hg concentrations between the vegetables and the soils was observed in the studied areas, which indicates that the transfer factors could only reflect the abilities of Hg uptake and accumulation in a specific plant, but they are unsuitable to be used as the general indexes for the mobility and bioavailability of Hg in soils. 相似文献
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贵州省普定水库水体及沉积物孔隙水中汞的含量和形态分布初步研究 总被引：2，自引：0，他引：2
为了弄清楚普定水库汞的地球化学循环特征,用金汞齐-冷原子荧光光谱法(CVAFS)和气相色谱技术(GC), 研究了乌江流域上游普定水库水体剖面和沉积物间隙水剖面汞的赋存形态(总汞 THg)、溶解态汞(DHg)、活性汞(RHg)、颗粒态汞(PHg)、总甲基汞(TMeHg)、溶解态甲基汞(DMeHg)和颗粒态甲基汞(PMeHg)的分布特征.结果显示,普定水库水体总汞浓度为1.29～3.18 ng/L, 活性汞浓度为0.09～0.43 ng/L, 总甲基汞浓度为0.06～0.18 ng/L.沉积物间隙水中溶解态汞浓度为2.65 ～11.47 ng/L, 溶解态甲基汞浓度为0.06 ～1.16 ng/L.实验数据表明,普定水库水体中溶解态汞和颗粒态含量相当,其中颗粒态汞占总汞的比例为46%,并与总汞存在极显著相关性(R=0.929,n=20,P＜0.01),溶解态汞与总汞相关性不明显(R=-0.067,n=20);冬季普定水库甲基汞以溶解态甲基汞为主,溶解态甲基汞占总甲基汞的比例为63%,溶解态甲基汞与总甲基汞无明显相关关系(R=0.292,n=20),颗粒态甲基汞与总甲基汞存在极显著的相关性(R=0.815,n=20,P＜0.01).试验数据表明沉积物孔隙水溶解态汞与溶解态甲基汞浓度明显高于上覆水体, 是普定水库水体中汞的一个重要来源. 相似文献