重金属污染土壤修复的Pb2+钝化产物稳定性

自然状态下土壤中重金属元素是否稳定存在是重金属污染固化修复技术中的核心问题。本文以常见重金属离子Pb²⁺为例,分析土壤中重金属离子与常见离子基团结合的稳定性。将第一性原理应用于Pb的存在形态和稳定性的分析,计算了PbCO₃、PbSO₄、PbCl₂、Pb₃（PO₄）₂、PbAl₂O₄和Pb₃Fe₂（PO₄）₄的自由能、能带和态密度。首先推断Pb²⁺和CO₃^2-、SO₄^2-、Cl^-、PO₄^3-等土壤中常见阴离子的结合稳定性,再判断加入金属阳离子Al³⁺和Fe³⁺对体系稳定性的影响。结果表明：铅化合物自由能从高到低趋势为PbCl₂、PbAl₂O₄、PbCO₃、PbSO₄、Pb₃（PO₄）₂、Pb₃Fe₂（PO₄）₄,其相应的结构稳定性顺序从大到小为Pb₃Fe₂（PO₄）₄、Pb₃（PO₄）₂、PbSO₄、PbCO₃、PbAl₂O₄、PbCl₂。通过对能带和态密度的分析,首先确定了SO₄^2-和PO₄^3-的引入能够增强含Pb体系的稳定性,进一步加入金属阳离子Fe³⁺会使体系更稳定。推测SO₄^2-、PO₄^3-为治理Pb²⁺污染合适的官能团,应选择容易释放SO₄^2-、PO₄^3-的物质作为合适的钝化剂。在实际应用中可选择磷酸二氢钠、无水硫酸钠、脱硫石膏等作为钝化剂。     

Raman Micro-Spectroscopic Study of Sulfate Ion in the System Na2SO4 – H2O

This work aims to quantify sulfate ion concentrations in the system Na₂SO₄-H₂O using Raman micro-spectroscopy.Raman spectra of sodium sulfate solutions with known concentrations were collected at ambient temperature（293 K） and in the 500 cm^₁-4000 cm^-1 spectral region.The results indicate that the intensity of the SO₄^2- band increases with increasing concentrations of sulfate ion.A linear correlation was found between the concentration of SO₄^2-（c） and parameter I₁,which represents the ratio of the area of the SO₄^2- band to that of the O-H stretching band of water（A_s/A_w）:I₁=-0.00102+0.01538 c.Furthermore,we deconvoluted the O-H stretching band of water(2800 cm^-1-3800 cm^-1) at 3232 and 3430 cm^-1 into two sub-Gaussian bands,and then defined Raman intensity of the two sub-bands as A_Bi(3232 cm^-1) and A_B2(3430 cm^-1),defined the full width of half maximum（FWHM） of the two sub-bands as W_B1(3232 cm^-1) and W_B2(3430 cm^-1).A linear correlation between the concentration of SO₄^2-（c） and parameter I₂,which represents the ratio of Raman intensity of SO₄^2-（A_s）(in 981 cm^-1) to(A_B1+A_B2),was also established:I₂=-0.0111+0.3653 c.However,no correlations were found between concentration of SO₄^2-（c） and FWHM ratios,which includes the ratio of FWHM of SO₄^2-（W_s） to W_B1 W_B2 and W_B1+B2(the sum of W_B1 and W_B2),suggesting that FWHM is not suitable for quantitative studies of sulfate solutions with Raman spectroscopy.A comparison of Raman spectroscopic studies of mixed Na₂SO₄ and NaCI solutions with a constant SO₄^2- concentration and variable CI^- concentrations suggest that the I\ parameter is affected by CI^-,whereas the I₂ parameter was not.Therefore,even if the solution is not purely Na₂SO₄-H₂O,SO₄^2- concentrations can still be calculated from the Raman spectra if the H₂O band is deconvoluted into two sub-bands,making this method potentially applicable to analysis of natural fluid inclusions.     

中国第二次北极科学考察沿线气溶胶成分分析

对2003年7月15~9月28日间中国第二次北极科学考察沿线所采集的气溶胶样品进行分析,获得了Na⁺、NH₄⁺ 、Ca²⁺、Cl^-、MSA、SO₄^2- 等11种离子的浓度数据(文中使用当量浓度).根据相关分析, 可将11种离子分为3类: 海盐源离子, 包括Na⁺、Mg²⁺、K⁺、Ca²⁺、Cl^-、SO₄^2-; 人为源, 包括NH₄⁺ 、NO₃^-; 其它源, 包括 CH₃COO^-、MSA、C₂O₄^2-. 气溶胶以海盐气溶胶为主, Cl^-、Na⁺ 离子分别是阴阳离子中含量最大的离子, (Na⁺ +Cl^-)对气溶胶载量(所测定的阴阳离子的总和)的贡献平均为60.2%, 占气溶胶总量的一半以上. NH₄⁺ /SO₄^2- 的比值的平均为0.45, 根据当地的大气环境和气溶胶的离子平衡, 认为气溶胶样品中NH₄⁺ 和 SO₄^2- 主要是以 NH4HSO4的形式结合. 根据考察沿线 NO₃^- 浓度的变化, 把考察沿线大致分为3个区: 日本海区, 中值为15.2 neq·m^-3; 鄂霍次克海及白令海区, 中值为1.8 neq·m^-3; 北冰洋区, 其浓度较低, 中值为0.4 neq·m^-3. 考察沿线白令海是MSA的高产区.     

秦岭太白山南麓降水中常量无机离子特征及其来源研究

以2011年11月至2014年9月连续采集的74个有效降水样品为研究载体,运用趋势分析法和相关分析法分析太白山南麓黄柏塬地区降水中常量无机离子（NH₄⁺、Ca²⁺、Na⁺、K⁺、Mg²⁺、SO₄^2-、NO₃^-、Cl^-、F^-）的化学特征,并结合富集因子法、端源贡献法及后向气流轨迹模型探究其来源。结果表明：研究区降水中各离子浓度大小顺序为Ca²⁺ > SO₄^2- > NH₄⁺ > NO₃^- > K⁺ > Na⁺ > Mg²⁺ > Cl^- > F^-,主要阳离子是Ca²⁺和NH₄⁺,共占阳离子总量的76.21%,主要阴离子是SO₄^2-和NO₃^-,共占阴离子总量的90.83%。降水总离子年平均浓度为404.64 μeq·L^-1,相对于国内外已研究的其他高山站点偏高,表现出典型的大陆型及人为源干扰的特征。受排放源、气象因子、植被、降水量等因素影响,降水总离子浓度表现出显著的季节差异,依次为冬季 > 春季 > 秋季 > 夏季。源解析结果显示降水中SO₄^2-和NO₃^-95%以上由人为源贡献,Ca²⁺和Mg²⁺主要来源于地壳风化,Na⁺海盐源和非海盐源贡献约各占一半,K⁺主要来自于非海盐贡献,而F^-和NH₄⁺则几乎全部由人为源贡献。不同路径气团影响下的降水离子组分具有明显不同,北方气团途径太原、石家庄、北京、兰州等工业发达城市,工业燃煤交通废气排放量大,降水中SO₄^2-、NO₃^-浓度均偏高,离子总浓度也明显高于南方气团。     

秦岭主峰太白山北麓降水化学特征分析

利用太白山北麓2011年12月-2013年7月共39次降水样品数据资料, 定量分析了该区域降水化学的特征和时间变化规律. 结果表明: 太白山北麓地区降水中, 除常量离子Na⁺、NH₄⁺、K⁺、Mg²⁺、Ca²⁺、F^-、Cl^-、SO₄^2-、NO₃^-外, CO₃^2-、HCO₃^-、PO₄^3-及低分子有机酸也占有相当比例. 研究区降水常量离子浓度的顺序依次为: NH₄⁺ > SO₄^2- > Ca²⁺ > NO₃^- > Na⁺ > Cl^- > Mg²⁺ > K⁺ > F^-, 离子总浓度表现出明显的季节变化: 夏季(轻度污染) < 秋季(中等污染) < 春季(严重污染) < 冬季(极重污染). 利用因子分析法得出太白山北麓地区降水组分主要有三种来源; Na⁺、Cl^-、Mg²⁺、Ca²⁺主要来自地壳源, SO₄^2-、NO₃^-、NH₄⁺主要来自人为源, K⁺和F^-主要由海盐源和人为源共同贡献. 根据Hysplit 后向气流轨迹分析, 得出不同路径气团降水离子组分不同: 受地形等因素影响, 北方路径的气团比南方路径气团离子总浓度较高; 受土壤类型影响, 西北方向气团降水Na⁺、Mg²⁺、Ca²⁺浓度较高; 受人为活动影响, 东北方向SO₄^2-、NO₃^-、NH₄⁺浓度较高.     

中国首次北极科学考察沿线气溶胶可溶性成分的分析

中国首次北极科学考察沿线采集的大气气溶胶样品可溶性成分分析表明,大气气溶胶的平均载量为195neq·m^-3,Na⁺和Cl^-的贡献为0%,NH₄⁺和SO₄^2-的贡献为27%,nssSO₄^2-对SO₄^2-的贡献为8%.气溶胶中阴、阳离子总量基本相当,大气环境呈中性.气溶胶中可溶性成分具有较强的纬度变化特征.根据离子的变化态势可将离子分为3大类,即1)Na⁺,Cl^-,SO₄^2-,K⁺,Mg²⁺,Ca²⁺;2)NH₄⁺,NO₃^-;3)MSA.Na⁺和Cl^-具有较好的线性关系,Cl^-/Na⁺的当量浓度比为1.01,小于其在海水中的比值1.1.NH₄⁺和NO₃^-的浓度随纬度的增加呈现减少的趋势,说明在低纬度近海岸地区人类活动的污染相当强烈.MSA的浓度在白令海区出现高值,与Shemya(52°N,174°E)站夏季浓度1.79±0.83neq·m^-3(170±79ng·m^-3)相当.通过与不同海区夏季释放DMS的通量对比,进一步证明了低温有利于DMS向MSA的转化.     

祁连山老虎沟地区夏季大气颗粒物中水溶性离子的变化特征

为了研究青藏高原东北缘老虎沟地区大气颗粒物中水溶性无机离子组分的变化特征,于2016年7月16日至8月11日共采集13个PM_2.5样品和4套粒径分级样品。研究结果显示：非沙尘期间,水溶性离子总质量浓度为2.35 μg·m^-3,主要离子SO₄^2-、Ca²⁺、NH₄⁺和NO₃^-的浓度分别为1.28、0.33、0.32和0.28 μg·m^-3,约占水溶性离子浓度总和的94%;沙尘期间,水溶性无机离子总质量浓度为12.63 μg·m^-3,是非沙尘期间浓度的5倍,主要离子SO₄^2-、Ca²⁺、Cl^-、Na⁺和NO₃^-的浓度依次为5.36、4.77、0.80、0.62和0.61 μg·m^-3,约占水溶性离子浓度总和的96%。分级样品分析结果表明,NO₃^-主要分布在粗颗粒模态,可能是前体物在粉尘表面发生非均相反应产生。在沙尘时期,SO₄^2-主要为粉尘贡献,集中分布在粗颗粒模态。在非沙尘时期,SO₄^2-在粗颗粒模态和积聚模态都有较多的分布。积聚模态的SO₄^2-主要是通过前体物与NH₃发生均相反应产生。据估算,非沙尘时期的二次反应对PM_2.5中SO₄^2-的贡献约为80%。     

气象要素影响下雪冰离子淋溶过程研究——以乌鲁木齐河源1号冰川为例

为了更好地理解化学离子在雪坑中的迁移和保存,进一步解释冰芯记录,基于乌鲁木齐河源1号冰川海拔4130 m处的雪冰化学资料,研究了气温和降水与离子淋溶过程的关系.结果表明：气温与离子浓度呈负相关关系,夏季的雪坑离子浓度波动剧烈,冬季的雪坑离子浓度相对稳定.离子浓度随正积温的升高呈指数衰减趋势,当正积温至0℃以上时,离子浓度急剧降低;当正积温升至60℃左右时,离子浓度呈缓慢降低.不同离子的淋溶过程对正积温的响应有所不同,随着正积温的增加,SO₄^2-,NO₃^-,Na⁺,Cl^-,NH₄⁺和Ca²⁺的衰减趋势非常显著,而Mg²⁺和K⁺则呈现无规律性的变化.淋溶因子指出,融水渗浸作用导致雪坑中大部分离子被淋溶;不同离子的淋溶因子也有明显差异,Mg²⁺淋溶因子最小（0.43）,SO₄^2-淋溶因子最大（0.84）,说明Mg²⁺最为稳定,而SO₄^2-最易淋溶.降水对雪坑离子浓度的影响较为微弱,主要通过增加表层雪离子浓度而提升整个雪坑的离子浓度.     

洮河流域水化学特征及其时空变化研究

以洮河流域河水为研究对象,通过对2018年每隔1月洮河干流及支流博拉河和广通河采样点的河水进行水化学研究,揭示了洮河流域河水的水化学组成,探讨了其水化学性质时空变化。结果表明：洮河流域水质偏碱性,干流上游pH值小于下游,并在枯水期都比丰水期为大;矿化度呈枯水期比丰水期小,河水属于中等矿化度水和适度硬水;总硬度、电导率呈枯水期比丰水期大;HCO₃^-、Ca²⁺、Na⁺、Cl^-、SO₄^2-、CO₃^2-含量呈枯水期比丰水期大;干流上游HCO₃^-、Ca²⁺、CO₃^2-含量大于下游,干流上游Mg²⁺、K⁺、Na⁺、Cl^-、SO₄^2-、MnO₄<...     

水化学及硫同位素对大冶矿区地下水硫酸盐污染的指示

铜铁矿区周边地下水硫酸盐污染是生态环境研究关注的热点问题,精确识别硫酸盐来源及迁移途径对于矿区周边地下水污染防控和供水安全至关重要.利用水化学与硫同位素耦合分析,结合矿区水文地质条件和潜在污染源分布,探讨了区内地下水硫酸盐污染特征、来源及迁移途径.区域内地下水包括松散岩类孔隙水、碳酸盐岩裂隙岩溶水及岩浆岩风化裂隙水,水化学类型主要为HCO₃·SO₄-Ca型,水化学组分主要来源于硅酸岩、碳酸盐岩和硫酸盐矿物的溶解以及硫化物氧化;地下水中SO₄^2-含量范围为44.4～2 089.0 mg/L,高值区主要分布在洪山溪尾矿库、矿渣堆存处及矿业生产区附近;地下水中δ³⁴S-SO₄^2-在2.6‰～31.5‰之间,反映其SO₄^2-具有多源性.地下水中SO₄^2-的主要来源包括含水层中石膏矿物的溶解和黄铁矿等含硫矿物氧化输入,高含量的SO₄     

磷灰石对湖泊沉积物中水铁矿稳定性的制约

通过在滇池开展原位实验,研究探讨了湖泊沉积物中磷灰石制约水铁矿分解和转化的机制,以及二者共存时的环境效应。结果表明:将水铁矿放置到沉积物中1个月,矿物保持稳定;放置时间达到3个月时,添加磷灰石实验中水铁矿发生了显著物相转变。冬天(12—2月)实验中,转化产物随深度的变化趋势为针铁矿+磁(赤)铁矿→针铁矿+纤铁矿→针铁矿;夏天(6—9月)实验中,转化产物随深度的变化趋势为针铁矿+纤铁矿+磁(赤)铁矿→针铁矿+纤铁矿→未转化。透射电镜分析结果显示冬天实验中生成的磁性铁氧化物为纳米磁铁矿和磁赤铁矿,夏天实验中产生的则主要为纳米磁铁矿。X射线光电子能谱分析结果显示冬天表层实验样品具有较高P含量。分析表明的湖泊沉积物中磷灰石促进水铁矿转化的过程为:(1)微生物促进磷灰石溶解;(2)磷灰石溶解释放的P促进铁还原菌生长;(3)铁还原菌促进水铁矿还原;(4)水铁矿还原产生的溶解态Fe²⁺催化水铁矿向针铁矿、纤铁矿和磁铁矿转化。冬天及沉积氧化-还原界面最适宜磷灰石分解菌和铁还原菌生长,水铁矿的转化和P释放能力也更强,相应地内源磷释放的风险也更大。     

Mössbauer hyperfine parameters of iron species in the course of <Emphasis Type="Italic">Geobacter</Emphasis>-mediated magnetite mineralization

Amorphous ferric iron species (ferrihydrite or akaganeite of <5 nm in size) is the only known solid ferric iron oxide that can be reductively transformed by dissimilatory iron-reducing bacteria to magnetite completely. The lepidocrocite crystallite can be transformed into magnetite in the presence of abiotic Fe(II) at elevated pH or biogenic Fe(II) with particular growth conditions. The reduction of lepidocrocite by dissimilatory iron-reducing bacteria has been widely investigated showing varying results. Vali et al. (Proc Natl Acad Sci USA 101:16121–16126, 2004) captured a unique biologically mediated mineralization pathway where the amorphous hydrous ferric oxide transformed to lepidocrocite was followed by the complete reduction of lepidocrocite to single-domain magnetite. Here, we report the ⁵⁷Fe Mössbauer hyperfine parameters of the time-course samples reported in Vali et al. (Proc Natl Acad Sci USA 101:16121–16126, 2004). Both the quadrupole splittings and linewidths of Fe(III) ions decrease consistently with the change of aqueous Fe(II) and transformations of mineral phases, showing the Fe(II)-mediated gradual regulation of the distorted coordination polyhedrons of Fe³⁺ during the biomineralization process. The aqueous Fe(II) catalyzes the transformations of Fe(III) minerals but does not enter the mineral structures until the mineralization of magnetite. The simulated abiotic reaction between Fe(II) and lepidocrocite in pH-buffered, anaerobic media shows the simultaneous formation of green rust and its gradual transformation to magnetite plus a small fraction of goethite. We suggested that the dynamics of Fe(II) supply is a critical factor for the mineral transformation in the dissimilatory iron-reducing cultures.     

江汉平原浅层含水层中土著硫酸盐还原菌对砷迁移释放的影响

硫酸盐还原菌是厌氧环境中参与砷形态转化的重要微生物种群,其介导的生物地球化学循环过程对铁氧化物表面吸附态砷迁移转化的影响亟待深入研究.选取江汉平原典型高砷含水层原位沉积物分离纯化出一株严格厌氧硫酸盐还原菌Desulfovibrio JH-S1,对其进行砷和铁还原能力鉴定,并通过模拟培养实验探究硫酸盐还原菌参与下的铁矿物相转化对吸附态砷迁移的影响.Desulfovibrio JH-S1具有Fe(III)还原能力,无硫和有硫体系中Fe(III)均能被还原,但在硫酸盐充足条件下铁还原量显著增加;该菌株不具备As(V)还原能力,但添加硫酸盐的培养体系中As(V)去除率可达96%以上.Desulfovibrio JH-S1能够还原硫酸盐从而促进载砷的水铁矿还原转化为纤铁矿,并导致吸附的砷释放.江汉平原高砷含水层土著硫酸盐还原菌兼具硫酸盐/铁还原功能,参与了高砷含水层系统中砷-铁-硫耦合循环,对高砷地下水的形成具有重要作用.      

海南红树林湿地可培养硫酸盐还原菌的垂直分布特征研究

利用厌氧微生物分离技术,对深度为1.2 m 的海南红树林湿地沉积物钻孔样品进行了分离培养,共获得11 株 厌氧sulfate-reducing bacteria（SRB） 菌株。经显微观察和16S rDNA序列分析,可归纳为6个属,其中已经报道有芽孢杆菌 属（Bacillus）、弧菌属（Vibrio） 和梭状芽胞杆菌属（Clostridium）,另外3个属分别为伯克霍尔德菌属（Burkholderia）、希瓦氏菌属（Shewanella） 和海杆菌属（Marinobacterium）。不同属的细菌对硫酸盐还原的速率最低为14.71%,最高可达 56.78%,并且以上6属11株菌都能将+6价的硫还原生成-2价硫,并与培养基中的Fe2+结合生成黑色FeS沉淀,而这些无定 形FeS沉淀是生成黄铁矿的前体。红树林湿地SRB种群数量随沉积物深度的增加而降低,结合沉积物的地球化学分析测试 结果表明,表层（0 cm） 水界面的沉积物由于处于氧化-还原界面,氧气的周期性输入在一定程度上抑制了SRB的生长;随着 深度增加（10~40 cm）,充足的有机质、偏中性的pH值以及厌氧环境的增强,使得SRB种类和数量明显增加;而60 cm以下 沉积物中因TOC含量降低,减少了微生物可利用的碳源,pH值明显降低,Na+和Ca2+离子浓度明显增加,这些因素都抑制了 SRB的生长,使得深部沉积物中SRB的种类和数量显著减少。     

Arsenic repartitioning during biogenic sulfidization and transformation of ferrihydrite

Iron (hydr)oxides are strong sorbents of arsenic (As) that undergo reductive dissolution and transformation upon reaction with dissolved sulfide. Here we examine the transformation and dissolution of As-bearing ferrihydrite and subsequent As repartitioning amongst secondary phases during biotic sulfate reduction. Columns initially containing As(V)-ferrihydrite coated sand, inoculated with the sulfate reducing bacteria Desulfovibrio vulgaris (Hildenborough), were eluted with artificial groundwater containing sulfate and lactate. Rapid and consistent sulfate reduction coupled with lactate oxidation is observed at low As(V) loading (10% of the adsorption maximum). The dominant Fe solid phase transformation products at low As loading include amorphous FeS within the zone of sulfate reduction (near the inlet of the column) and magnetite downstream where Fe(II)_(aq) concentrations increase; As is displaced from the zone of sulfidogenesis and Fe(III)_(s) depletion. At high As(V) loading (50% of the adsorption maximum), sulfate reduction and lactate oxidation are initially slow but gradually increase over time, and all As(V) is reduced to As(III) by the end of experimentation. With the higher As loading, green rust(s), as opposed to magnetite, is a dominant Fe solid phase product. Independent of loading, As is strongly associated with magnetite and residual ferrihydrite, while being excluded from green rust and iron sulfide. Our observations illustrate that sulfidogenesis occurring in proximity with Fe (hydr)oxides induce Fe solid phase transformation and changes in As partitioning; formation of As sulfide minerals, in particular, is inhibited by reactive Fe(III) or Fe(II) either through sulfide oxidation or complexation.     

Dependence of microbial magnetite formation on humic substance and ferrihydrite concentrations

Iron mineral (trans)formation during microbial Fe(III) reduction is of environmental relevance as it can influence the fate of pollutants such as toxic metal ions or hydrocarbons. Magnetite is an important biomineralization product of microbial iron reduction and influences soil magnetic properties that are used for paleoclimate reconstruction and were suggested to assist in the localization of organic and inorganic pollutants. However, it is not well understood how different concentrations of Fe(III) minerals and humic substances (HS) affect magnetite formation during microbial Fe(III) reduction. We therefore used wet-chemical extractions, magnetic susceptibility measurements and X-ray diffraction analyses to determine systematically how (i) different initial ferrihydrite (FH) concentrations and (ii) different concentrations of HS (i.e. the presence of either only adsorbed HS or adsorbed and dissolved HS) affect magnetite formation during FH reduction by Shewanella oneidensis MR-1. In our experiments magnetite formation did not occur at FH concentrations lower than 5 mM, even though rapid iron reduction took place. At higher FH concentrations a minimum fraction of Fe(II) of 25-30% of the total iron present was necessary to initiate magnetite formation. The Fe(II) fraction at which magnetite formation started decreased with increasing FH concentration, which might be due to aggregation of the FH particles reducing the FH surface area at higher FH concentrations. HS concentrations of 215-393 mg HS/g FH slowed down (at partial FH surface coverage with sorbed HS) or even completely inhibited (at complete FH surface coverage with sorbed HS) magnetite formation due to blocking of surface sites by adsorbed HS. These results indicate the requirement of Fe(II) adsorption to, and subsequent interaction with, the FH surface for the transformation of FH into magnetite. Additionally, we found that the microbially formed magnetite was further reduced by strain MR-1 leading to the formation of either dissolved Fe(II), i.e. Fe²⁺, in HEPES buffered medium or Fe(II) carbonate (siderite) in bicarbonate buffered medium. Besides the different identity of the Fe(II) compound formed at the end of Fe(III) reduction, there was no difference in the maximum rate and extent of microbial iron reduction and magnetite formation during FH reduction in the two buffer systems used. Our findings indicate that microbial magnetite formation during iron reduction depends on the geochemical conditions and can be of minor importance at low FH concentrations or be inhibited by adsorption of HS to the FH surface. Such scenarios could occur in soils with low iron mineral or high organic matter content.     

硫酸盐还原菌的驯化培养及脱硫性能研究

采用单因素法及静态实验法研究驯化所得硫酸盐还原菌(sulfate-reducing bacteria，SRB)，旨在对影响菌群生长的因素及脱硫性能进行分析和研究。结果显示，该菌群属于中温菌，培养与应用均以35C为宜；生长环境酸碱度较宽，适宜的初始pH值为7．5左右；可在较高的氯化钠浓度下生存，适宜的浓度范围为10%左右。同时，脱硫实验表明菌的脱硫性能和硫酸根离子的去除率随硫酸根浓度的增加逐渐降低     

The mineralogic transformation of ferrihydrite induced by heterogeneous reaction with bioreduced anthraquinone disulfonate (AQDS) and the role of phosphate

Bioreduced anthraquinone-2,6-disulfonate (AH₂DS; dihydro-anthraquinone) was reacted with a 2-line, Si-substituted ferrihydrite under anoxic conditions at neutral pH in PIPES buffer. Phosphate (P) and bicarbonate (C); common adsorptive oxyanions and media/buffer components known to effect ferrihydrite mineralization; and Fe(II)_aq (as a catalytic mineralization agent) were used in comparative experiments. Heterogeneous AH₂DS oxidation coupled with Fe(III) reduction occurred within 0.13-1 day, with mineralogic transformation occurring thereafter. The product suite included lepidocrocite, goethite, and/or magnetite, with proportions varing with reductant:oxidant ratio (r:o) and the presence of P or C. Lepidocrocite was the primary product at low r:o in the absence of P or C, with evidence for multiple formation pathways. Phosphate inhibited reductive recrystallization, while C promoted goethite formation. Stoichiometric magnetite was the sole product at higher r:o in the absence and presence of P. Lepidocrocite was the primary mineralization product in the Fe(II)_aq system, with magnetite observed at near equal amounts when Fe(II) was high [Fe(II)/Fe(III)] = 0.5 and P was absent. P had a greater effect on reductive mineralization in the Fe(II)_aq system, while AQDS was more effective than Fe(II)_aq in promoting magnetite formation. The mineral products of the direct AH₂DS-driven reductive reaction are different from those observed in AH₂DS-ferrihydite systems with metal reducing bacteria, particularly in presence of P.     

泥炭中厌氧细菌的数量分布及其地质意义

在严格厌氧条件下,分别用滚管计数法和MPN计数法测定了不同环境泥炭样品中的发酵型细菌,硫酸盐还原细菌和厌氧纤维素分解细菌的数量与分布,并考察了产甲烷细菌的存在与活性,同时分析了这四种细菌类群相应的地质意义。实验结果表明,在泥炭中发酵型细菌数量与有机质的含量特别是腐殖酸含量具有正相关性;硫酸盐还原细菌数量与硫酸盐含量之间的关系并不明显,与样品埋藏深度具有一定负相关性,硫酸盐还原细菌数量与硫酸盐含量的最小值均出现在泥炭层最底层;厌氧纤维素分解菌只在少数样品中检测到,而产甲烷细菌广泛存在于所有样品中,且可以与硫酸盐还原细菌共存于许多样品中。     

Nitrite reduction by Fe(II) associated with kaolinite

Interactions of iron (Fe) with the nitrogen (N) cycle have emerged and contain elements of abiotic and biological reactions. One such abiotic reaction which has received little study is the reactivity of NO₂ ^? and Fe(II) associated with a major clay mineral, kaolinite. The main objective of this study was to evaluate the reactivity of NO₂ ^? with Fe(II) added to kaolinite under anoxic conditions. Stirred batch reactivity experiments were carried out with 10 g L^?1 kaolinite spiked with 25 and 100 µM Fe(II) at pH 6.45 in an anaerobic chamber. Approximately 500 µM NO₂ ^? was added to initiate the reaction with Fe(II)-loaded kaolinite. The rate of nitrite removal from solution was 2.4-fold slower in the high Fe(II) treatment when compared with the low Fe(II) treatment. A large portion of the NO₂ ^? removed from solution was confirmed to be reduced to N₂O_(g) in the Fe(II)-kaolinite slurries. However, NO₂ ^? reduction was also noticed in the presence of kaolinite-alone and to somewhat lesser extent in the presence of dithionite-citrate-bicarbonate (DCB)-treated kaolinite. Chemical extractions coupled with infrared spectroscopy suggest that Fe(III) oxide mineral impurities and structural Fe(III) in kaolinite may participate in NO₂ ^? removal from solution. Furthermore, a magnetite mineral was identified based on X-ray diffraction analysis of untreated kaolinite and DCB-treated kaolinite. Our findings reveal a novel pathway of NO₂ ^? transformation in the environment in the presence of Fe(II) associated (sorbed and impurity) with kaolinite.