Catalytic oxidation effect of MnSO4 on As(III) by air in alkaline solution

The catalytic oxidation effect of MnSO₄ on As(III) by air in an alkaline solution was investigated. According to the X-ray diffraction (XRD), scanning electron microscope-energy dispersive spectrometer (SEM-EDS) and X-ray photoelectron spectroscopy (XPS) analysis results of the product, it was shown that the introduction of MnSO₄ in the form of solution would generate Na_0.55Mn₂O₄·1.5H₂O with strong catalytic oxidation ability in the aerobic alkaline solution, whereas the catalytic effect of the other product MnOOH is not satisfactory. Under the optimal reaction conditions of temperature 90°C, As/Mn molar ratio 12.74:1, air flow rate 1.0 L/min, and stirring speed 300 r/min, As(III) can be completely oxidized after 2 hr reaction. The excellent catalytic oxidation ability of MnSO₄ on As(III) was mainly attributed to the indirect oxidation of As(III) by the product Na_0.55Mn₂O₄·1.5H₂O. This study shows a convenient and efficient process for the oxidation of As(III) in alkali solutions, which has potential application value for the pre-oxidation of arsenic-containing solution or the detoxification of As(III).     

石油污染生物修复技术研究

本文概述了影响石油污染物生物降解修复处理的多种因素，对石油污染生物处理技术的发展进行了展望。其中主要影响因素包括：菌种的影响，菌种在不同的环境中和对不同碳链长度的碳氢化合物表现出不同的降解效率；石油物质本身物理化学特性的影响，如石油物质在水体或土壤中的浓度以及石油的粘度、沸点、折射率等特性；生存环境条件的影响，在接种入高效率的降解菌或利用土著微生物进行降解时，降解率受到生存环境中各种条件的影响，如表面活性剂、光照条件、吸附剂的利用、营养盐、共代谢底物、氧气、温度、盐度等。     

石油污染土壤生物修复技术的研究进展

目前对石油污染环境的治理方法有物理法、化学法和生物修复三种类型。文章综合论述了国内外对石油污染土壤的几种微生物修复方法,分别介绍了利用植物、动物及微生物进行治理的修复技术。在我国,对于石油污染的治理应更多地采用低成本、无污染、高效率的生物治理技术。     

Arsenic biotransformation and an arsenite S-adenosylmethionine methyltransferase in plankton

<正>Arsenic(As)is a well-recognized toxicant and carcinogen.Chronic exposure to inorganic arsenic causes a range of human cancers(e.g.,skin,bladder,and lung)and increases the risk of developing diabetes,hypertension,and cardiovascular and neurological diseases.The prevalence of arsenic species and the severity of their health effects continue to drive and demand for extensive research(Carlin et al.,2016).     

华南某金矿下游河道砷镉分布特征

对华南某金矿下游河道砷、镉分布特征进行了初步研究,在金矿下游河道沿程布设7个沉积物采样点及两个河道断面,分析了沉积物及断面土壤的砷、镉、铬、铜、镍、铅、锌含量。采用Tessier连续提取法分析沉积物中砷、镉等重金属的形态。砷含量高达10 208⁷0 621 mg/kg,镉含量达2.870 621 mg/kg,镉含量达2.8¹0.2 mg/kg。沉积物中砷、铅元素含量沿水流方向总体呈现减少趋势,铬、铜元素含量沿水流方向呈现增加趋势,镉元素含量沿水流方向先增加后减少。上游断面沉积物砷、镉等重金属浓度由河流中泓线向河岸方向增加,砷含量由16 617 mg/kg增加至53 197 mg/kg;下游断面则反之,砷含量由16 860 mg/kg减少至384mg/kg。沉积物中砷、镉等重金属元素主要以铁锰氧化态、有机结合态和残渣态的形式存在。     

复合微生物菌剂在近海污水中的修复作用研究

采用直接投加复合微生物菌剂原位修复深圳湾污染水体,去除水体中的有机物、氮和磷等污染物,15天检测分析微生物处理对水体溶解氧（DO）、氨态氮（NH4-N）、悬浮物（SS）、总氮（TN）、总磷（TP）变化的影响。结果表明：采用微生物技术修复深圳湾近海污染水环境具有显著效果,试验期间水体中DO明显提高,最佳复配硝化茵（B2）与枯草芽孢杆菌（B6）对NH4-N降低了53．9％,悬浮物（ss）降低了56．9％,总氮（TN）降低52．1％,总磷（TP）降低57．6％。有害弧菌单一菌落数降低了64．9％     

宏基因组技术在土壤污染微生物修复中的应用

微生物修复在土壤污染治理中具有重要地位。虽然环境中可以培养的微生物比例很低,但微生物的基因资源十分丰富,运用宏基因组技术可以克服传统修复技术中微生物资源利用不充分的问题,为未培养微生物的研究提供了有力手段。本文对宏基因组技术一般流程作了介绍,并结合土壤污染的特点,对该技术应用在土壤污染微生物修复的现状、研究及展望作了阐述。     

电动生物修复湖泊底泥中直链烷基苯磺酸钠

直链烷基苯磺酸钠(Linear Alkylbenzene Sulfonates,LAS)是环境中最常见的具有代表性的一类有机污染物,城市湖泊长期以来接纳了大量的污染物,致使底泥沉积了大最的LAS.采用电动生物复合技术修复东湖底泥中LAS,由于其LAS含量过高,当直接添加芽孢杆菌降解LAS时,发现无明显的降解效果.经过驯...     

土壤重金属污染的生物修复技术

随着城市化和工业化的加速,土壤的重金属污染问题日趋严重。生物修复技术作为一种环境友好型治理措施越来越受到关注,其主体主要包括植物修复、动物修复以及微生物修复。文章首先综述了生物修复土壤重金属污染的机理及其研究进展,其中植物修复包括降解、提取、挥发、根系钝化以及固定等,而微生物修复机理主要包括生物富集、生物吸着以及生物转化;其次分析了生物修复技术的局限性,如超富集植物积累重金属的单一性,植物的生长速度慢、积累效率低、适应性弱,微生物的种间拮抗作用等;最后对其发展前景提出展望,认为通过加强国际交流,重视多学科的交叉应用,以及合理配置人才与资源等措施,有利于突破技术瓶颈,发展出更具应用价值的复合修复技术。     

Antimony smelting process generating solid wastes and dust：Characterization and leaching behaviors

A large amount of solid waste has been produced by the antimony smelting process in the＂World Capital of Antimony＂, Xikuangshan area in China. This study comprehensively investigated the physical and chemical characteristics of the various solid wastes, as well as the leaching behavior of the solid wastes, which included water-quenched slag,arsenic-alkali residue, desulfurized slag and blast furnace dust. These four types of waste were enriched in a variety of heavy metals and metalloids and more specifically with As and Sb levels up to 8.6 × 104 and 3.16 × 105mg/kg, respectively, in arsenic-alkali residue. For desulfurized slag and water-quenched slag, the leaching concentration of Sb significantly exceeded the acceptable limits during the leaching tests using the toxicity characteristic leaching procedure and the synthetic precipitation leaching procedure. In addition, As leaching in arsenic-alkali residue was extraordinarily hazardous, being three orders of magnitude higher than the regulatory level of As. According to the results of the extraction tests, all the tested wastes were classified as hazardous waste.