固定化硫酸盐还原菌处理含铊废水效果及其解毒机制
Effect and detoxification mechanism for treating wastewater containing thallium by immobilized sulfate reducing bacteria
-
摘要: 生物固定化是一种新型防控水源地水体重金属污染技术.实验采用固定化硫酸盐还原菌(SRB)处理含铊废水,并研究了SRB处理含铊废水的机理.研究结果表明,包埋后SRB仍能够保持较强活性,pH和接触时间对固定化SRB处理含铊废水具有较大影响,包埋小球pH耐受性较好,最适pH值是6,处理在720min达到饱和量.菌液包埋量和废水中硫酸根离子浓度对固定化处理含铊废水作用重要,处理量高达253.94 μg·g-1.采用EDS和XRD分析了反应体系中沉淀物的组成,表明溶液和小球沉淀物中均含有硫化铊,硫化铊沉淀是固定化SRB处理含铊废水过程中铊污染去除的重要机制,固定化SRB可有效防控水源地铊污染.Abstract: Biological immobilization is a new method for the prevention and control of heavy metal pollution in the water source areas. In this study, ilumobilized sulfate reducing bacteria (SRB) was used to treat wastewater containing thallium, and the main mechanism of thallium removal was studied. The results indicate that the SRB retained its activity after immobilization, and pH and contact time had great impact on thallium removal. The beads had great tolerance to pH change, and the optimum value is 6. Saturated amount was reached at 720 min. The amount of bacteria entrapped and concentration of sulfate in wastewater played key roles in the process of treating thallium by immobilized SRB, and the max treatment amount of thallium was up to 253.94 μg·g-1. The composition of precipitation in the immobilized SRB system was analyzed by energy dispersive spectrometer (EDS) and X-ray diffraction (XRD). It was revealed that thallium sulfide existed in the precipitation of the solution and beads. Precipitation of thallium sulfide was the important mechanism for thallium removal during the course of treating wastewater containing thallium by the beads of immobilized SRB. Immobilized SRB can effectively prevent and control thallium pollution in water source areas.
-
Key words:
- immobilized SRB /
- toxicity /
- mechanism /
- precipitation
-
[1] XIAO T, GUHA J, BOYLE D, et al. Naturally occurring thallium:A hidden geoenvironmental health hazard?[J]. Environ Int, 2004,30:501-507 [2] JOHN PETER A L, VIRARAGHAVAN T. Thallium:A review of public health and environmental concerns[J]. Environment International, 2005, 31:493-501. [3] YANG C X, CHEN Y H, PENG P A, et al. Distribution of natural and anthropogenic thallium in highly weathered soils[J]. The Science of Total Environment, 2005, 341:159-172. [4] Twidwell L G, Williams-Beam C. Potential technologies for removing thallium from mine and process wastewater:An annotation of the literature[J]. Euro-Miner Process Environ Prot 2002,2:1-10. [5] 刘敬勇,常向阳,涂湘林.重金属铊污染及防治对策研究进展[J]. 土壤,2007,39(4):528-535. LIU J Y, CHANG X Y, TU X L. Thallium pollution and its countermeasures[J]. Soils,2007,39(4):528-535(in Chinese).
[6] ZHANG L, HUANG T, ZHANG M, et al. Studies on the capability and behavior of adsorption of thallium on nano-Al2O3[J]. Journal of Hazardous Materials, 2008, 157:352-357. [7] 孙嘉龙,肖唐付,周连碧,等.铊矿山废水的微生物絮凝处理研究[J]. 地球与环境, 2010,38(3):383-385. SUN J L, XIAO T F, ZHOU L B, et al. Bioflocculant treatment of mine water from tl mineralized area[J]. Earth and Environment, 2010,38(3):383-385(in Chinese).
[8] QIN Z, CHEN Y, MING Y, et al. Enhanced bioremediation of heavy metal from effluent by sulfate-reducing bacteria with copper-iron bimetallic particles support[J]. Bioresource Technology, 2013, 136(5):413-417. [9] 陈炜婷,张鸿郭,陈永亨,等. pH、温度及初始铊浓度对硫酸盐还原菌脱铊的影响[J].环境工程学报,2014,8(10):4105-4109. CHEN W T, ZHANG H G, CHEN Y H, et al. Effect of pH, temperature and initial concentration on thallium removal by sulfate-reducing bacteria[J]. Chinese Journal of Environmental Engineering,2014,8(10):4105-4109(in Chinese).
[10] WANNARAK N, PARICHAT N, ONRUTHAL P. Diesel oil removal by immobilized Pseudoxanthomonas sp. RN402[J].Biodegradation, 2013,24(3):386-397. [11] 俞毓馨,吴国庆,孟宪庭,等.环境工程微生物检验手册[M].北京:中国环境科学出版社,1990:163-165. YU Y X, WU G Q, MENG X T, et al. Environmental engineering microbiology examination handbook[M]. Beijing:China Environmental Science Press, 1990:163 -165(in Chinese).
[12] MANSOUR M, OSSMAN M, FARAG H. Removal of Cd (Ⅱ) ion from waste water by adsorption onto polyaniline coated on sawdust[J]. Desalination,2011,272(1):301-305. [13] PARK Y J, KO J J, YUN S L, et al. Enhancement of bioremediation by Ralstonia sp. HM-1 in sediment polluted by Cd and Zn[J]. Bioresource Technology,2008,99(16):7458-7463. [14] XU X Q, LI X M, YANG L, et al.Biosorption of lead and copper ions by penicillium simplicissimum immobilized on a loofa sponge immobilized biomass[J].Acta Scientiae Circumstantia, 2008,28(1):95-100. [15] CAO J Y, ZHANG G J, MAO Z S, et al. Influence of Mg2+ on the growth and activity of sulfate reducing bacteria[J]. Hydrometallurgy, 2009, 95(1-2):127-134. [16] ZAGURY G J, KULNIEKS V I, NECULITA C M. Characterization and reactivity assessment of organic substrates for sulphate-reducing bacteria in acid-mine drainage treatment[J]. Chemosphere,2006, 64(6):944-954. [17] MIN X B, CHAI L Y, ZHANG C F, et al. Control of metal toxicity, effluent COD and regeneration of gel beads by immobilized sulfate-reducing bacteria[J].Chemosphere,2008,72(7):1086-1091. [18] FANG D, ZHANG R, LIU X, et al. Selective recovery of soil-borne metal contaminants through integrated solubilization by biogenic sulfuric acid and precipitation by biogenic sulfide[J]. Journal of Hazardous Materials, 2012, 219-220(12):119-126. [19] CHEN J H,NI J C, LIU Q L, et al. Adsorption behavior of Cd(Ⅱ) ions on humic acid-immobilized sodium alginate and hydroxyl ethyl cellulose blending porous composite membrane adsorption[J]. Desalination,2012,285(31):54-61.
计量
- 文章访问数: 1060
- HTML全文浏览数: 1016
- PDF下载数: 400
- 施引文献: 0