|
|
Effect of Wuliangsuhai iron-reducing microorganisms on the migration and transformation of As-P |
SHI Wen-jing, LIU Yi-zhe, XU Hao-ran, LI Wei-ping |
Collaborative Innovation Center for Ecological Protection and Comprehensive Utilization of the Inner Mongolia Section of the Yellow River Basin, School of Energy and Environment, Inner Mongolia University of Science &Technology, Baotou 014010, China |
|
|
Abstract This study taken Wuliangsuhai Lake as the research object to reveal the microbial community structure of lake sediments, elucidated the representative iron-reducing microorganisms and their abundance, investigated the seasonal differences in the impact of iron-reducing microorganisms on As-P migration and transformation during the ice-bound period and the summer, and the impact of P on As migration and transformation, with the aim of providing a basis for deepening the understanding of the environmental geochemical behavior of As in cold and arid regions and As pollution remediation, and providing reference for the water environmental protection of As pollution and eutrophication risks in dual-risk lakes. The results showed that the relative abundance of iron-reducing microorganisms during the ice-bound period was higher than that in summer. There were seasonal differences in the representative iron-reducing microorganisms. Bacillus and Geobacter were the dominant genera of iron-reducing microorganisms during the ice-bound period and summer, but Geothrix was also one of the representative iron-reducing microorganisms in summer, and Shiwanella was one of the representative iron-reducing microorganisms during the ice-bound period. The correlation analysis and PLS-SEM model results showed that the representative iron-reducing microorganisms that play a major driving role in As-P migration and transformation and their impact on As-P migration and transformation exist significant seasonal differences. In summer, although the abundance of Thermoanaerobium was small, the iron-reduction process driven by Thermoanaerobium (path coefficient=0.178) would affect the release of As and P from sediments to water to a certain extent. In addition, Bacillus could also promote the iron-reduction process (Path coefficient=0.115) and was the main driver of As-P mobility and transformation. During the ice-bound period, the more abundant Geobacter was an important driver (path coefficient=0.530) of As mobility, which had an important effect on the mobility and transformation of As-P, and the effect of Thermoanaerobium on iron reduction (Path coefficient=0.284) and As-P mobility and transformation was greater than in summer (path coefficient=0.178).
|
Received: 30 August 2024
|
|
Corresponding Authors:
李卫平,教授,sjlwp@163.com
E-mail: sjlwp@163.com
|
|
|
|
[1] Long H, Sun Y, Li Z, et al. Beyond the geological origin of sediment arsenic in groundwater systems:Arsenic redux by redox[J]. Science Bulletin, 2023,68(15):1616-1620. [2] Michael H. An arsenic forecast for China[J]. Science, 2013,341(6148):852-853. [3] Anawar H, Akai J, Mihaljevic M, et al. Arsenic contamination in groundwater of Bangladesh:Perspectives on geochemical, microbial and anthropogenic issues[J]. Water, 2011,3(4):1050-1076. [4] Gorra R, Webster G, Martin M, et al. Dynamic microbial community associated with iron-arsenic co-precipitation products from a groundwater storage system in Bangladesh[J]. Microbial Ecology, 2012,64(1):171-186. [5] 刘韩.河套平原高砷地下水中异化铁还原菌对砷迁移转化的影响研究[D].武汉:中国地质大学, 2021. Liu H. Arsenic mobilization affected by dissimilatory iron reducing bacteria from high arsenic groundwater in Hetao Basin[D]. Wuhan:China University of Geosciences, 2021. [6] Deng Y, Zheng T, Wang Y, et al. Effect of microbially mediated iron mineral transformation on temporal variation of arsenic in the Pleistocene aquifers of the central Yangtze River basin[J]. Science of the Total Environment, 2018,619:1247-1258. [7] Campbell K,Malasarn D,Saltikov C,et al. Simultaneous microbial reduction of iron (Ⅲ) and arsenic (V) in suspensions of hydrous ferric oxide[J]. Environmental Science and Technology, 2006,40(19):5950-5955. [8] Wu X, Jiang Q, Ma T. Geochemical processes of phosphorus‑iron on sediment-water interface during discharge of groundwater to freshwater lakes:Kinetic and mechanistic insights[J]. Science of the Total Environment, 2023,901:165962. [9] 郭华明,王焰新,李永敏.山阴水砷中毒区地下水砷的富集因素分析[J].环境科学, 2003,24(4):60-67. Guo H, Wang Y, Li Y. Analysis of factors influencing arsenic enrichment in groundwater in the Shanxi arsenic poisoning area[J]. Environmental Science, 2003,24(4):60-67. [10] 杨桂山,马荣华,张路,等.中国湖泊现状及面临的重大问题与保护策略[J].湖泊科学, 2010,22(6):799-810. Yang G, Ma R, Zhang L, et al. Current status, major issues, and protection strategies of lakes in China[J]. Journal of Lake Sciences, 2010,22(6):799-810. [11] 刘帅,谢茂嵘,吕文,等.阳澄湖入湖河道分类、污染特征分析及治理策略[J].湖泊科学, 2024,36(3):741-755. Liu S, Xie M, Lu W, et al. Classification, pollution characteristics and treatment strategy of the inflow rivers into Lake Yangcheng[J]. Journal of Lake Sciences, 2024,36(3):741-755. [12] 杨安,邢文聪,王小霞等.西藏中部河流、湖泊表层沉积物及其周边土壤重金属来源解析及风险评价[J].中国环境科学, 2020,40(10):4557-4567. Yang A, Xing W, Wang X, et al. Source and risk assessment of heavy metals in surface sediments of rivers, lakes and their surrounding soils in central Tibet[J]. China Environmental Science, 2020,40(10):4557-4567. [13] 史锐,毛若愚,张梦,等.乌梁素海流域地表水中全氟化合物分布、来源及其生态风险[J].环境科学, 2021,42(2):663-672. Shi R, Mao R, Zhang M, et al. Distribution, sources, and ecological risks of polyfluoroalkyl substances in the surface water of the Wuliangsuhai Watershed[J]. Environmental Science, 2021,42(2):663-672. [14] 何连生,席北斗,雷宏军,等.2013乌梁素海综合治理规划研究[M].北京:中国环境出版社, 2013:1-105. He L, Xi B, Lei H, et al. Study on the comprehensive management plan of Wuliangsuhai Lake in 2013[M]. Beijing:China Environmental Science Press, 2013:1-105. [15] 李磊.内蒙古高原湖泊铁的地球化学特征与环境意义[D].呼和浩特:内蒙古大学, 2017. Li L. Geochemical characteristics and environmental significance of iron fractions in lake sediments on the western inner mongolia plateau[D]. Hohhot:Inner Mongolia University, 2017. [16] 石文静,赵心亚,刘轶哲,等.乌梁素海冰封期砷与环境因子响应及风险评价[J].中国环境科学, 2024,44(2):972-983. Shi W, Zhao X, Liu Y, et al. Response between arsenic and environmental factors and risk assessment in Wuliangsuhai during the ice-bound period[J]. China Environmental Science, 2024,44(2):972-983. [17] 崔志谋,史小红,赵胜男,等.基于PCA-APCS-MLR模型的乌梁素海表层沉积物重金属时空分布及来源解析[J].环境科学, 2024,45(3):1415-1427. Cui Z, Shi X, Zhao S, et al. Spatiotemporal distribution and dource analysis of heavy metals in surface sediments in lake Ulansuhai based on PCA-APCS-MLR model[J]. Environmental Science, 2024,45(3):1415-1427. [18] Yamaguchi N, Nakamura T, Dong D, et al. Arsenic release from flooded paddy soils is influenced by speciation, Eh, pH, and iron dissolution[J]. Chemosphere, 2011,83(7):925-932. [19] Bennett W W, Teasdale P R, Panther J G, et al. Investigating arsenic speciation and mobilization in sediments with DGT and DET:A mesocosm evaluation of oxic-anoxic transitions[J]. Environmental Science& Technology, 2012,46(7):3981-3989. [20] 钟松雄,尹光彩,陈志良,等.Eh,pH和铁对水稻土砷释放的影响机制[J].环境科学, 2017,38(6):2530-2537. Zhong S, Yin G, Chen N et al. Influencing mechanism of Eh, pH and iron on the release of arsenic in paddy soil[J]. Environmental Science, 2017,38(6):2530-2537. [21] 周月雯.砷钼蓝法测定三价砷和五价砷[J].环境保护科学, 1990,(4):45-47. Zhou Y. Determination of trivalent and pentavalent arsenic using arsenic molybdenum blue method[J]. Environmental Protection Science, 1990,(4):45-47. [22] Li Y, Yu C, Zhao B, et al. Spatial variation in dissolved phosphorus and interactions with arsenic in response to changing redox conditions in floodplain aquifers of the Hetao Basin, Inner Mongolia[J]. Water Research, 2022,209. [23] 国家环境保护总局水和废水监测分析方法编委会.水和废水监测分析方法(第四版)[M].北京:中国环境科学出版社, 2002. Editorial Committee of Monitoring and Analysis Methods of Water and Wastewater, State Environmental Protection Administration. Monitoring and analysis methods of water and wastewater[M]. 4th Ed. Beijing:China Environmental Science Press, 2002. [24] 杨娅婷.冰封/非冰封期不同类型湖泊菌藻群落特征及差异性研究[D].包头:内蒙古科技大学, 2023. Yang Y. Characteristics and differences of bacterial and algal communities in different lakes during freezing and non freezing period[D]. Baotou:Inner Mongolia University of Science and Technology, 2023. [25] 邢奕,司艳晓,洪晨,等.铁矿区重金属污染对土壤微生物群落变化的影响[J].环境科学研究, 2013,26(11):1201-1211. Xing Y, Si, Hong C, et al. Impact of long-term heavy metal pollution on microbial community in iron mine soil[J]. Research of Environmental Sciences, 2013,26(11):1201-1211. [26] 于玲红,齐璐,杨文焕,等.包头南海湖冰封期沉积物细菌群落多样性[J].环境化学, 2019,38(6):8. Yu L, Qi L, Yang W, et al. Diversity of bacterial communities in the sediment of Baotou Nanhai Lake in ice period[J]. Environmental Chemistry, 2019,38(6):1348-1355. [27] 刘璐,刘星,靖宪月,等.地杆菌:驱动厌氧生物地球化学循环的"多面手"[J].微生物学报, 2022,62(6):2277-2288. Liu L, Liu X, Jing X, et al. Geoabcter:The"generalist"driving anaerobic biogeochemical cycles. Acta Microbiologica Sinica, 2022, 62(6):2277-2288. [28] Lin B, Hyacinthe C, Bonneville S, et al. Phylogenetic and physiological diversity of dissimilatory ferric iron reducers in sediments of the polluted Scheldt estuary, Northwest Europe[J]. Environmental Microbiology, 2007,9(8):1956-1968. [29] Laursen B,Bay L,Cleenwerck I,et al.Carnobacterium divergens and Carnobacterium maltaromaticum as spoilers or protective cultures in meat and seafood:phenotypic and genotypic characterization[J]. Systematic and Applied Microbiology, 2005,28(2):151-164. [30] Nayak S K,Maji P.Physiological characteristics of Bacillus species and their potential applications in agriculture[J]. Biocontrol Science and Technology, 2020,30(2):123-140. [31] Makkar R, Cameotra S. Production of biosurfactant at mesophilic and thermophilic conditions by a strain of Bacillus subtilis[J]. Journal of Industrial Microbiology& Biotechnology, 1998,20(1):48-52. [32] 杜彩丽,黎佳茜,李国文,等.乌梁素海表层沉积物中营养盐和重金属分布特征以及风险评价[J].环境科学, 2022,43(12):5598-5607. Du C, Li J, Li G, et al. Distribution and risk assessment on the nutrients and heavy metals in surface sediments of Wuliangsuhai lake[J]. Environmental Science, 2022,43(12):5598-5607. [33] Fan L, Zhao F, Liu J, et al. The As behavior of natural arsenical-containing colloidal ferric oxyhydroxide reacted with Sulfate Reducing Bacteria[J]. Chemical Engineering Journal, 2017:S1385894717315772. [34] Lu C, He J, Zuo L, et al. Processes and their explanatory factors governing distribution of organic phosphorous pools in lake sediments[J]. Chemosphere, 2016,145(FEB.):125-134. [35] Zhu J, Yan X, Zhou L,et al.Insight of bacteria and archaea in Feammox community enriched from different soils[J]. Environmental research, 2022,203:111802. [36] Huang L,Feng C,Jiang H,et al. Reduction of structural Fe (III) in nontronite by thermophilic microbial consortia enriched from hot springs in Tengchong, Yunnan Province, China. Chemical Geology, 2018,(479):47-57. [37] Qiao J, Li X, Hu M, et al. Transcriptional activity of arsenic-reducing bacteria and genes regulated by lactate and biochar during arsenic transformation in flooded paddy soil[J]. Environmental Science& Technology, 2018,52(1):61-70. [38] Qiao J, Li X, Li F. Roles of different active metal-reducing bacteria in arsenic release from arsenic-contaminated paddy soil amended with biochar[J]. Journal of Hazardous Materials, 2018,344:958-967. [39] 贾蓉,曲东,乔莎莎.发酵脱氢产氢过程对微生物铁还原的影响[J].农业环境科学学报, 2012,32(12):2395-2402. Jia R, Qu D, Qiao S. Microbial iron reduction as influenced by fermentative dehydrogenation and hydrogen production[J]. Journal of Agro-Environment Science, 2012,32(12):2395-2402. [40] Giri A K, Patel R k,Mahapatra S S.Artificial neural network (ANN) approach for modelling of arsenic (III) biosorption from aqueous solution by living cells of Bacillus cereus biomass[J]. Chemical Engineering Journal, 2011,178(24):15-25. [41] 司慧.芽孢杆菌对铀、锰、砷富集植物体的减容机理研究[D].绵阳:西南科技大学, 2017. Si H. Study on the mechanism of reducing of Bacaillus to the U, Mn, As enrichment plants[D]. Mianyang:Southwest University of Science and Technology, 2017. [42] 邓博環,许丽英,王玉龙,等.一株芽孢杆菌对含砷矿物中砷的还原作用[J].生态学杂志, 2016,35(12):3374-3381. Deng B, Xu L, Wang Y, et al. Reduction of arsenic in arsenic bearing minerals by a Bacillus strain[J]. Chinese Journal of Ecology, 2016, 35(12):3374-3381. [43] 陈优阳.富氮生物炭对福州平原稻田土壤铁动态与碳释放的影响[D].福州:福建师范大学, 2020. Chen Y. Effects of nitrogen-rich biochar on soil iron dynamics and carbon release in paddy field of Fuzhou Plain[D]. Fuzhou:Fujian Normal University, 2020. [44] 林颖.水稻根际土壤铁还原微生物的丰度及多样性变化特征[D].杨凌:西北农林科技大学, 2019. Lin Y. Changing characteristics of iron-reducing microbial abundance and diversity in paddy rhizosphere soil[D]. Yangling:Northwest A&F University, 2019. [45] Lovley D, Holmes D, Nevin K. Dissimilatory Fe (III) and Mn (IV) reduction[J]. Advances in Microbial Physiology, 2004,49:219-286. [46] Antonio García-Moyano, Elena González-Toril, Aguilera N, et al. Comparative microbial ecology study of the sediments and the water column of the Río Tinto, an extreme acidic environment[J]. FEMS Microbiology Ecology, 2012,81(2):1-12. [47] Gonzalez-Toril E,Aguilera A,Souza-Egipsy V,et al.Geomicrobiology of La Zarza-perrunal acid mine effluent (Iberian Pyritic Belt, Spain)[J]. Applied& Environmental Microbiology, 2011,77(8):2685-2694. [48] 罗晓佼,张钘,黄伟,等.三峡库区澎溪河河段间水华程度差异及其机制[J].环境科学, 2023,44(1):282-292. Luo X, Zhang X, Huang W, et al. Severity differences and mechanisms of algal blooms among sections in Pengxi River of the three gorges reservoir[J]. Environmental Science, 2023,44(1):282-292. [49] 朱鹏航,于瑞宏,葛铮,等.乌梁素海长时序水质变化及其驱动因子[J].生态学杂志, 2022,41(3):546-553. Zhu P, Yu R, Ge Z, et al. Long-term changes of water quality and the driving factors of Wuliangsuhai Lake. Chinese Journal of Ecology, 2022,41(3):546-553. |
|
|
|