生物炭及其水溶组分促进水铁矿微生物还原

夏金霞, 孙金涛, 于蕊, 王一初, 安伟奇, 金洁, 曹丹丹

中国环境科学 ›› 2023, Vol. 43 ›› Issue (10) : 5422-5432.

PDF(1743 KB)
PDF(1743 KB)
中国环境科学 ›› 2023, Vol. 43 ›› Issue (10) : 5422-5432.
环境生态

生物炭及其水溶组分促进水铁矿微生物还原

  • 夏金霞, 孙金涛, 于蕊, 王一初, 安伟奇, 金洁, 曹丹丹
作者信息 +

Effects of biochar and its dissolved fractions on microbial reduction of ferrihydrite

  • XIA Jin-xia, SUN Jin-tao, YU Rui, WANG Yi-chu, AN Wei-qi, JIN Jie, CAO Dan-dan
Author information +
文章历史 +

摘要

采用水稻秸秆在300, 400和500℃热解温度下制备生物炭(BC),并从中提取生物炭水溶组分(DBC),结合微生物还原实验和傅里叶转换红外光谱仪(FTIR)、X射线衍射晶体衍射(XRD)、电子顺磁(EPR)等表征手段考察BC和DBC对Geobacter sulphurreducens PCA还原水铁矿的影响和作用机制.结果表明,400℃热解BC可使微生物异化铁还原的速率增加12倍,还原率最高,这是由于其含有最多的醌基、羧基基团,可以作为电子穿梭体促进电子转移. BC不能作为电子供体直接向微生物或水铁矿提供电子. DBC使水铁矿的长期微生物异化铁还原程度和初始还原速率分别增加了10倍和2倍以上. 500℃热解DBC可以充当电子供体或者电子穿梭体,促进水铁矿的微生物还原,但是不能直接化学还原水铁矿.

Abstract

In this study, biochar (BC) was prepared from rice straw at different pyrolysis temperatures (300, 400, and 500℃), and was used for dissolved fractions (DBC) extraction. In this study, the effects of BC and DBC on the reduction of ferrihydrite by Geobacter sulphurreducens PCA were investigated by combining microbial reduction experiments and various characterization methods including Fourier transition infrared spectroscopy (FTIR), X-ray diffraction crystal diffraction (XRD), and Electron paramagnetic resonance (EPR). The results showed that the highest reduction rate of ferrihydrite was achieved after the addition of BC prepared at 400℃ (BC-400), which increased the rate of microbial dissimilatory iron reduction by 12 times. Containing the most quinone and carboxyl groups, BC-400 could function as an electron shuttle to promote electron transfer. BC could not serve as an electron donor to provide electrons directly to PCA or ferrihydrite. DBC increased the degree of long-term microbial reduction extent and initial reduction rate by more than 10 times and 2 times, respectively. DBC extracted from BC prepared at 500℃ served as an both electron shuttle and electron donor to promote the microbial reduction of ferrihydrite, but it cannot directly chemically reduce ferrihydrite.

关键词

生物炭 / 生物炭水溶组分 / 水铁矿 / 异化铁还原菌

Key words

biochar / dissimilatory iron-reducing bacteria / dissolved biochar fractions / ferrihydrite

引用本文

导出引用
夏金霞, 孙金涛, 于蕊, 王一初, 安伟奇, 金洁, 曹丹丹. 生物炭及其水溶组分促进水铁矿微生物还原[J]. 中国环境科学. 2023, 43(10): 5422-5432
XIA Jin-xia, SUN Jin-tao, YU Rui, WANG Yi-chu, AN Wei-qi, JIN Jie, CAO Dan-dan. Effects of biochar and its dissolved fractions on microbial reduction of ferrihydrite[J]. China Environmental Science. 2023, 43(10): 5422-5432
中图分类号: X172   

参考文献

[1] Lu Y, Hu Y, Tang L, et al. Effects and mechanisms of modified biochars on microbial iron reduction of Geobacter sulfurreducens[J]. Chemosphere, 2021,283:130983.
[2] Navrotsky A, Mazeina L, Majzlan J. Size-driven structural and thermodynamic complexity in iron oxides[J]. Science, 2008,319(5870):1635-1638.
[3] Borch T, Kretzschmar R, Kappler A, et al. Biogeochemical redox processes and their impact on contaminant dynamics[J]. Environmental Science and Technology, 2010,44(1):15-23.
[4] An W H, Wu C, Xue S G, et al. Effects of biochar on the arsenic and mineral transformation in the reduction process od As(Ⅲ)-adsorbed ferrihydrite[J]. Acta Scientiae Circumstantiae, 2021,41(9):3497-3512.
[5] Cayuela M L, Sánchez-Monedero M A, Roig A, et al. Biochar and denitrification in soils:when, how much and why does biochar reduce N2O emissions?[J]. Scientific Reports, 2013,3:1732.
[6] Yu L, Yuan Y, Tang J, et al. Biochar as an electron shuttle for reductive dechlorination of pentachlorophenol by Geobacter sulfurreducens[J]. Scientific Reports, 2015,5:16221.
[7] Chen S, Rotaru A E, Shrestha P M, et al. Promoting interspecies electron transfer with biochar[J]. Scientific Reports, 2014,4(5019):5019.
[8] Xu X, Huang H, Zhang Y, et al. Biochar as both electron donor and electron shuttle for the reduction transformation of Cr(VI) during its sorption[J]. Environmental Pollution, 2019,244(1):423-430.
[9] Saquing J M, Yu Y H, Chiu P C, et al. Wood-derived black carbon (biochar) as a microbial electron donor and acceptor[J]. Environmental Science and Technology Letters, 2016,3(2):62-66.
[10] Xu S, Adhikari D, Huang R, et al. Biochar-facilitated microbial reduction of hematite[J]. Environmental Science and Technology, 2016,50(5):2389-2395.
[11] Kapper A, Wuestner M L, Ruecker A, et al. Biochar as an electron shuttle between bacteria and Fe(III) minerals[J]. Environmental Science and Technology Letters, 2014,1(8):339-344.
[12] Mukherjee A, Zimmerman A R. Organic carbon and nutrient release from a range of laboratory-produced biochars and biochar-soil mixtures[J]. Geoderma, 2013,193-194:122-130.
[13] Zhang B, Zhou S, Zhou L, et al. Pyrolysis temperature-dependent electron transfer capacities of dissolved organic matters derived from wheat straw biochar[J]. Science of the Total Environment, 2019,(696):133895.
[14] Guéguen C, Cuss C W. Characterization of aquatic dissolved organic matter by asymmetrical flow field-flow fractionation coupled to UV-Visible diode array and excitation emission matrix fluorescence[J]. Journal of Chromatography A, 2011,1218(27):4188-4198.
[15] Stedmon C A, Bro R. Characterizing dissolved organic matter fluorescence with parallel factor analysis:a tutorial:fluorescence-parafac analysis of DOM[J]. Limnology and oceanography, methods, 2008,6(11):572-579.
[16] Wu J, Hua Z, Yao Q S, et al. Toward understanding the role of individual fluorescent components in DOM-metal binding[J]. Journal of Hazardous Materials, 2012,215-216(May 15):294-301.
[17] Matilainen A, Gjessing E T, Lahtinen T, et al. An overview of the methods used in the characterization of natural organic matter (NOM) in relation to drinking water treatment[J]. Chemosphere, 2011,83(11):1431-1442.
[18] Sun T, Levin B D A, Guzman J J L, et al. Rapid electron transfer by the carbon matrix in natural pyrogenic carbon[J]. Nature Communications, 2017,8(1):1-12.
[19] Scott D T, Mcknight D M, Blunt-Harris E L, et al. Quinone moieties act as electron acceptors in the reduction of humic substances by humics-reducing microorganisms[J]. Environmental Science and Technology, 1998,32(19):372-372.
[20] Keiluweit M, Nico P S, Johnson M G, et al. Dynamic molecular structure of plant biomass-derived black carbon (biochar)[J]. Environmental Science and Technology, 2010,44(4):1247-1253.
[21] Liu G, Hao Z, Jiang Z, et al. Effects of biochar input on the properties of soil nanoparticles and dispersion/sedimentation of natural mineral nanoparticles in aqueous phase[J]. Science of The Total Environment, 2018,634(SEP.1):595-605.
[22] Lies D P, Hernandez M E, Kappler A, et al. Shewanella oneidensis MR-1uses overlapping pathways for iron reduction at a distance and by direct contact under conditions relevant for biofilms[J]. Applied and Environmental Microbiology, 2005,71(8):4414-4426.
[23] Uchimiya M, Stone A T. Reversible redox chemistry of quinones:Impact on biogeochemical cycles[J]. Chemosphere, 2009,77(4):451-458.
[24] Liao S, Pan B, Li H, et al. Detecting free radicals in biochars and determining their ability to inhibit the germination and growth of corn, wheat and rice seedlings[J]. Environmental Science and Technology, 2014,48(15):8581-8587.
[25] Weishaar J L, Aiken G R, Bergamaschi B A, et al. Evaluation of specific ultraviolet absorbance as an indicator of the chemical composition and reactivity of dissolved organic carbon[J]. Environmental Science and Technology, 2003,37(20):4702-4708.
[26] Xu W, Walpen N, Keiluweit M, et al. Redox properties of pyrogenic dissolved organic matter (pyDOM) from biomass-derived chars[J]. Environmental Science and Technology, 2021,55(16):11434-11444.
[27] He Z, Mao J, Honeycutt C W, et al. Characterization of plant-derived water extractable organic matter by multiple spectroscopic techniques[J]. Biology and Fertility of Soils, 2009,45(6):609-616.
[28] Haan H D, Boer T D. Applicability of light absorbance and fluorescence as measures of concentration and molecular size of dissolved organic carbon in humic Lake Tjeukemeer[J]. Water Research, 1987,21(6):731-734.
[29] Rajapaksha A U, Yong S, El-Naaggar A, et al. Dissolved organic matter characterization of biochars produced from different feedstock materials[J]. Journal of Environmental Management, 2018,233:393-399.
[30] Ishii S, Boyer T H. Behavior of reoccurring PARAFAC components in fluorescent dissolved organic matter in natural and engineered systems:a critical review[J]. Environmental Science and Technology, 2012,46(4):2006-2017.
[31] Yang Z, Sun T, Subdiaga E, et al. Aggregation-dependent electron transfer via redox-active biochar particles stimulate microbial ferrihydrite reduction[J]. Science of The Total Environment, 2019, 703:135515.
[32] Kluepfel L, Keiluweit M, Kleber M, et al. Redox properties of plant biomass-derived black carbon (biochar)[J]. Environmental Science and Technology, 2014,48(10):5601-5611.
[33] Ahmad M, Lee S S, Dou X M, et al. Effects of pyrolysis temperature on soybean stover-and peanut shell-derived biochar properties and TCE adsorption in water[J]. Bioresource Technol, 2012,118(-):536-544.
[34] Song W, Fang G, Wang Y, et al. Redox-active oxygen-containing functional groups in activated carbon facilitate microbial reduction of ferrihydrite[J]. Environmental Science and Technology, 2017,51(17):9709-9717.
[35] Sharpless C M, Aeschbacher M, Page S E, et al. Photooxidation-induced changes in optical, electrochemical, and photochemical properties of humic substances[J]. Environmental Science and Technology, 2014,48(5):2688-2696.
[36] Zhang Y, Xu X, Cao L, et al. Characterization and quantification of electron donating capacity and its structure dependence in biochar derived from three waste biomasses[J]. Chemosphere, 2018,211(11):1073-1081.
[37] Bauer I, Kappler A. Rates and extent of reduction of Fe(III) compounds and O2 by humic substances[J]. Environmental Science and Technology, 2009,43(13):4902-4908.
[38] Li X, Liu T, Li F, et al. Reduction of structural Fe(III) in oxyhydroxides by Shewanella decolorationis S12and characterization of the surface properties of iron minerals[J]. Journal of Soils and Sediments, 2012,12(2):217-227.

基金

国家自然科学基金资助项目(42177204);持久性有毒污染物环境与健康危害湖北省重点实验室开放基金资助项目(PTS-2020-04);中央高校基本科研业务费专项资金(2020MS038)

PDF(1743 KB)

Accesses

Citation

Detail

段落导航
相关文章

/