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·2584·                            精细化工   FINE CHEMICALS                                 第 37 卷

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            分别为 8.22 mg  Cr(Ⅵ)/g 及 2.56 mg  Cr(Ⅵ)/g,与              for the treatment of wastewater having low COD/SO 4  ratio[J].
            BC-500 相比,SBC-500 对 Cr(Ⅵ)具有更好的去除能                      Journal of Hazardous Materials, 2008, 159(2): 616-625.
                                                               [3]   RONG X, XIE M, KONG L S, et al. The magnetic biochar derived
            力。在 Cr(Ⅵ)初始质量浓度增加到 120 mg/L 时,                         from banana peels as a persulfate activator for organic contaminants
            SBC-500 及 BC-500 对于 Cr(Ⅵ)去除效果趋于稳定。                     degradation[J]. Chemical Engineering Journal, 2019, 372: 294-303.
                                                               [4]   FARIA W  M,  FIGUEIREDO C C, COSER T  R,  et al. Is  sewage
                 在较低的 Cr(Ⅵ)初始质量浓度下,两种生物炭
                                                                   sludge biochar capable of replacing inorganic fertilizers for corn
            材料均具有较高的去除率,其可能是生物炭材料表                                 production? Evidence from a two-year field experiment[J]. Archives
            面有效活性位点较多,有利于 Cr(Ⅵ)的吸附。相较                              of Agronomy and Soil Science, 2018, 64(4): 505-519.
                                                               [5]   HUANG H, KUMAR B B, CHEN G H, et al. Sulfidogenic anaerobic
            于 BC-500,SBC-500 具有更高的 Cr(Ⅵ)去除率,可
                                                                   digestion of sulfate-laden waste activated sludge: Evaluation on
            能由于 SBC-500 孔道结构增加,有凹凸不平的吸附                            reactor performance and dynamics  of microbial community[J].
                                                2
            空穴,其具有较大的比表面积(17.90 m /g)和总孔                           Bioresource Technology, 2020, 297: 122396.
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            容(0.0423 mL/g),并且 SBC-500 的晶型结构更为
                                                                   characteristics in soil of different mining activity zones[J]. Transactions
            丰富,存在 FeS 及某些金属氧化物。                                    of Nonferrous Metals Society of China, 2008, 18(1): 207-211.
                 与 SHAKYA 等   [31] 在 650  ℃下热解制备生物炭            [7]   NIKFAR S, PARSA A,  BAHALOO-HOREH  N,  et al. Enhanced
                                                                   bioleaching of Cr and Ni from a chromium-rich electroplating sludge
            研究相比,其在初始 Cr(Ⅵ)质量浓度为 50 mg/L 时,                        using the filtrated culture of Aspergillus niger[J]. Journal of Cleaner
            去除率达到 27.28%,在初始 Cr(Ⅵ)质量浓度为                            Production, 2020, 264: 121622.
            100 mg/L 时,去除率为 19.8%,本研究在 500  ℃下                 [8]   Ministry of Ecological and Environment of the People's Republic of
                                                                   China. Announcement on the publication of list of toxic and harmful
            以硫酸盐还原剩余污泥制备 SBC-500,低于该研究                             water pollutants (the first batch): 000014672/2019-01115[S]. Beijing:
            热解温度,对能源消耗更低,且对 Cr(Ⅵ)去除率高                              General Office of the Ministry of Ecology and Environment(生态环
            于 SHAKYA 等    [31] 的研究结果。因此,本研究可对硫                     境部办公厅), 2019.
                                                               [9]   MA Y, LIU W J, ZHANG  N,  et al. Polyethylenimine  modified
            酸盐还原剩余污泥进行资源化合理处置,还可为污                                 biochar adsorbent for  hexavalent chromium removal from the
            泥基生物炭修复重金属污染水体提供新的理念与                                  aqueous solution[J]. Bioresource Technology, 2014, 169: 403-408.
            思路。                                                [10]  YU J D, JIANG C Y, GUAN Q Q, et al. Enhanced removal of Cr(Ⅵ)
                                                                   from aqueous solution by supported ZnO nanoparticles on biochar
                                                                   derived from waste water hyacinth[J]. Chemosphere, 2018, 195: 632-640.
            3   结论                                             [11]  LI Y H, CHANG F M, HUANG  B,  et al. Activated carbon
                                                                   preparation from pyrolysis char of sewage sludge and its adsorption
                (1)为实现剩余污泥合理处置,制备了以硫酸                              performance for organic compounds in sewage[J]. Fuel, 2020, 266:
            盐还原剩余污泥为原料的生物炭 SBC-500,其具有                             117053.
                                                               [12]  PINTO M, SILVA D, GOMES A, et al. Biochar from carrot residues
            碱性大,灰分及产率高的特性,BET 比表面积为                                chemically modified with magnesium for removing phosphorus from
                   2
            17.90 m /g,孔容为 0.0423 mL/g,明显高于以浓缩                     aqueous solution[J]. Journal of Cleaner Production, 2019, 222: 36-46.
            池污泥制备生物炭 BC-500,制备的两种碳材料均以                         [13]  WANG  G G (王格格), LI G (李刚), LU J  Y (陆江银),  et al.
                                                                                                          2+
                                                                   Preparation of slush-based biochar and its adsorption of Hg [J].
            介孔结构为主。                                                Chemical Environmental Protection (化工环保), 2016, 36(3): 283-287.
                (2)以 SRS 制备的 SBC-500,孔道结构明显,                   [14]  SELVARAJ K, MANONMANI S,  PATTABHI S. Removal of
            生物炭内部镶嵌有不规则边缘的晶型结构;XRD 结                               hexavalent chromium using distillery sludge[J]. Bioresource Technology,
                                                                   2003, 89(2): 207-211.
            果显示 SBC-500 具有规则的石墨烯碳、非晶型碳及                        [15]  American Society of Testing Materials.Standard test method for ash
            FeS 晶型结构;FTIR 结果显示具有 O==S==O 的反                        in analysis of petroleum coke: D4422-2003(2008)[S]. Washington D
            对称伸缩振动峰。                                               C: ASTM, 2003.
                                                               [16]  APHA.Standard methods for the examination of water and
                (3)在 pH 为 3,投加量为 0.2 g,Cr(Ⅵ)初始质                    wastewater[M]. 20th ed. Washington D C: American Public Health
            量浓度为 10 mg/L,在吸附 48 h 后,SBC-500 对 Cr(Ⅵ)                Association/American Water Works Association/Water Environment
                                                                   Federation, 1998.
            去除率达到 100%。当 Cr(Ⅵ)初始质量浓度增至
                                                               [17]  YIN C K, SHEN Y W,  YUAN R X,  et al. Sludge-based
            200 mg/L 时,SBC-500 对 Cr(Ⅵ)的吸附量为 8.22 mg                biochar-assisted thermophilic anaerobic digestion of waste-activated
            Cr(Ⅵ)/g。相较于 BC-500,SBC-500 对 Cr(Ⅵ)具有                   sludge in microbial electrolysis cell for methane production[J].
                                                                   Bioresource Technology, 2019, 284: 315-324.
            更好的去除能力。
                                                               [18]  JIANG G, RONG Z D, SUN W. Effects of metakaolin on mechanical
                                                                   properties, pore structure and hydration heat of mortars at 0.17 w/b
            参考文献:                                                  ratio[J]. Construction and Building Materials, 2015, 93(93): 564-572.
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                 synthesis-based pharmaceutical wastewater containing  rich organic   swine sludge to prepare modified biochar adsorbent for the efficient
                 sulfur compounds and sulfate and associated microbial characteristics[J].   removal of Pb(Ⅱ) from water[J]. Journal of Cleaner Production,
                 Chemical Engineering Journal, 2015, 260: 55-63.   2020, 257: 120322.
            [2]   SABUMON P C. Development of enhanced sulphidogenesis process               (下转第 2592 页)
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