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Included as T2 Level in the High-Quality Science and Technology Journals in the Field of Environmental Science
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Volume 39 Issue 11
Jan.  2022
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Article Contents
CAO Yuan, LI Xiao-dong, PENG Chang-sheng, SUN Zong-quan, SHEN Jia-lun, MA Fu-jun, GU Qing-bao. REMOVAL OF 2,4-DINITROTOLUENE BY PERSULFATE ACTIVATED WITH IRON MODIFIED BIOCHAR PREPARED BY DIPPING-PYROLYSIS PROCESS[J]. ENVIRONMENTAL ENGINEERING , 2021, 39(11): 135-142,178. doi: 10.13205/j.hjgc.202111017
Citation: CAO Yuan, LI Xiao-dong, PENG Chang-sheng, SUN Zong-quan, SHEN Jia-lun, MA Fu-jun, GU Qing-bao. REMOVAL OF 2,4-DINITROTOLUENE BY PERSULFATE ACTIVATED WITH IRON MODIFIED BIOCHAR PREPARED BY DIPPING-PYROLYSIS PROCESS[J]. ENVIRONMENTAL ENGINEERING , 2021, 39(11): 135-142,178. doi: 10.13205/j.hjgc.202111017

REMOVAL OF 2,4-DINITROTOLUENE BY PERSULFATE ACTIVATED WITH IRON MODIFIED BIOCHAR PREPARED BY DIPPING-PYROLYSIS PROCESS

doi: 10.13205/j.hjgc.202111017
  • Received Date: 2021-02-04
    Available Online: 2022-01-26
  • To explore and optimize the experimental conditions and influence factors of the removal of organic pollutants by persulfate activated with iron modified biochar prepared by the dipping-pyrolysis process, 2,4-dinitrotoluene (2,4-DNT) was selected as the target pollutant to investigate the effects of pyrolysis parameters (pyrolysis temperature, heating rate, and residence time), FeCl3 concentration and initial pH values on 2,4-DNT removal. The electron spin resonance and free radical quenching test were used to assess the intensity of SO4-· and ·OH in the PS/MBC system. The results showed that:1) The pyrolysis temperature had the most significant influence on removal of 2,4-DNT by PS activated with MBC, followed by heating rate and residence time. When the pyrolysis parameters were retained at 300℃, 3 h, and 10℃/min, the best removal of 2,4-DNT was obtained by PS/MBC oxidation. 2) The concentration of FeCl3 was an important factor of MBC activation. The removal of 2,4-DNT first increased and then decreased with the increase of the FeCl3 concentration. When the concentration of FeCl3 was retained at 100 mmol/L, the removal efficiency of 2,4-DNT reached 100% after the reaction of 5 h, and the pseudo-first-order kinetic constant (kobs) of 2,4-DNT removal was determined to be 1.373 min-1. 3)When the initial pH ranged from 5.0 to 9.0, 2,4-DNT had a good removal by PS/MBC oxidation, the removal efficiencies were 94.5%~83.6%, and the kobs values were 0.606~0.345 min-1. 4) ·OH was the main factor for the removal of 2,4-DNT by PS/MBC oxidation. The signals of ·OH with different strengths were observed, with the addition of MBC prepared by different pyrolysis temperatures and FeCl3 concentrations. The results showed that MBC prepared by dipping-pyrolysis could effectively activate PS to achieve the removal of organic pollutants, which provided a new idea for treatment of organically polluted water by PS based-advanced chemical oxidation.
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  • [1]
    王璇. 硝基苯类有机污染物在环境中的来源与归趋行为研究[J]. 科技视界,2013(26):513.
    [2]
    KEITH L H, TELLIARD W A. Priority pollutants I-a perapective view[J]. ES&T Special Report, 1979,13(4):416-423.
    [3]
    LI X D, WU B, ZHANG Q, et al. Mechanisms on the impacts of humic acids on persulfate/Fe2+-based groundwater remediation[J]. Chemical Engineering Journal, 2019,378:122142.
    [4]
    张琦,王静贤,于鸽方,等. 不同方式活化过硫酸盐处理含油污泥及机理探究[J]. 现代化工,2020,40(10):120-130.
    [5]
    FANG J Y, SHANG C. Bromate formation from bromide oxidation by the UV/persulfate process[J]. Environmental Science & Technology, 2012,46(16):8976-8983.
    [6]
    ANIOSITAKIS G P, DIONYSIOU D D. Radical generation by the interaction of transition metals with common oxidants[J]. Environmental Science & Technology, 2004,13(38):3705-3712.
    [7]
    WANG J L, WANG S Z. Activation of persulfate (PS) and peroxymonosulfate (PMS) and application for the degradation of emerging contaminants[J]. Chemical Engineering Journal, 2018,334(15):1502-1517.
    [8]
    HUANG K C, COUTTENEY R A, HOAG G E. Kinetics of heat-assisted persulfate oxidation of methyl tert-butyl ether (MTBE)[J]. Chemosphere, 2002,49(4):413-420.
    [9]
    ZHANG Y X, LIU H L, XIN Y J, et al. Erythromycin degradation and ERY-resistant gene inactivation in erythromycin mycelial dreg by heat-activated persulfate oxidation[J]. Chemical Engineering Journal, 2019,358(15):1446-1453.
    [10]
    THINES K R, ABDULLAH E C, MUBARAK N M, et al. Synthesis of magnetic biochar from agricultural waste biomass to enhancing route for waste water and polymer application:a review[J]. Renewable and Sustainable Energy Reviews, 2017,67:257-276.
    [11]
    FANG G D, LIU C, GAO J, et al. Manipulation of persistent free radicals in biochar to activate persulfate for contaminant degradation[J]. Environmental Science & Technology, 2015,49(9):5645-5653.
    [12]
    YUAN Y, NAUTHI B, ANTONIN P, et al. Applications of biochar in redox-mediated reactions[J]. Bioresource Technology, 2017, 246:271-281.
    [13]
    ZHU S S, HUANG X C, MA F, et al. Catalytic removal of aqueous contaminants on N-doped graphitic biochars:inherent roles of adsorption and nonradical mechanisms[J]. Environmental Science & Technology, 2018,52(15):8649-8658.
    [14]
    KEMMOU L, FRONTISTIS Z, VAKROS J, et al. Degradation of antibiotic sulfamethoxazole by biochar-activated persulfate:factors affecting the activation and degradation processes[J]. Catalysis Today, 2018,313(1):128-133.
    [15]
    许端平,姜紫微,张朕. 磁性生物炭对铅和镉离子的竞争吸附动力学[J]. 安徽农业科学,2020,22(48):67-72.
    [16]
    WANG S Y, TANG Y K, LI K, et al. Combined performance of biochar sorption and magnetic separation processes for treatment of chromium-contained electroplating wastewater[J]. Bioresource Technology, 2014,174:67-73.
    [17]
    LIU W J, TIAN K, JIANG H, et al. Facile synthesis of highly efficient and recyclable magnetic solid acid from biomass waste[J]. Scientific Reports, 2013,3(1):2419.
    [18]
    ZHU X D, LIU Y C, QIAN F, et al. Preparation of magnetic porous carbon from waste hydrochar by simultaneous activation and magnetization for tetracycline removal[J]. Bioresource Technology, 2014,154:209-214.
    [19]
    YI Y Q, TU G Q, TSANG P E, et al. Insight into the influence of pyrolysis temperature on Fenton-like catalytic performance of magnetic biochar[J]. Chemical Engineering Journal, 2020, 380(15):122518.
    [20]
    梁宇飞,薛振华. 沙柳的低温热解特性研究[J]. 木材加工机械,2014,25(4):48-58.
    [21]
    RONG X, XIE M, KONG L S, et al. The magnetic biochar derived from banana peels as a persulfate activator for organic contaminants degradation[J]. Chemical Engineering Journal, 2019,372(15):294-303.
    [22]
    LI Q Q, HUANG X C, SUN G J, et al. The regular/persistent free radicals and associated reaction mechanism for the degradation of 1,2,4-trichlorobenzene over different MnO2 polymorphs[J]. Environmental Science & Technology, 2018,52(22):13351-13360.
    [23]
    郑凯琪,王俊超,刘姝彤,等. 不同热解温度污泥生物炭对Pb2+、Cd2+的吸附特性[J]. 环境工程学报,2016,10(12):7277-7282.
    [24]
    SUN X M, LI Y D. Colloidal carbon spheres and their core/shell structures with noble-metal nanoparticles[J]. Angewandte Chemie, 2004,116(5):607-611.
    [25]
    ZHANG K K, SUN P, MARIE C A S F, et al. Characterization of biochar derived from rice husks and its potential in chlorobenzene degradation[J]. Carbon, 2018,130:730-740.
    [26]
    JIA C J, SUN D L, LUO F, et al. Large-scale synthesis of single-crystalline iron oxide magnetic nanorings[J]. Journal of American Chemical Society, 2008,130(50):16968-16977.
    [27]
    郭明帅,王菲,张学良,等. 改性生物炭活化过硫酸盐对水中苯和氯苯的去除机制[J]. 中国环境科学,2020,12(40):5280-5289.
    [28]
    YANG J P, ZHAO Y C, MA S M, et al. Mercury removal by magnetic biochar derived from simultaneous activation and magnetization of sawdust[J]. Environmental Science & Technology, 2016,50(21):12040-12047.
    [29]
    BU L J, SHI Z, ZHOU S Q. Modeling of Fe(Ⅱ)-activated persulfate oxidation using atrazine as a target contaminant[J]. Separation and Purification Technology, 2016,169(1):59-65.
    [30]
    KUSIC H, PETERNEL I, UKIC S, et al. Modeling of iron activated persulfate oxidation treating reactive azo dye in water matrix[J]. Chemical Engineering Journal, 2011,172(1):109-121.
    [31]
    SONG Q, FENG Y P, LIU G G, et al. Degradation of the flame retardant triphenyl phosphate by ferrous ionactivated hydrogen peroxide and persulfate:kinetics, pathways, and mechanisms[J]. Chemical Engineering Journal, 2019,361:929-936.
    [32]
    SHANG W T, DONG Z J, LI M, et al. Degradation of diatrizoate in water by Fe (Ⅱ)-activated persulfate oxidation[J]. Chemical Engineering Journal, 2019,361(1):1333-1334.
    [33]
    LAU T K, CHU W, GRAHAM N J D. The aqueous degradation of butylated hydroxyanisole by UV/S2O82-:study of reaction mechanisms via dimerization and mineralization[J]. Environmental Science & Technology, 2007,41(2):613-619.
    [34]
    FANG G D, CHEN X R, WU W H, et al. Mechanisms of interaction between persulfate and soil constituents:activation, free radical formation, conversion, and identification[J]. Environmental Science & Technology, 2018,52(24):14352-14361.
    [35]
    FANG G D, DIONYSIOU D D, ZHOU D M, et al. Transformation of polychlorinated biphenyls by persulfate at ambient temperature[J]. Chemosphere, 2013,90(5):1573-1580.
    [36]
    LIANG C J, LIN Y T, SHIH W H. Treatment of trichloroethylene by adsorption and persulfate oxidation in batch studies[J]. Industrial & Engineering Chemistry Research, 2009,48(18):8373-8380.
    [37]
    OUYANG D, YAN J C, QIAN L B, et al. Degradation of 1,4-dioxane by biochar supported nano magnetite particles activating persulfate[J]. Chemosphere, 2017,184:609-617.
    [38]
    YANG L, CHEN Y, OUYANG D, et al. Mechanistic insights into adsorptive and oxidative removal of monochlorobenzene in biochar-supported nanoscale zero-valent iron/persulfate system[J]. Chemical Engineering Journal, 2020,400(15):125811.
    [39]
    NGUYEN T B, DOONG R, HUANG C P, et al. Activation of persulfate by CoO nanoparticles loaded on 3D mesoporous carbon nitride (CoO@meso-CN) for the degradation of methylene blue (MB)[J]. Science of the Total Environment, 2019,675(20):531-541.
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