Source Jouranl of CSCD
Source Journal of Chinese Scientific and Technical Papers
Included as T2 Level in the High-Quality Science and Technology Journals in the Field of Environmental Science
Core Journal of RCCSE
Included in the CAS Content Collection
Included in the JST China
Indexed in World Journal Clout Index (WJCI) Report
SHI En, ZHANG Shuai, ZHANG Miao, LIU Shasha, ZOU Yuliang, ZHANG Xiangzhi. ENVIRONMENTAL IMPACT ASSESSMENT OF SLUDGE-BASED ACTIVATED CARBON PREPARATION PROCESS BASED ON LIFE CYCLE[J]. ENVIRONMENTAL ENGINEERING , 2024, 42(2): 40-47. doi: 10.13205/j.hjgc.202402005
Citation: SHI En, ZHANG Shuai, ZHANG Miao, LIU Shasha, ZOU Yuliang, ZHANG Xiangzhi. ENVIRONMENTAL IMPACT ASSESSMENT OF SLUDGE-BASED ACTIVATED CARBON PREPARATION PROCESS BASED ON LIFE CYCLE[J]. ENVIRONMENTAL ENGINEERING , 2024, 42(2): 40-47. doi: 10.13205/j.hjgc.202402005

ENVIRONMENTAL IMPACT ASSESSMENT OF SLUDGE-BASED ACTIVATED CARBON PREPARATION PROCESS BASED ON LIFE CYCLE

doi: 10.13205/j.hjgc.202402005
  • Received Date: 2023-10-14
    Available Online: 2024-04-28
  • The preparation of activated carbon from sludge is a resourceful way to utilize sludge and with a wide range of applications. However, few studies have been conducted to evaluate the process of sludge-based activated carbon(SDAC) preparation. In this study, the activated carbon prepared from sewage plant sludge was used as an object, and a flow chart of the preparation process was established to quantitatively reveal the environmental impacts and key influencing factors of the preparation process by applying life cycle assessment(LCA). The results showed that the environmental impact of the roasting step dominated the whole preparation process, followed by the grinding or impregnation step, and then the washing and drying steps. The energy consumption of water vapor physical activation, CO2 physical activation, KOH impregnation, ZnCl2 impregnation, H3PO4 impregnation, ZnCl2 molten salt method, and physicochemical method were 68.976, 79.776, 47.376, 53.964, 48.564, 45.828, and 46.764 MJ/kg of activated carbon, respectively, whereas the values of global warming potential were 14.93, 17.06, 15.54, 13.42, 14.51, 12.65 and 13.91 kg CO2 eq/kg of activated carbon, respectively. The LCA results showed that the preparation of activated carbon using the CO2 physical activation method had the highest environmental impact, while the ZnCl2 molten salt method had the lowest environmental impact. The results of sensitivity analysis on the ZnCl2 molten salt method showed that electricity consumption and activator are the two key factors for further optimization of the activated carbon preparation method. Based on the life cycle perspective, the ZnCl2 molten salt method is more effective in preparing SDAC, and the energy-saving modification of the equipment should be strengthened, which can significantly reduce the environmental impact of the SDAC preparation process.
  • [1]
    王志朴,朱赫男,邢文龙,等.污泥与秸秆共热解制备生物炭工艺优化及其对Cr(Ⅵ)的吸附[J].环境工程,2019,37(2):138-143.
    [2]
    WU B,DAI X,CHAI X.Critical review on dewatering of sewage sludge:influential mechanism,conditioning technologies and implications to sludge re-utilizations[J].Water Research,2020,180:115912.
    [3]
    郭朝强,尚双,兰奎,等.不同含水率污泥和小麦秸秆混合热解制备富氢合成气[J].环境工程,2020,38(5):160-164

    ,214.
    [4]
    MURAKAMI T,SUZUKI Y,NAGASAWA H,et al.Combustion characteristics of sewage sludge in an incineration plant for energy recovery[J].Fuel Processing Technology,2009,90(6):778-783.
    [5]
    LIEW C S,YUNUS N M,CHIDI B S,et al.A review on recent disposal of hazardous sewage sludge via anaerobic digestion and novel composting[J].Journal of Hazardous Materials,2022,423:126995.
    [6]
    戴亮,赵伟繁,张洪伟,等.污泥生物炭去除水中重金属的研究进展[J].环境工程,2020,38(12):70-77.
    [7]
    刘宇程,刘骞,陈菊,等.基于响应曲面法优化生物质污泥活性炭的制备方法[J].环境工程学报,2017,11(11):6041-6049.
    [8]
    范晓丹,康婷婷,尹乐,等.污泥活性炭对复合染料的脱色及其重金属浸出毒性[J].环境工程学报,2012,6(10):3623-3628.
    [9]
    KACAN E.Optimum BET surface areas for activated carbon produced from textile sewage sludges and its application as dye removal[J].Journal of Environmental Management,2016,166:116-123.
    [10]
    ZHANG M,GAO J,SHI E,et al.Mesoporous carbon derived from anaerobic granular sludge through molten salt method and its application for dye adsorption:an experimental and molecular dynamics simulation study[J].Biomass Conversion and Biorefinery,2022:1-10.
    [11]
    张俊杰,邵敬爱,黄河洵,等.利用污泥制备活性炭及其吸附特性的研究进展[J].化工进展,2017,36(10):3876-3886.
    [12]
    矫旭东,吴佳,王韬,等.基于全生命周期管理的固体废物分类资源化利用研究[J].环境工程,2021,39(10):201-206

    ,170.
    [13]
    叶宁,卢皓,史晨,等.基于生命周期的白酒丢糟资源化新工艺技术环境影响研究[J/OL].环境工程,1-13[2023-12-08

    ]http://kns.cnki.net/kcms/detail/11.2097.X.20230902.0028.002.html.
    [14]
    刘航驿,颜蓓蓓,林法伟,等.生命周期视角下2种餐厨垃圾资源化处理方案的对比分析[J].环境工程,2021,39(9):169-175.
    [15]
    NOWROUZI M,ABYAR H,YOUNESI H,et al.Life cycle environmental and economic assessment of highly efficient carbon-based CO2 adsorbents:a comparative study[J].Journal of CO2 Utilization,2021,47:101491.
    [16]
    HJAILA K,BACCAR R,SARRA M,et al.Environmental impact associated with activated carbon preparation from olive-waste cake via life cycle assessment[J].Journal of Environmental Management,2013,130:242-247.
    [17]
    MAITI P,SIDDIPI H,KUMARI U,et al.Adsorptive remediation of azo dye contaminated wastewater by ZnCl2 modified bio-adsorbent:batch study and life cycle assessment[J].Powder Technology,2023,415:118153.
    [18]
    霍丽丽,赵立欣,孟海波,等.秸秆类生物质气炭联产全生命周期评价[J].农业工程学报,2016,32(增刊1):261-266.
    [19]
    窦鑫,曾淦宁,艾宁,等.铜藻基活性炭全生命周期温室气体排放分析[J].环境科学与技术,2015,38(12):262-266.
    [20]
    LI W H,YUE Q Y,GAO B Y,et al.Preparation of sludge-based activated carbon made from paper mill sewage sludge by steam activation for dye wastewater treatment[J].Desalination,2011,278(1/2/3):179-185.
    [21]
    RIO S,FAUR-BRASQUET C,LE Coq L,et al.Production and characterization of adsorbent materials from an industrial waste[J].Adsorption,2005,11:793-798.
    [22]
    LI Z,DENG H,YANG L,et al.Influence of potassium hydroxide activation on characteristics and environmental risk of heavy metals in chars derived from municipal sewage sludge[J].Bioresource Technology,2018,256:216-223.
    [23]
    LI L Y,GONG X D,ABIDA O.Waste-to-resources:exploratory surface modification of sludge-based activated carbon by nitric acid for heavy metal adsorption[J].Waste Management,2019,87:375-386.
    [24]
    ZHANG F S,NRIAGU J O,ITOH H.Mercury removal from water using activated carbons derived from organic sewage sludge[J].Water Research,2005,39(2/3):389-395.
    [25]
    尹炳奎,朱石清,朱南文,等.生物质活性炭的制备及其染料废水中的应用[J].环境污染与防治,2006(8):608-611.
    [26]
    ALTHAUS H J,CHUDACOFF M,HISCHIER R,et al.Life cycle inventories of chemicals[J].Ecoinvent Report,2007,2.
    [27]
    DONES R,BAUER C,BOLLIGER R,et al.Life cycle inventories of energy systems:results for current systems in Switzerland and other UCTE countries[J].Final Report Ecoinvent,2007,2:5.
    [28]
    WANG S,PERSSON H,YANG W,et al.Pyrolysis study of hydrothermal carbonization-treated digested sewage sludge using a Py-GC/MS and a bench-scale pyrolyzer[J].Fuel,2020,262:116335.
    [29]
    蔡旭,黄群星,王飞,等.污泥在CO2气氛下热解CO与CH4的生成特性[J].环境工程学报,2016,10(7):3779-3786.
    [30]
    GABARRELL X,FONT M,VICENT T,et al.A comparative life cycle assessment of two treatment technologies for the Grey Lanaset G textile dye:biodegradation by Trametes versicolor and granular activated carbon adsorption[J].The International Journal of Life Cycle Assessment,2012,17:613-624.
    [31]
    HUANG C,MOHAMED B A,LI L Y.Comparative life-cycle assessment of pyrolysis processes for producing bio-oil,biochar,and activated carbon from sewage sludge[J].Resources,Conservation and Recycling,2022,181:106273.
    [32]
    冯博博.氢氧化钾生产中的三废综合治理[J].氯碱工业,2011,47(6):32-33.
    [33]
    卢芳仪,卢爰军.无污染的氯化锌生产工艺[J].化学世界,2006(2):125-126.
    [34]
    李伟,赵连文,多春玲.盐酸生产中尾气吸收工艺改进[J].氯碱工业,2022,58(7):24-25.
    [35]
    潘宇婷,李霞,李金枝,等.工业用氢氧化钠中氯酸钠含量测定方法的探讨[J].中国氯碱,2017(3):30-33.
    [36]
    唐松标,周卫红,杨改秀.不同温度场下生物质热解特性及物质流和能量流分析[J].太阳能学报,2023,44(7):511-519.
    [37]
    BAYER P,HEUER E,KARL U,et al.Economical and ecological comparison of granular activated carbon (GAC) adsorber refill strategies[J].Water Research,2005,39(9):1719-1728.
  • Relative Articles

    [1]LI Si, YUAN Huizhou, KE Shuizhou, LIU Xiaoming. CARBON NEUTRAL POTENTIAL OF WHOLE PROCESS OF CO-DIGESTION OF FOOD WASTE AND SLUDGE[J]. ENVIRONMENTAL ENGINEERING , 2024, 42(11): 90-98. doi: 10.13205/j.hjgc.202411010
    [2]WANG Tao, YUE Bo, MENG Bangbang, LIU Bo, GAO Hong. A LIFE CYCLE ASSESSMENT OF SECONDARY COPPER PRODUCTION[J]. ENVIRONMENTAL ENGINEERING , 2024, 42(7): 225-232. doi: 10.13205/j.hjgc.202407025
    [3]XU Jiarui, LIU Hao, LUAN Weihao, WANG Chao, LIU Changqing, YANG Yandong. ADSORPTION PERFORMANCE OF DISSOLVED ORGANIC MATTER BY IRON-MODIFIED ACTIVATED CARBON FROM SECONDARY EFFLUENT OF WASTEWATER TREATMENT PLANTS[J]. ENVIRONMENTAL ENGINEERING , 2024, 42(3): 67-72. doi: 10.13205/j.hjgc.202403008
    [4]TAN Yujie, CHEN Yayi, ZHOU Binjie, LU Xueqin, ZHEN Guangyin, HU Weijie. PROMOTING DEWATERABILITY OF WASTE ACTIVATED SLUDGE BY ACTIVATED CARBON ACTIVATED PERSULFATE OXIDATION[J]. ENVIRONMENTAL ENGINEERING , 2024, 42(5): 70-74. doi: 10.13205/j.hjgc.202405009
    [5]LIANG Wenjun, LU Dan, HU Wei. EVALUATION OF ADSORPTION PERFORMANCE USING COMMERCIAL ACTIVATED CARBON FOR TYPICAL GASOLINE-VAPOR VOCs AT SERVICE STATIONS[J]. ENVIRONMENTAL ENGINEERING , 2024, 42(10): 65-72. doi: 10.13205/j.hjgc.202410009
    [6]LI Xiaolong, ZHANG Tao, ZHAO Jingchen. INFLUENCE MECHANISM OF ABRASIVE RESISTANCE OF ACTIVATED CARBON FOR FLUE GAS PURIFICATION[J]. ENVIRONMENTAL ENGINEERING , 2023, 41(5): 45-51,60. doi: 10.13205/j.hjgc.202305007
    [7]CHEN Renjie, DONG Bin, DAI Xiaohu. OVERVIEW AND PROSPECT ON APPLICATION OF HYDROTHERMAL TREATMENT ON SEWAGE SLUDGE HARMLESSNESS[J]. ENVIRONMENTAL ENGINEERING , 2023, 41(9): 201-209. doi: 10.13205/j.hjgc.202309025
    [8]ZHANG Jiwen, XU Zunzhu, ZHANG Yuwei, CHEN Yuqi, JIN Xiaoxian, LIU Dong, LU Zhaoyang. LIFE CYCLE ASSESSMENT OF COORDINATED TREATMENT OF WASTE GAS POLLUTION AND CARBON REDUCTION IN ANAEROBIC POND IN A PHARMACEUTICAL FACTORY[J]. ENVIRONMENTAL ENGINEERING , 2023, 41(3): 192-201. doi: 10.13205/j.hjgc.202303026
    [9]LIAO Chengfeng, LIU Yuchen, TANG Yuting, TANG Jiehong, MA Xiaoqian. LIFE CYCLE ASSESSMENT AND TECHNO-ECONOMIC ANALYSIS OF PRODUCING AMMONIA BY ALGAL BIOMASS GASIFICATION[J]. ENVIRONMENTAL ENGINEERING , 2023, 41(5): 187-194. doi: 10.13205/j.hjgc.202305025
    [10]QUAN Zhaoxi, CHEN Xiangsheng, CHEN Feng, GAO Wang, HAN Wenlong. ANALYSIS OF CARBON REDUCTION EFFECT OF TUNNEL CONSTRUCTION MUCK SOIL UTILIZATION BASED ON LIFE CYCLE ASSESSMENT[J]. ENVIRONMENTAL ENGINEERING , 2023, 41(10): 91-98,162. doi: 10.13205/j.hjgc.202310012
    [11]LIAO Ziying, ZHANG Huanjun, HAN Shuguang, PAN Zhengguo, LI Yi. LIFE CYCLE ASSESSMENT OF TYPICAL CYANOBACTERIA TREATMENT EQUIPMENT[J]. ENVIRONMENTAL ENGINEERING , 2023, 41(6): 143-150. doi: 10.13205/j.hjgc.202306019
    [12]DU Minghui, BI Yingying, DONG Li, WANG Yong, SUN Xiaoming. INFLUENCE MECHANISM OF ACTIVATED CARBON PARTICLE SIZE ON O3-AC TREATMENT OF ORGANIC WASTEWATER[J]. ENVIRONMENTAL ENGINEERING , 2022, 40(4): 22-28. doi: 10.13205/j.hjgc.202204004
    [13]DANG Xiaoqing, JING Kairui, MA Hongzhou, DONG Haoyun, CAO Li, LI Yu, LIU Xia, LI Shijie. EXPERIMENTAL RESEARCH ON VACUUM-THERMAL REGENERATION OF ACTIVATED CARBON FOR ADSORPTION OF VOCs AND THE INFLUENCING FACTORS[J]. ENVIRONMENTAL ENGINEERING , 2022, 40(8): 62-68,130. doi: 10.13205/j.hjgc.202208008
    [14]XU Xiaozhu, ZHANG Yun, GAO Qiufeng, XU Yurong, WANG Zhanbo. LIFE CYCLE ASSESSMENT OF HYDRODESULFURIZATION WASTE METAL CATALYST RECOVERY PROCESS[J]. ENVIRONMENTAL ENGINEERING , 2022, 40(8): 185-190. doi: 10.13205/j.hjgc.202208026
    [15]CHEN Li, LI Jia-bin, FU Wan-yi, ZHANG Xi-hui. EFFECT OF CERAMIC MEMBRANE COMBINED PROCESS IN TREATMENT OF SLUDGE WATER FROM DRINKING WATER TREATMENT PLANT[J]. ENVIRONMENTAL ENGINEERING , 2021, 39(7): 80-87,12. doi: 10.13205/j.hjgc.202107009
    [16]XIE Chao, LV Bin, WANG Si-si, WANG Pei-jun. REVIEW ON RESOURCE AND ENVIRONMENTAL IMPACT ASSESSMENT OF PERMEABLE PAVEMENT BASED ON LIFE CYCLE THINKING[J]. ENVIRONMENTAL ENGINEERING , 2021, 39(8): 197-202,44. doi: 10.13205/j.hjgc.202108027
    [17]LIU Yu-tong, ZHANG Yun, HOU Hao-chen, GAO Qiu-feng, XU Xiao-zhu. LIFE CYCLE ASSESSMENT OF HIGH PURITY MAGNESIUM PRODUCTION[J]. ENVIRONMENTAL ENGINEERING , 2021, 39(6): 187-191. doi: 10.13205/j.hjgc.202106028
    [18]CHEN Wei-gang, WU Hai-xia, FAN Jia-wei. ACTIVATED CARBON HETEROGENEOUS ACTIVATION OF DIFFERENT PERSULFATES TO DEGRADATION AZO DYE ACID ORANGE Ⅱ[J]. ENVIRONMENTAL ENGINEERING , 2020, 38(8): 113-118,57. doi: 10.13205/j.hjgc.202008019
    [19]SHI Hui-min, WANG Qun-hui, NI Jin, GAO Ming, WU Chuan-fu. DEGRADATION OF AMOXICILLIN SIMULATED WASTEWATER USING A THREE-DIMENSIONAL ELECTRODES REACTOR[J]. ENVIRONMENTAL ENGINEERING , 2020, 38(5): 30-35. doi: 10.13205/j.hjgc.202005006
    [20]Zhang Xiaoxu, Zhang Hongyu, Li Guoxue, . EFFECT OF ADDITIVE QUANTITY OF STALKS ON H2 S AND NH3 EMISSION DURING KITCHEN WASTE COMPOSTING[J]. ENVIRONMENTAL ENGINEERING , 2015, 33(1): 95-99. doi: 10.13205/j.hjgc.201501022
  • Cited by

    Periodical cited type(1)

    1. 臧丽慧,徐丽. 污泥基吸附剂去除抗生素废水的研究进展. 辽宁化工. 2024(10): 1605-1607 .

    Other cited types(0)

  • Created with Highcharts 5.0.7Amount of accessChart context menuAbstract Views, HTML Views, PDF Downloads StatisticsAbstract ViewsHTML ViewsPDF Downloads2024-052024-062024-072024-082024-092024-102024-112024-122025-012025-022025-032025-04051015202530
    Created with Highcharts 5.0.7Chart context menuAccess Class DistributionFULLTEXT: 20.3 %FULLTEXT: 20.3 %META: 75.5 %META: 75.5 %PDF: 4.2 %PDF: 4.2 %FULLTEXTMETAPDF
    Created with Highcharts 5.0.7Chart context menuAccess Area Distribution其他: 21.2 %其他: 21.2 %上海: 2.4 %上海: 2.4 %东莞: 0.5 %东莞: 0.5 %六安: 2.4 %六安: 2.4 %北京: 1.9 %北京: 1.9 %南京: 2.8 %南京: 2.8 %台州: 0.5 %台州: 0.5 %合肥: 0.5 %合肥: 0.5 %大同: 0.5 %大同: 0.5 %天津: 1.9 %天津: 1.9 %常州: 1.4 %常州: 1.4 %常德: 0.5 %常德: 0.5 %广州: 0.5 %广州: 0.5 %张家口: 4.7 %张家口: 4.7 %徐州: 0.5 %徐州: 0.5 %成都: 1.4 %成都: 1.4 %昆明: 0.9 %昆明: 0.9 %晋城: 0.5 %晋城: 0.5 %杭州: 0.9 %杭州: 0.9 %武汉: 1.4 %武汉: 1.4 %沈阳: 0.9 %沈阳: 0.9 %海东: 0.5 %海东: 0.5 %深圳: 1.9 %深圳: 1.9 %湖州: 1.9 %湖州: 1.9 %漯河: 2.8 %漯河: 2.8 %石家庄: 1.4 %石家庄: 1.4 %芒廷维尤: 26.4 %芒廷维尤: 26.4 %芝加哥: 5.7 %芝加哥: 5.7 %衢州: 0.5 %衢州: 0.5 %西宁: 0.9 %西宁: 0.9 %西安: 0.5 %西安: 0.5 %西雅图: 0.5 %西雅图: 0.5 %贵阳: 0.5 %贵阳: 0.5 %运城: 3.3 %运城: 3.3 %遵义: 0.5 %遵义: 0.5 %郑州: 0.5 %郑州: 0.5 %重庆: 1.4 %重庆: 1.4 %金华: 0.5 %金华: 0.5 %镇江: 0.5 %镇江: 0.5 %长沙: 0.9 %长沙: 0.9 %青岛: 0.9 %青岛: 0.9 %其他上海东莞六安北京南京台州合肥大同天津常州常德广州张家口徐州成都昆明晋城杭州武汉沈阳海东深圳湖州漯河石家庄芒廷维尤芝加哥衢州西宁西安西雅图贵阳运城遵义郑州重庆金华镇江长沙青岛

Catalog

    通讯作者: 陈斌, bchen63@163.com
    • 1. 

      沈阳化工大学材料科学与工程学院 沈阳 110142

    1. 本站搜索
    2. 百度学术搜索
    3. 万方数据库搜索
    4. CNKI搜索

    Article Metrics

    Article views (159) PDF downloads(9) Cited by(1)
    Proportional views
    Related

    /

    DownLoad:  Full-Size Img  PowerPoint
    Return
    Return