生产与科研应用·

餐厨垃圾与果蔬垃圾高温干式厌氧发酵产氢技术

  • 炊春萌 ,
  • 张斯颖 ,
  • 王娜 ,
  • 刘乾静 ,
  • 李保国 ,
  • 刘莉
展开
  • 1(上海理工大学 医疗器械与食品学院,上海,200093)
    2(中国科学院上海高等研究院,上海,201210)
    3(上海有机固废生物转化工程技术研究中心,上海,200241)
硕士研究生(李保国教授和刘莉副研究员为共同通讯作者,E-mail:lbaoguo@126.com;liul@sari.ac.cn)

收稿日期: 2020-10-04

  修回日期: 2020-11-30

  网络出版日期: 2021-08-02

基金资助

国家重点研发计划项目(2018YFC1901000);上海有机固废生物转化工程技术研究中心开放课题(SERC2020A03)

Hydrogen production by thermophilic dry anaerobic fermentation of food waste and fruit and vegetable waste

  • CHUI Chunmeng ,
  • ZHANG Siying ,
  • WANG Na ,
  • LIU Qianjing ,
  • LI Baoguo ,
  • LIU Li
Expand
  • 1(School of Medical Instrument and Food Engineering,University of Shanghai for Science and Technology,Shanghai,200093,China)
    2(Shanghai Advanced Research Institute,Chinese Academy of Sciences,Shanghai,201210,China)
    3(Shanghai Engineering Research Center of Biotransformation of Organic Solid Waste,Shanghai,200241,China)

Received date: 2020-10-04

  Revised date: 2020-11-30

  Online published: 2021-08-02

摘要

随着餐饮行业的发展,食物浪费成为一个不断被关注的问题,餐厨垃圾对公众健康和环境构成了巨大的威胁。厌氧发酵被认为是一种有前途的固体废物处理技术。研究在55 ℃条件下利用不同餐厨垃圾和果蔬垃圾的混合比例(100∶0,80∶20,60∶40,50∶50,40∶60,20∶80和0∶100),基于挥发性固体(volatile solid,VS),评估了果蔬垃圾作为共底物的高温干厌氧发酵的产氢潜力。结果表明,当餐厨垃圾和果蔬垃圾的比例为80∶20时,最大累积产氢量达到64.10 NmL/g VS。与单一餐厨垃圾和果蔬垃圾发酵相比,分别增加了169.10%和97.17%。有机物去除率达到53.03%,是单一餐厨垃圾发酵的2.04倍,是单一果蔬垃圾发酵的1.55倍。研究结果表明,在餐厨垃圾厌氧发酵产氢过程中,与单一物料发酵相比,果蔬垃圾作为辅助基质能提高厌氧发酵的产氢量和有机物去除率。

本文引用格式

炊春萌 , 张斯颖 , 王娜 , 刘乾静 , 李保国 , 刘莉 . 餐厨垃圾与果蔬垃圾高温干式厌氧发酵产氢技术[J]. 食品与发酵工业, 2021 , 47(13) : 240 -245 . DOI: 10.13995/j.cnki.11-1802/ts.025806

Abstract

With the development of the catering industry, kitchen waste has become a constant concern, and kitchen waste poses a huge threat to public health and the environment. Anaerobic fermentation is considered a promising solid waste treatment technology. This study used different mixing ratios of kitchen waste and fruit and vegetable waste,100∶0, 80∶20, 60∶40, 50∶50, 40∶60, 20∶80, and 0∶100, based on volatile solid (VS) at 55 ℃, evaluated the hydrogen production potential of thermophilic dry anaerobic fermentation with fruit and vegetable waste as a co-substrate. The results showed that when the proportion of kitchen waste and fruit and vegetable waste was 80∶20, the maximum cumulative hydrogen production reached 64.10 NmL/g VS. It had increased by 169.10% and 97.17%, respectively, compared to that of single kitchen waste and fruit and vegetable waste fermentation; the organic matter removal rate reached 53.03%, which was 2.04 times of single kitchen waste, and 1.55 times of single fruit and vegetable waste fermentation. The research results showed that in the process of anaerobic fermentation of kitchen waste for hydrogen production, compared with single-material fermentation, fruit and vegetable waste as an auxiliary substrate could increase the hydrogen production and organic matter removal rate of anaerobic fermentation.

参考文献

[1] 郝春霞, 陈灏,赵玉柱.餐厨垃圾厌氧发酵处理工艺及关键设备[J].环境工程,2016,34(S1):691-695.
HAO C X,CHEN H,ZHAO Y Z.Anaerobic fermentation techniques and key equipments for treatment of kitchen waste[J].Environmental Engineering,2016,34(S1):691-695.
[2] YIN C H,DONG X,LV L,et al.Economic production of probiotics from kitchen waste[J].Food Science and Biotechnology,2013,22(S1):59-63.
[3] 李志强, 曹秀芹,张达飞,等.餐厨垃圾干式厌氧消化的试验研究[J].科学技术与工程,2018,18(8):343-348.
LI Z Q,CAO X Q,ZHANG D F,et al.Experimental study on dry anaerobic digestion by food waste[J].Science Technology and Engineering,2018,18(8):343-348.
[4] 黄林丽, 谢斌,陈立,等.公共餐厨垃圾饲料化利用的混合菌发酵工艺[J].食品与发酵工业,2019,45(24):148-152.
HUANG L L,XIE B,CHEN L,et al.Mixed fermentation of public kitchen waste to animal feed[J].Food and Fermentation industries,2019,45(24):148-152.
[5] 赵明星, 黄月,缪恒锋,等.餐厨垃圾与剩余污泥协同厌氧连续处置研究[J].食品与发酵工业,2020,46(19):92-98.
ZHAO M X,HUANG Y,MIAO H F,et al.Continuous anaerobic co-digestion of food waste and excess sludge[J].Food and Fermentation Industries,2020,46(19):92-98.
[6] 邬苏焕, 宋兴福,刘够生,等.双菌固态发酵处理餐厨垃圾[J].食品与发酵工业,2004,30(5):63-68.
WU S H,SONG X F,LIU G S,et al.Solid-state fermentation of waste food to produce feeding-protein by mixed fungal strains[J].Food and Fermentation Industries,2004,30(5):63-68.
[7] ZHAI N N,ZHANG T,YIN D X,et al.Effect of initial pH on anaerobic co-digestion of kitchen waste and cow manure[J].Waste Management,2015,38:126-131.
[8] IZUMI K,OKISHIO Y K,NAGAO N,et al.Effects of particle size on anaerobic digestion of food waste[J].International Biodeterioration & Biodegradation,2010,64(7):601-608.
[9] 郭晓慧. 餐厨垃圾厌氧消化产甲烷工艺特性及其微生物学机理研究[D].杭州:浙江大学,2014.
GUO X H.Food waste anaerobic digestion process performancee and the microbial mechanisms[D].Hangzhou:Zhejiang University,2014.
[10] 潘冬梅, 杨丹丹,刘圣鹏,等.餐厨垃圾发酵生产的生物饲料对猪生长性能及粪便中微生物的影响[J].中国农学通报,2017,33(14):117-120.
PAN D M,YANG D D,LIU S P,et al.Bioactive-feed fermented by food waste affecting growth performance and fecal microorganism of pigs[J].Chinese Agricultural Science Bulletin,2017,33(14):117-120.
[11] 周俊,王梦瑶,王改红,等.餐厨垃圾资源化利用技术研究现状及展望[J].生物资源,2020,42(1):87-96.
ZHOU J,WANG M Y,WANG G H,et al.Research status and prospect of food waste utilization technology[J].Biotic Resources,2020,42(1):87-96.
[12] HORNSBY C,RIPA M,VASSILLO C,et al.A roadmap towards integrated assessment and participatory strategies in support of decision-making processes.The case of urban waste management[J].Journal of Cleaner Production,2017,142:157-172.
[13] SRIVASTAVA R K,SHETTI N P,REDDY K R,et al.Sustainable energy from waste organic matters via efficient microbial processes[J].Science of the Total Environment,2020,722:137 927.
[14] 胡新军, 张敏,余俊锋,等.中国餐厨垃圾处理的现状、问题和对策[J].生态学报,2012,32(14):4 575-4 584.
HU X J,ZHANG M,YU J F,et al.Food waste management in China:status problems and solutions[J].Acta Ecologica Sinica,2012,32(14):4 575-4 584.
[15] YADAV A,GARG V K.Vermicomposting-An effective tool for the management of invasive weed Parthenium hysterophorus[J].Bioresource Technology,2011.102(10):5 891-5 895.
[16] ERIKSSON M,OSOWSKI C P,MALEFORS C,et al.Quantification of food waste in public catering services-A case study from a Swedish municipality[J].Waste Management,2017,61:415-422.
[17] ANJUM M,Al-MAKISHAH N H,BARAKAT M A.Wastewater sludge stabilization using pre-treatment methods[J].Process Safety and Environmental Protection,2016.102:615-632.
[18] 林艺芸. 预处理污泥与餐厨垃圾联合产氢试验研究[D].福州:福建师范大学,2008.
LIN Y Y.Research on anaerobic fermentative hydrogen production from combination substrates of pretreated sewage sludge and food waste[D].Fuzhou:Fujian Normol University,2008.
[19] 李燕红, 林钰,杏艳,等.农作物秸秆废弃物厌氧发酵生物制氢的研究[J].环境科学与技术,2006,11:8-9;117;115.
LI Y H,LIN Y,XING Y,et al.Biohydrogen production from wheat straw waste by dark fermentation[J].Environmental Science and Technology,2006,11:8-9;17;115.
[20] 严零陵,肖利平,袁雨珍.质量混合比对餐厨垃圾厌氧发酵产氢的影响[J].广州化学,2019,44(2):68-71;76.
YAN L L,XIAO L P,YUAN Y Z.Effect of mass mixing ratio on hydrogen production during anaerobic fermentation of kitchen waste[J].Guangzhou Chemistry,2019,44(2):68-71;76.
[21] GAO S M,HUANG Y,YANG L L,et al.Evaluation the anaerobic digestion performance of solid residual kitchen waste by NaHCO3 buffering[J].Energy Conversion and Management,2015.93:166-174.
[22] 王权, 宫常修,蒋建国,等.NaCl对餐厨垃圾厌氧发酵产VFA浓度及组分的影响[J].中国环境科学,2014,34(12):3 127-3 132.
WANG Q,GONG C X,JIANG J G,et al.Effect of NaCl content on VFA concentration and composition during anaerobic fermentation of kitchen waste[J].China Environmental Science,2014,34(12):3 127-3 132.
[23] ABUBACKAR H N,KESKIN T,ARSLAN K,et al.Effects of size and autoclavation of fruit and vegetable wastes on biohydrogen production by dark dry anaerobic fermentation under mesophilic condition[J].International Journal of Hydrogen Energy,2019,44(33):17 767-17 780.
[24] ZHAO G,MA F,WEI L,et al.Using rice straw fermentation liquor to produce bioflocculants during an anaerobic dry fermentation process[J].Bioresource Technology,2012,113:83-88.
[25] XU F Q,LI Y Y,GE X M,et al.Anaerobic digestion of food waste-Challenges and opportunities[J].Bioresource Technology,2018,247:1 047-1 058.
[26] 李迎新, 王勇,李彤,等.温度和物料配比对餐厨垃圾与果蔬垃圾协同厌氧产氢的影响研究[J].环境污染与防治,2018,40(3):259-264.
LI Y X,WANG Y,LI T,et al.Effects of temperature and raw material ratio on combined anaerobic hydrogen production potential of kitchen waste and fruit vegetable waste[J].Environmental Pollution & Control,2018,40(3):259-264.
[27] 江志坚. 果蔬与餐厨垃圾混合两相厌氧消化性能的试验研究[D].北京:北京化工大学,2013.
JIANG Z J.Performance of two-phase anaerobic co-digestion of fruit and vegetable waste and kitchen waste[D].Beijing:Beijing University of Chemical Technology,2013.
[28] 杜薇. 果蔬和餐厨垃圾混合干式厌氧消化性能及污泥流变行为研究[D].重庆:重庆大学,2018.
DU W.Dry anaerobic digestion performance and sludge rheological behavior of mixed FVW and FW[D].Chongqing:Chongqing University,2018.
[29] 占美丽, 董蕾,孙英杰,等.青岛市餐厨垃圾与菜市场垃圾混合高温厌氧消化研究[J].环境工程学报,2013,7(5):1 945-1 950.
ZHAN M L,DONG L,SUN Y J,et al.Study on thermophilic anaerobic digestion of mixture of kitchen wastes and vegetable market wastes in Qingdao[J].Chinese Journal of Environmental Engineering,2013,7(5):1 945-1 950.
[30] APHA.Standard methods for the examination of water and wastewater[S].Washington:American Public Health Association,1995.
[31] 中华人民共和国农业部.NY/T 1121.1—1121.21 土壤检测 土壤水溶性盐总量的测定[S].北京:中国农业出版社,2006.
Ministry of Agriculture of the People’s Republic of China.NY/T 1121.1—1121.21 Soil testing determination of total water-soluble salt in soil[S].Beijing:China Agricultural Press,2006.
[32] 张红漫, 郑荣平,陈敬文,等.NREL法测定木质纤维素原料组分的含量[J].分析试验室,2010,29(11):15-18.
ZHANG H M,ZHENG R P,CHEN J W,et al.Investigation on the determination of lignocellulosics components by NREL method[J].Chinese Journal of Analysis Laboratory,2010,29(11):15-18.
[33] THIEX N J,ANDERSON S,GILDEMEISTER B.Crude fat,diethyl ether extraction,in feed,cereal grain,and forage (Randall/Soxtec/submersion method):Collaborative study[J].Journal AOAC International,2003,86(5):888-898.
[34] HALL N G,SCHONFELDT H C,Total nitrogen vs.amino-acid profile as indicator of protein content of beef[J].Food Chemistry,2013,140(3):608-612.
文章导航

/