超高温预处理对猪粪堆肥过程碳氮素转化与损失的影响

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摘要以猪粪、砻糠为原料，利用自行设计的超高温预处理装置，开展了为期56d的模拟堆肥试验，比较了超高温预处理好氧堆肥（HPC）和常规高温好氧堆肥（CK）过程中碳、氮素转化及损失.结果表明，CK有机质最大降解度（42.58%）比HPC堆体（49.29%）小，但降解速率常数（0.1d^-1）高于HPC（0.07d^-1），两种堆肥工艺碳素降解率差异不显著.HPC堆体NH₄⁺-N、TN质量分数平均比CK高143.9%、11.2%，而NO₃^--N质量分数则比CK低58.8%.HPC堆肥后期胡敏酸含量及腐殖质聚合程度分别比CK高45.2%~56.8%、59.1%~65.3%.在预处理阶段以及后续堆肥阶段，HPC、CK有机碳损失率分别为48%、51%，氮损失率分别为18%、27%.说明超高温预处理不仅有利于堆肥过程的保氮，而且促进富里酸向胡敏酸的转化，提高了堆肥产品腐殖化水平.

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	曹云
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	段会英
	徐跃定
	靳红梅
	常志州

关键词 ：超高温预处理, 堆肥, 氮损失, 有机质降解, 猪粪

Abstract：A period of 56d of simulated pig manure and rice husk composting experiment was carried out to study the conversion and loss of carbon (C) and nitrogen (N) in the novel hyperthermophilic pre-treatment plus an in-vessel post-composting process (HPC) and the conventional in-vessel composting (CK) process, by using a self-designed hyperthermerphilic pretreatment reactor. The results showed that the maximum carbon degradation degree in CK (42.58%) was smaller than that of HPC (49.29%), but the carbon degradation rate constant in CK (0.1d^-1) was greater than that of HPC (0.07d^-1). The difference in C degradation in the two composting processes was not significant overall. The concentrations of NH₄⁺-N and total N in the subsequent in-vessel composting of HPC were 143.9% and 11.2% higher than that in CK. The nitrate concentration in HPC, by contrast, was lowered by 58.8%. During composting, the content of humic acid (HA) and the ratio of HA to fulvic acid (FA) were on average 45.2%~56.8% and 59.1%~65.3% higher than that in CK duirng the later stage of composting. The carbon loss during the pretreatment process and subsequent in-vessel composting process in HPC and CK were 48% and 51%, respectively. The loss rates of N were 18% and 27% in HPC and CK, respectively. It was concluded that hyperthermophilic pretreatment could not only reduce the nitrogen loss significantly during composting process, but also promote the transformation of FA to HA, resulting in improved humification level of composting products.

Key words： hyperthermophilic pretreatment composting nitrogen loss organic matter degradation pig manure

收稿日期: 2017-10-23

X705

基金资助:国家重点研发计划（2016YFD0501401）；国家自然科学基金资助项目（41701340）；江苏省自然科学基金（BK20150542）；江苏省农业科学院院基金（027026111631）

通讯作者: 黄红英,研究员,sfmicrolab@163.com E-mail: sfmicrolab@163.com

作者简介: 曹云(1981-),女,江苏丹阳人,副研究员,博士,主要从事农业固体废弃物资源化利用研究.发表论文20余篇.

引用本文:

曹云, 黄红英, 孙金金, 吴华山, 段会英, 徐跃定, 靳红梅, 常志州. 超高温预处理对猪粪堆肥过程碳氮素转化与损失的影响[J]. 中国环境科学, 2018, 38(5): 1792-1800. CAO Yun, HUANG Hong-ying, SUN Jin-jin, WU Hua-shan, DUAN Hui-ying, XU Yue-ding, JIN Hong-mei, CHANG Zhi-zhou. Effect of hyperthermerphilic pretreatment on transformation and losses of C and N during pig manure composting. CHINA ENVIRONMENTAL SCIENCECE, 2018, 38(5): 1792-1800.

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http://www.zghjkx.com.cn/CN/ 或 http://www.zghjkx.com.cn/CN/Y2018/V38/I5/1792

[1]	陈菲菲,张崇尚,王艺诺,等.规模化生猪养殖粪便处理与成本收益分析[J]. 中国环境科学, 2017,37(9):3455-3463.
[2]	Paillat J, Robin P, Hassouna M, et al. Predicting ammonia and carbon dioxide emissions from carbon and nitrogen biodegradability during animal waste composting[J]. Atmospheric Environment, 2005,39:6833-6842.
[3]	Zhou Y, Selvam A, Wong J W C. Evaluation of humic substances during co-composting of food waste, sawdust and Chinese medicinal herbal residues[J]. Bioresource Technology, 2014,168:229-234
[4]	黄向东,韩志英,石德智,等.畜禽粪便堆肥过程中氮素的损失与控制[J]. 应用生态学报, 2010,21(1):247-254.
[5]	Nakhshiniev B, Perera C, Kunta M et al. Reducing ammonia volatilization during composting of organic waste through addition of hydrothermally treated lignocellulose[J]. International Biodeterioration & Biodegradation, 2014,96:58-62.
[6]	鲍艳宇,周启星,颜丽,等.畜禽粪便堆肥过程中各种氮化合物的动态变化及腐熟度评价指标[J]. 应用生态学报, 2008,19(2):374-380.
[7]	Lim S, Park H, Hao X, et al. Nitrogen, carbon, and dry matter losses during composting of livestock manure with two bulking agents as affected byco-amendments of phosphogypsum and zeolite[J]. Ecological Engineering, 2017,102:280-290.
[8]	Onwosi C O, Igbokwe V C, Odimba J N, et al. Composting technology in waste stabilization:On the methods, challenges and future prospects[J]. Journal of Environmental Management, 2017,190:140-157.
[9]	朱金龙,魏自民,贾璇,等.湿热水解预处理对餐厨废弃物液相物质转化的影响[J]. 环境科学研究, 2015,28(3):440-446.
[10]	杜静,陈广银,黄红英,等.温和湿热预处理对稻秸理化特性及生物产沼气的影响[J]. 中国环境科学, 2016,36(2):485-491.
[11]	Yamada T, Suzuki A, Ueda H. Successions of bacterial community in composting cow dung wastes with or without hyperthermophilic pre-treatment[J]. Applied Microbiological Biotechnology, 2008,81:771-781.
[12]	Yamada T, Keisuke M, Hideyo U, et al. Composting cattle dung wstes by using a hyperthermophilic pre-treatment process:characterization by physicochemical and molecular biological analysis[J]. Journal of bioscience and bioengineering, 2007, 104(5):408-415.
[13]	曹云,黄红英,钱玉婷,等.超高温预处理装置及其促进鸡粪稻秸好氧堆肥腐熟效果[J]. 农业工程学报, 2017,33(13):243-250.
[14]	鲍士旦.土壤农化分析[M]. 北京:中国农业出版社, 1999:25-27.
[15]	NY/T 1867-2010土壤腐殖质组成的测定[S].
[16]	Sanchez-Monedero M A, Cayuela M L, Roig A, et al. Role of biochar as an additive in organic waste composting[J]. Bioresource Technology, 2018,247:1155-1164.
[17]	Wang Q, Awasthi M K, Zhao J, et al. Improvement of pig manure compost lignocellulose degradation, organic matter humification and compost quality with medical stone[J]. Bioresource Technology, 2017,243:771-777.
[18]	周江明,王利通,徐庆华,等.适宜猪粪与菌渣配比提高堆肥效率[J]. 农业工程学报, 2015,31(7):201-207.
[19]	于子旋,杨静静,王语嫣,等.畜禽粪便堆肥的理化腐熟指标及其红外光谱[J]. 应用生态学报, 2016,27(6):2015-2023.
[20]	鲍艳宇,颜丽,娄翼来,等.鸡粪堆肥过程中各种碳有机化合物及腐熟度指标的变化[J]. 农业环境科学学报, 2005,4:820-824.
[21]	Hao X, Chang C, Larney F J. Carbon, nitrogen balances and greenhouse gas emission during cattle feedlot manure composting[J]. Journal of Environmenal Quality, 2004,33(1):37-44.
[22]	周俊强,邱忠平,韩云平,等.纤维素降解菌的筛选及其产酶特性[J]. 环境工程学报, 2010,3:704-708.
[23]	Ge J, Huang G, Huang J, et al. Mechanism and kinetics of organic matter degradation based on particle structure variation during pig manure aerobic composting[J]. Journal of Hazardous Materials, 2015,292(15):19-26.
[24]	Straathof A L, Comans R N J. Input materials and processing conditions control compost dissolved organic carbon quality[J]. Bioresource Technology, 2015,179:619-623.
[25]	Ashraf M T, Thomsen M H, Schmidt J E. Hydrothermal pretreatment and enzymatic hydrolysis of mixed green and woody lignocellulosics from arid regions[J]. Bioresource Technology, 2017,238:369-378.
[26]	Wang C, Huang C, Qian J, et al. Rapid and accurate evaluation of the quality of commercial organic fertilizers using near infrared spectroscopy[J]. PLOS one, 2013,9(2):8279-8284.
[27]	Wang H, Wang S Y, Li H Y, et al. Decomposition and humification of dissolved organic matter in swine manure during housefly larvae composting[J]. Waste Management & Research, 2016,34(5):465-473.
[28]	Zhang J, Lv B, Xing M, et al. Tracking the composition and transformation of humic and fulvic acids during vermicomposting of sewage sludge by elemental analysis and fluorescence excitationemission matrix[J]. Waste Management, 2015,39:111-118.
[29]	Bustamante M A, Paredes C, Marhuenda-Egea F C, et al. Co-composting of distillery wastes with animal manures:Carbon and nitrogen transformations in the evaluation of compost stability[J]. Chemosphere, 2008,72:551-557.
[30]	李国学,张福锁.固体废物堆肥化与有机复混肥生产[M]. 北京:化学工业出版社, 2000.
[31]	Kulikowska D. Kinetics of organic matter removal and humification progress during sewage sludge composting[J]. Waste Management, 2016,49:196-203.
[32]	Wang C, Tu Q, Dong D, et al. Spectroscopic evidence for biochar amendment promoting humicacid synthesis and intensifying humification during composting[J]. Journal of Hazardous Materials, 2014,280:409-416.
[33]	孙向平.不同控制条件下堆肥过程中腐殖质的转化机制研究[D]. 北京:中国农业大学, 2013.
[34]	Maeda K, Toyoda D H S, Yoshida N, et al. Microbiology of nitrogen cycle in animal manure compost[J]. Microbial Biotechnology, 2011,4(6):700-709.
[35]	姜继韶,黄懿梅,黄华,等.猪粪秸秆高温堆肥过程中碳氮转化特征与堆肥周期探讨[J]. 环境科学学报, 2011,31(11):2511-2517.
[36]	Li Q, Wang X C, Zhang H H, et al. Characteristics of nitrogen transformation and microbial community in an aerobic composting reactor under two typical temperatures[J]. Bioresource Technology, 2013,137:270-277.
[37]	Nigussie A, Bruun S, Kuyper T W, et al. Delayed addition of nitrogen-rich substrates during composting of municipal waste:Effects on nitrogen loss, greenhouse gas emissions and compost stability[J]. Chemosphere, 2017,166:352-362.
[38]	Wang Q, Awasthi M K, Ren X, et al. Comparison of biochar, zeolite and their mixture amendment for aiding organic matter transformation and nitrogen conservation during pig manure composting[J]. Bioresource Technology, 2017,245:300-308.
[39]	Li Y, Luo W, Li G, et al. Performance of phosphogypsum and calcium magnesium phosphate fertilizer for nitrogen conservation in pig manure composting[J]. Bioresource Technology, 2018,250:53-59.
[40]	Fukumoto Y, Suzuki K, Osada T, et al. Reduction of nitrous oxide emission from pig manure composting by addition of nitriteoxidizing bacteria[J]. Environmental Science and Technology, 2006,40:6787-6791.