Batch anaerobic co-digestion of proteins and carbohydrates

被引：70

作者：

Elbeshbishy, Elsayed ^{[1
,2
]}

Nakhla, George ^{[1
]}

机构：

[1] Univ Western Ontario, Dept Chem & Biochem Engn, London, ON N6A 5B9, Canada

[2] Trojan Technol, London, ON N5V 4T7, Canada

来源：

BIORESOURCE TECHNOLOGY | 2012年 / 116卷

关键词：

Co-digestion; Proteins; Carbohydrate; Mixing ratio; Hydrolysis coefficient; ORGANIC WASTES; SOLID-WASTE; AMMONIA; INHIBITION; MUNICIPAL; KINETICS; DEGRADATION; HYDROLYSIS;

D O I：

10.1016/j.biortech.2012.04.052

中图分类号：

S2 [农业工程];

学科分类号：

0828 ;

摘要：

Batch anaerobic studies were conducted using five mixtures (M1-M5) of bovine serum albumin (BSA) and starch. The results showed that co-digestion of BSA and starch had a positive impact on the methane production. The highest methane production of 288 mL, the highest methane yield of 360 mL CH4/g CODadded, and the highest maximum methane production rate of 62 mL CH4/d were achieved for M4 (20% BSA and 80% starch). Most of the particulate proteins (90%) as well as particulate carbohydrates (95%) were degraded in the first 3 days. The hydrolysis coefficients of particulate proteins and particulate carbohydrates ranged from 0.65 to 1.01 d(-1) and from 0.53 to 1.06 d(-1), respectively. The highest methane production was achieved at C:N ratio of 12.8 for M4. For BSA only, propionic acid was the main volatile fatty acid (VFA), while for the starch only, butyric acid was the predominant VFA. (C) 2012 Elsevier Ltd. All rights reserved.

引用

页码：170 / 178

页数：9

共 36 条

[1] Anaerobic codigestion of municipal, farm, and industrial organic wastes:: A survey of recent literature [J].

Alatriste-Mondragon, Felipe ;

Samar, Parviz ;

Cox, Huub H. J. ;

Ahring, Birgitte K. ;

Iranpour, Reza .

WATER ENVIRONMENT RESEARCH, 2006, 78 (06) :607-636

[2] DETERMINATION OF BICARBONATE AND TOTAL VOLATILE ACID CONCENTRATION IN ANAEROBIC DIGESTERS USING A SIMPLE TITRATION [J].

ANDERSON, GK ;

YANG, G .

WATER ENVIRONMENT RESEARCH, 1992, 64 (01) :53-59

[3] Defining the biomethane potential (BMP) of solid organic wastes and energy crops: a proposed protocol for batch assays [J].

Angelidaki, I. ;

Alves, M. ;

Bolzonella, D. ;

Borzacconi, L. ;

Campos, J. L. ;

Guwy, A. J. ;

Kalyuzhnyi, S. ;

Jenicek, P. ;

van Lier, J. B. .

WATER SCIENCE AND TECHNOLOGY, 2009, 59 (05) :927-934

[4]

APHA (AMERICAN PUBLIC HEALTH ASSOCIATION), 1995, Standard Methods for the Examination of Water and Waste Water

[5] The influence of substrate kinetics on the microbial community structure in granular anaerobic biomass [J].

Batstone, DJ ;

Keller, J ;

Blackall, LL .

WATER RESEARCH, 2004, 38 (06) :1390-1404

[6] PROTEIN-DEGRADATION IN ANAEROBIC-DIGESTION - INFLUENCE OF VOLATILE FATTY-ACIDS AND CARBOHYDRATES ON HYDROLYSIS AND ACIDOGENIC FERMENTATION OF GELATIN [J].

BREURE, AM ;

MOOIJMAN, KA ;

VANANDEL, JG .

APPLIED MICROBIOLOGY AND BIOTECHNOLOGY, 1986, 24 (05) :426-431

[7] Inhibition of anaerobic digestion process: A review [J].

Chen, Ye ;

Cheng, Jay J. ;

Creamer, Kurt S. .

BIORESOURCE TECHNOLOGY, 2008, 99 (10) :4044-4064

[8]

Converti A, 1997, J CHEM TECHNOL BIOT, V69, P231, DOI 10.1002/(SICI)1097-4660(199706)69:2<231::AID-JCTB690>3.0.CO

[9]

2-7

[10] Will anaerobic digestion of solid waste survive in the future? [J].

De Baere, L .

WATER SCIENCE AND TECHNOLOGY, 2006, 53 (08) :187-194

← 1 2 3 4 →