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在添加和不添加奶牛粪便的水稻秸秆消化生物反应器中微生物群落组成和多样性。

Microbial community composition and diversity in rice straw digestion bioreactors with and without dairy manure.

机构信息

School of Engineering, Newcastle University, Cassie Building, Newcastle upon Tyne, NE1 7RU, UK.

Department of Civil and Environmental Engineering, University of Illinois at Urbana-Champaign, 205 North Mathews Ave, Urbana, IL, 61801, USA.

出版信息

Appl Microbiol Biotechnol. 2018 Oct;102(19):8599-8612. doi: 10.1007/s00253-018-9243-7. Epub 2018 Jul 27.

DOI:10.1007/s00253-018-9243-7
PMID:30051138
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC6153884/
Abstract

Anaerobic digestion (AD) uses a range of substrates to generate biogas, including energy crops such as globally abundant rice straw (RS). Unfortunately, RS is high in lignocellulosic material and has high to C:N ratios (~80:1), which makes it (alone) a comparatively poor substrate for AD. Co-digestion with dairy manure (DM) has been promoted as a method for balancing C:N ratios to improve RS AD whilst also treating another farm waste and co-producing a potentially useful fertiliser. However, past co-digestion studies have not directly compared RS AD microbial communities with and without DM additions, which has made it hard to assess all impacts of DM addition to RS AD processes. Here, four RS:DM ratios were contrasted in identical semi-continuous-fed AD bioreactors, and 100% RS was found to produce the highest specific methane yields (112 mL CH/g VS/day; VS, volatile solids), which is over double yields achieved in the reactor with the highest DM content (30:70 RS:DM by mass; 48 mL CH/g VS/day). To underpin these data, microbial communities were sequenced and characterised across the four reactors. Dominant operational taxonomic units (OTUs) in the 100% RS unit were Bacteroidetes/Firmicutes, whereas the 30:70 RS:DM unit was dominated by Proteobacteria/Spirochaetes, suggesting major microbial community shifts occur with DM additions. However, community richness was lowest with 100% RS (despite higher specific yields), suggesting particular OTUs may be more important to yields than microbial diversity. Further, ambient VFA and VS levels were significantly higher when no DM was added, suggesting DM-amended reactors may cope better with higher organic loading rates (OLR). Results show that RS AD without DM addition is feasible, although co-digestion with DM will probably allow higher OLRs, resulting in great RS throughput in farm AD units.

摘要

厌氧消化(AD)利用一系列基质来产生沼气,包括全球丰富的水稻秸秆(RS)等能源作物。不幸的是,RS 富含木质纤维素物质,且 C:N 比高(~80:1),这使得它(单独)作为 AD 的底物相对较差。与奶牛粪便(DM)共消化已被推广为一种平衡 C:N 比的方法,以提高 RS AD 的效率,同时处理另一种农场废物并共同生产一种潜在有用的肥料。然而,过去的共消化研究并没有直接比较添加和不添加 DM 的 RS AD 微生物群落,这使得难以评估 DM 添加对 RS AD 过程的所有影响。在这里,四个 RS:DM 比例在相同的半连续进料 AD 生物反应器中进行了对比,发现 100% RS 产生了最高的特定甲烷产量(112 mL CH/g VS/天;VS,挥发性固体),这超过了 DM 含量最高的反应器(质量比为 30:70 RS:DM;48 mL CH/g VS/天)的产量。为了支持这些数据,对四个反应器中的微生物群落进行了测序和表征。在 100% RS 单元中占主导地位的操作分类单元(OTU)是拟杆菌门/厚壁菌门,而 30:70 RS:DM 单元则以变形菌门/螺旋体门为主,这表明随着 DM 的添加,微生物群落发生了重大变化。然而,在没有 DM 添加的情况下,100% RS 的群落丰富度最低(尽管产量较高),这表明某些 OTU 对产量的重要性可能高于微生物多样性。此外,当不添加 DM 时,环境 VFA 和 VS 水平显著升高,这表明添加 DM 的反应器可能更能适应更高的有机负荷率(OLR)。结果表明,不添加 DM 的 RS AD 是可行的,尽管与 DM 共消化可能会允许更高的 OLR,从而在农场 AD 单元中实现更高的 RS 吞吐量。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/bc79/6153884/19754b7458fc/253_2018_9243_Fig5_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/bc79/6153884/bb9ab1e12a5e/253_2018_9243_Fig1_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/bc79/6153884/7fbbf7da88d0/253_2018_9243_Fig2_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/bc79/6153884/c3327d531759/253_2018_9243_Fig3_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/bc79/6153884/9f36a21c58b8/253_2018_9243_Fig4_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/bc79/6153884/19754b7458fc/253_2018_9243_Fig5_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/bc79/6153884/bb9ab1e12a5e/253_2018_9243_Fig1_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/bc79/6153884/7fbbf7da88d0/253_2018_9243_Fig2_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/bc79/6153884/c3327d531759/253_2018_9243_Fig3_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/bc79/6153884/9f36a21c58b8/253_2018_9243_Fig4_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/bc79/6153884/19754b7458fc/253_2018_9243_Fig5_HTML.jpg

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