Substrate influence on the structure of methanogenic Archaea communities during anaerobic digestion
D. Dąbrowska, K. Bułkowska, S. Ciesielski
{"title":"Substrate influence on the structure of methanogenic Archaea communities during anaerobic digestion","authors":"D. Dąbrowska, K. Bułkowska, S. Ciesielski","doi":"10.14799/EBMS264","DOIUrl":null,"url":null,"abstract":"This study compares the diversity of methanogenic archaeal communities that developed during biogas production in reactors fed with different substrates. Reactor I was fed with silages of maize and of alfalfa and timothy; and Reactor II was fed with these silages plus pig slurry and glycerol as co‐substrates. The archaeal community structure was studied using polymerase chain reaction–denaturing gradient gel © UNIVERSITY OF WARMIA AND MAZURY IN OLSZTYN IN TRO DUC TION Methane fermentation has recently been a subject of much interest because methane is a renewable energy source and fermentation provides a way to utilize waste. For better methane production, the process parameters can be adjusted for the specific waste product being used as a substrate, and co-substrates can be added. In this way, greater process stability can be achieved, and the quantity and methane content of biogas can be increased (Bułkowska et al. 2012). Although it is known that the Archaea are one of the groups of microorganisms that perform methane fermentation, their community structure and diversity are poorly understood, as is the effect of conditions in the bioreactor on these community characteristics (Ciesielski et al. 2013). For example, the choice of feedstock can affect these characteristics (Ziganshin et al. 2013). The feedstock that is chosen can come from a variety of industries, and its choice can depend on the availability of raw materials. Although in Europe, the materials most commonly used in biogas production are plant-based, some animal-derived organic wastes and other organic wastes are also used, such as pig slurry or glycerol from the biodiesel industry (Hijazi et al. 2016). The effect on biogas production of addition of substrates that are not plant-based has been investigated (Bułkowska et al. 2012). However, little is known about how the diversity of the archaeal community is affected when glycerol and pig slurry are added as co-substrates to plantbased substrates. 42 ENVIRONMENTAL BIOTECHNOLOGY 11 (2) 2015 column was then centrifuged for 1 minute at high speed before the filtrate was poured out and washed twice with A1 solution (A&A Biotechnology). The DNA was then suspended in 50μL of water and stored at -20°C until further analysis. Polymerase chain reaction Genomic DNA was amplified using polymerase chain reaction (PCR). The gene fragment encoding for 16S rRNA was amplified using a pair of primers (GC-0357F-5’ CGCCCGCCGCGCCCCGCGCCCGTCCCGCCGCCCC CGCCCGCCCTACGGGGCGCAGCAG 3’; 0691R-5’ GG ATTACATGATTTCAC 3’) (Watanabe et al. 2004). The amplified fragments measured approximately 500bp. The PCR mix (30μL per reaction) was composed of 3μL of 10×PCR buffer, 2.4μL MgCl2 (25mM), 1.3μL of dNTPs (200μM final concentration), 0.15μL Taq polymerase (2 U·1μL-1·reaction-1), 0.5μL of each primer (20pmol), 18.15μL of dH2O and 1μL of genomic DNA. Reactions were performed in 0.5mL DNA-free PCR tubes using a thermocycler, and the PCR steps were as follows: denaturation at 94°C for 10min, followed by 30 cycles of denaturation at 94°C for 1min, annealing at 54°C for 1min in the initial cycle, and then for a period that was 2 seconds shorter after each subsequent cycle, and extension at 72°C for 1min. After completion, an additional extension step was performed at 72°C for 10min, and the samples were then chilled to 4°C. The length of the PCR product was verified on 1% agarose gel, stained with ethidium bromide, and visualized and photographed under UV light. Denaturing Gradient Gel Electrophoresis (DGGE) PCR products with a GC clamp were resolved in 6% polyacrylamide gel (37.5:1 acrylamide:bisacrylamide) with a gradient ranging from 30 to 60% urea. Electrophoresis was performed for 12h at 60V in 1xTAE buffer (2M Tris base, 2M acetic acid, 0.05M EDTA) using the DCodeTM Universal Mutation Detection System (Bio-Rad Laboratories Inc., U.S.A.). The DNA mixture resolved in gel was visualized by staining with 1:10,000 SybrGold (Invitrogen) for 20 minutes followed by UV transillumination. Images were recorded and analyzed with KODAK 1D 3.6 Image Analysis Software.","PeriodicalId":11733,"journal":{"name":"Environmental biotechnology","volume":null,"pages":null},"PeriodicalIF":0.0000,"publicationDate":"2015-01-01","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"2","resultStr":null,"platform":"Semanticscholar","paperid":null,"PeriodicalName":"Environmental biotechnology","FirstCategoryId":"1085","ListUrlMain":"https://doi.org/10.14799/EBMS264","RegionNum":0,"RegionCategory":null,"ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"","JCRName":"","Score":null,"Total":0}
引用次数: 2
Abstract
This study compares the diversity of methanogenic archaeal communities that developed during biogas production in reactors fed with different substrates. Reactor I was fed with silages of maize and of alfalfa and timothy; and Reactor II was fed with these silages plus pig slurry and glycerol as co‐substrates. The archaeal community structure was studied using polymerase chain reaction–denaturing gradient gel © UNIVERSITY OF WARMIA AND MAZURY IN OLSZTYN IN TRO DUC TION Methane fermentation has recently been a subject of much interest because methane is a renewable energy source and fermentation provides a way to utilize waste. For better methane production, the process parameters can be adjusted for the specific waste product being used as a substrate, and co-substrates can be added. In this way, greater process stability can be achieved, and the quantity and methane content of biogas can be increased (Bułkowska et al. 2012). Although it is known that the Archaea are one of the groups of microorganisms that perform methane fermentation, their community structure and diversity are poorly understood, as is the effect of conditions in the bioreactor on these community characteristics (Ciesielski et al. 2013). For example, the choice of feedstock can affect these characteristics (Ziganshin et al. 2013). The feedstock that is chosen can come from a variety of industries, and its choice can depend on the availability of raw materials. Although in Europe, the materials most commonly used in biogas production are plant-based, some animal-derived organic wastes and other organic wastes are also used, such as pig slurry or glycerol from the biodiesel industry (Hijazi et al. 2016). The effect on biogas production of addition of substrates that are not plant-based has been investigated (Bułkowska et al. 2012). However, little is known about how the diversity of the archaeal community is affected when glycerol and pig slurry are added as co-substrates to plantbased substrates. 42 ENVIRONMENTAL BIOTECHNOLOGY 11 (2) 2015 column was then centrifuged for 1 minute at high speed before the filtrate was poured out and washed twice with A1 solution (A&A Biotechnology). The DNA was then suspended in 50μL of water and stored at -20°C until further analysis. Polymerase chain reaction Genomic DNA was amplified using polymerase chain reaction (PCR). The gene fragment encoding for 16S rRNA was amplified using a pair of primers (GC-0357F-5’ CGCCCGCCGCGCCCCGCGCCCGTCCCGCCGCCCC CGCCCGCCCTACGGGGCGCAGCAG 3’; 0691R-5’ GG ATTACATGATTTCAC 3’) (Watanabe et al. 2004). The amplified fragments measured approximately 500bp. The PCR mix (30μL per reaction) was composed of 3μL of 10×PCR buffer, 2.4μL MgCl2 (25mM), 1.3μL of dNTPs (200μM final concentration), 0.15μL Taq polymerase (2 U·1μL-1·reaction-1), 0.5μL of each primer (20pmol), 18.15μL of dH2O and 1μL of genomic DNA. Reactions were performed in 0.5mL DNA-free PCR tubes using a thermocycler, and the PCR steps were as follows: denaturation at 94°C for 10min, followed by 30 cycles of denaturation at 94°C for 1min, annealing at 54°C for 1min in the initial cycle, and then for a period that was 2 seconds shorter after each subsequent cycle, and extension at 72°C for 1min. After completion, an additional extension step was performed at 72°C for 10min, and the samples were then chilled to 4°C. The length of the PCR product was verified on 1% agarose gel, stained with ethidium bromide, and visualized and photographed under UV light. Denaturing Gradient Gel Electrophoresis (DGGE) PCR products with a GC clamp were resolved in 6% polyacrylamide gel (37.5:1 acrylamide:bisacrylamide) with a gradient ranging from 30 to 60% urea. Electrophoresis was performed for 12h at 60V in 1xTAE buffer (2M Tris base, 2M acetic acid, 0.05M EDTA) using the DCodeTM Universal Mutation Detection System (Bio-Rad Laboratories Inc., U.S.A.). The DNA mixture resolved in gel was visualized by staining with 1:10,000 SybrGold (Invitrogen) for 20 minutes followed by UV transillumination. Images were recorded and analyzed with KODAK 1D 3.6 Image Analysis Software.
厌氧消化过程中底物对产甲烷古菌群落结构的影响
本研究比较了不同基质反应器产气过程中产生的产甲烷古菌群落的多样性。一号反应器用玉米、苜蓿和提摩西青贮饲料饲喂;反应器II用这些青贮饲料加猪浆和甘油作为共底物。利用聚合酶链反应-变性梯度凝胶研究古细菌群落结构©瓦姆尼亚和马祖里大学IN OLSZTYN IN TRO DUC生产甲烷发酵最近成为一个非常感兴趣的主题,因为甲烷是一种可再生能源,发酵提供了一种利用废物的方法。为了更好地生产甲烷,可以根据用作底物的特定废物调整工艺参数,并可以添加辅助底物。这样可以获得更大的工艺稳定性,并可以增加沼气的数量和甲烷含量(Bułkowska et al. 2012)。虽然已知古生菌是进行甲烷发酵的微生物群之一,但人们对其群落结构和多样性知之甚少,生物反应器条件对这些群落特征的影响也是如此(Ciesielski et al. 2013)。例如,原料的选择会影响这些特性(Ziganshin et al. 2013)。所选择的原料可以来自各种行业,其选择可以取决于原材料的可用性。虽然在欧洲,沼气生产中最常用的材料是植物性的,但也使用一些动物来源的有机废物和其他有机废物,例如来自生物柴油行业的猪浆或甘油(Hijazi et al. 2016)。已经研究了添加非植物基基质对沼气生产的影响(Bułkowska等人,2012)。然而,当甘油和猪浆作为共底物添加到植物基底物中时,古细菌群落的多样性是如何受到影响的,人们知之甚少。42 ENVIRONMENTAL BIOTECHNOLOGY 11(2) 2015柱高速离心1分钟后,倒出滤液,用A1溶液(A&A BIOTECHNOLOGY)洗涤2次。将DNA悬浮于50μL水中,-20℃保存,待进一步分析。采用聚合酶链反应(PCR)扩增基因组DNA。编码16S rRNA的基因片段使用一对引物(GC-0357F-5’cgcccgccgcgccccgcgcccccccccccccccccccgccccccctacggggcgcagcag 3’;0691R-5 ' GG ATTACATGATTTCAC 3 ') (Watanabe et al. 2004)。扩增片段的测量值约为500bp。PCR混合物(每反应30μL)由3μL 10×PCR缓冲液、2.4μL MgCl2 (25mM)、1.3μL dNTPs(终浓度200μM)、0.15μL Taq聚合酶(2 μ U·1μL-1·reaction-1)、0.5μL每个引物(20pmol)、18.15μL dH2O和1μL基因组DNA组成。用热循环仪在0.5mL无dna PCR管中进行反应,PCR步骤如下:94℃变性10min, 94℃变性1min,初始循环30个循环,54℃退火1min,每个循环后延长2秒,72℃延长1min。完成后,在72°C下进行额外延长步骤10min,然后将样品冷却至4°C。在1%琼脂糖凝胶上验证PCR产物的长度,用溴化乙啶染色,在紫外光下观察和拍照。变性梯度凝胶电泳(DGGE) PCR产物用GC钳在6%聚丙烯酰胺凝胶(37.5:1丙烯酰胺:双丙烯酰胺)中分离,梯度范围为30 - 60%尿素。采用DCodeTM通用突变检测系统(Bio-Rad Laboratories Inc., usa),在1 × tae缓冲液(2M Tris碱基,2M乙酸,0.05M EDTA)中,在60V下电泳12h。用1:10 000 SybrGold (Invitrogen)染色20分钟,然后紫外透照,可见凝胶中溶解的DNA混合物。使用KODAK 1D 3.6图像分析软件记录和分析图像。
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