耐高温厨余垃圾降解菌的分离、驯化与应用

为提高厨余垃圾减量效率,从不同来源的垃圾样品中分离筛选高效耐高温降解菌株应用于厨余垃圾降解。经平板涂布和划线分离法筛选共获得18株耐高温菌株,进一步利用平板透明圈法考察菌株对淀粉、蛋白、脂肪和纤维素的降解能力,最终获得4株耐高温强降解能力的菌株;经形态学和分子生物学鉴定,菌株分别为枯草芽孢杆菌(Bacillus subtilis)、短小芽孢杆菌(Bacillus pumilus)、特基拉芽孢杆菌(Bacillus tequilensis)和嗜温鞘氨醇杆菌(Sphingobacterium thalpophilum);为进一步提高厨余垃圾减量性能,以厨余垃圾浸出液作为培养基,对菌株进行定向驯化并制备复合菌剂,应用于厨余垃圾处理器,48 h后厨余垃圾质量减少了73.8%,与对照组相比,质量减少率分别提高约10%和35.1%。本研究利用厨余垃圾浸出液对筛选获得的菌株进行驯化和制备培养,不仅提高了菌剂降解活性,而且实现了废弃物的资源化利用。     

水产源芽胞杆菌的分离鉴定及生物学功能分析

筛选具有较好生物学功能的芽胞杆菌(Bacillus),用以改善池塘养殖过程饲料等有机物降解、抑制水体中的病原菌,对从健康养殖鱼虾塘水体中分离的菌株,进行生化试验和16S rDNA序列分子鉴定;通过产酶、耐酸、耐高温试验,抑菌试验以及安全性试验研究分离菌株的生物学功能。试验共筛选出8株细菌,经生化试验及16S rDNA序列的分子鉴定,确定菌株ZHX17、ZHX18、ZHX31为贝莱斯芽胞杆菌（Bacillus velezensis）,菌株ZHX14、ZHX15为地衣芽胞杆菌（Bacillus licheniformis）、菌株NSX4、NSX7、NSX9为枯草芽胞杆菌（Bacillus subtilis）。试验结果表明,8株芽胞杆菌均具有较强的耐酸、耐高温特性,其中3株贝莱斯芽胞杆菌具有较强的分泌淀粉酶、纤维素酶、蛋白酶的能力,抑菌效果好于其他5株芽胞杆菌。安全性试验结果表明,8株芽胞杆菌对草鱼、罗非鱼相对安全。8株芽胞杆菌同时具备分泌淀粉酶、纤维素酶和蛋白酶3种胞外酶的能力,其中贝莱斯芽胞杆菌具有较强的病原菌抑菌能力,可以作为病原拮抗益生菌做进一步研究。     

1株大熊猫肠道纤维素降解菌的分离鉴定及其酶学性质

以羧甲基纤维素钠为唯一碳源,利用刚果红染色法,从大熊猫粪便内筛选具有降解纤维素能力的菌株,并研究其酶学特性。分离获得1株酶活力较高的菌株A1,通过形态学和BD PhoenixTM-100全自动细菌鉴定仪鉴定为蜡样芽胞杆菌(Bacillus cereus)。菌株A1最适生长条件和酶活力测定表明,其最适生长温度为37℃,Na Cl浓度为0.5%,p H值为7.0,内切葡聚糖苷酶、外切葡聚糖苷酶、β-葡萄糖苷酶和总酶活的最大值分别为0.139、0.074、0.126、0.108 5 IU/m L。丰富了大熊猫肠道纤维素降解菌的种类,为后续研究大熊猫如何消化利用竹纤维提供了菌源。     

辣椒镰孢根腐病防病促生细菌的筛选及其效应

【目的】筛选辣椒(Capsicum annuum L.)根腐病防病促生细菌并明确其防病促生效应。【方法】采集健康辣椒根围土壤样品,以辣椒根腐病病原真菌茄镰孢(Fusarium solani)和尖镰孢(Fusarium oxysporum)为指示菌,采用平板对峙法筛选生防细菌,采用选择性培养基筛选溶无机磷、溶有机磷、固氮菌和解钾菌等促生菌,钼锑抗比色法测定溶磷量,凯氏定氮法测定固氮量,火焰原子吸收光谱法测定解钾量。对特性良好组合的菌株进行16S rDNA序列分析鉴定并制作菌剂,最后采用盆栽法测定菌剂防病促生效果。【结果】共筛选得到323株特性良好的功能菌株,拮抗菌78株,溶有机磷菌87株,溶无机磷菌107株,固氮菌128株,解钾菌123株,部分菌株同时具有多个功能特性。互作组合得到6个特性良好的菌株组合,包括8株功能菌株,鉴定发现XP271和XP181为枯草芽胞杆菌(Bacillus subtilis),XP125为特基拉芽胞杆菌(Bacillus tequilensis),XP236为耐盐芽胞杆菌(Bacillus halotolerans),XP79为巨大芽胞杆菌(Bacillus ...     

菠萝渣淀粉功能降解菌筛选及s2b7-4的鉴定

为了加快菠萝渣发酵,本试验通过利用多种选择性培养基,从自然发酵的菠萝渣中分离到多种淀粉分解菌,经过初筛和复筛,获得了降解菠萝渣的淀粉降解功能菌株s2b7-1和s2b7-4,筛选出其最适培养基为改良LB培养基及其优化组合。通过形态、生理生化和分子综合鉴定得出s2b7-4菌株为枯草芽胞杆菌(Bacillus subtilis)。     

应用混料实验设计制备秸秆复合降解菌剂

农业秸秆类废弃物含有大量木质纤维素,该类物质结构稳定,不易降解,为秸秆的合理利用带来诸多困难。本实验尝试利用混料实验设计对筛选出可以共同培养的五种木质纤维素降解菌的配比进行研究,寻求复合发酵降解剂各组分的最佳配比,并分析发酵产品得到适用于不同发酵目的的菌剂。通过对发酵产品中木质素和纤维素降解率及还原糖的含量的分析建立模型,分析预测纤维素降解率最高为35.75%,木质素降解率最高为27%,还原糖含量最高为3.39mg/g。通过优化得出发酵菌剂最优配比为枯草芽胞杆菌12.1%,克鲁斯假丝酵母10%,地衣芽胞杆菌27.2%,变色栓菌10.6%,黄孢原毛平革菌40%。对应三指标的实测值为：35.47%,26.41%和2.37mg/g。     

1株产聚-β-羟基丁酸芽胞杆菌的分离、筛选与鉴定

从浙江省金华市花生地土样中筛选、分离纯化得到1株产聚-β-羟基丁酸编号为PX-95的芽胞杆菌,PHB产量为135.81 mg/L。根据形态特征、生理生化特征初步鉴定为芽胞杆菌属蜡样芽胞杆菌群,16S rDNA序列分析显示PX-95菌株与苏云金芽胞杆菌以及蜡样芽胞杆菌均具有高度同源性,最后采用扩增gyrB（DNA促旋酶B亚单位）基因的方法将其鉴定为苏云金芽胞杆菌（Bacillus thuringiensis）。     

枯草芽胞杆菌降解木质纤维素能力及产酶研究

从农林废物堆肥中分离得到1株细菌经鉴定为枯草芽胞杆菌,将该细菌用于木质素类化合物利用.固态培养条件下考察其对木质纤维素的降解能力及产酶特性,另外对发酵前后的稻草结构进行了红外光谱分析.结果表明,枯草芽胞杆菌具有木质素降解能力,兼具低分子量木质素酚型、非酚型类物质的降解能力.其对木质素降解是木质素过氧化物酶、锰过氧化物酶、漆酶、纤维素酶和半纤维素酶共同作用的结果.在实验条件下,培养30 d使木质素降解率达9.47%,同时对纤维素、半纤维素也有较高程度的降解;降解率分别为38.8%、41.84%.红外光谱分析结果表明,稻草木质素结构被破坏,枯草芽胞杆菌对木质素各官能团的降解作用有所不同.     

复合菌系降解纤维素过程中微生物群落结构的变化

为明确高效纤维素降解复合菌系降解过程中微生物群落结构的变化规律及关键的降解功能菌,利用该复合菌系对滤纸和稻秆进行生物处理,通过底物降解、微生物生长量、发酵液pH的变化情况,选择不同降解时期复合菌系提取的总DNA进行细菌16S rRNA基因扩增子高通量测序。通过分解特性试验确定在接种后培养第12、72、168 h分别作为降解初期、高峰期、末期。该复合菌系分别主要由1个门、2个纲、2个目、7个科、11个属组成。随着降解的进行,短芽胞杆菌属Brevibacillus、喜热菌属Caloramator的相对丰度逐渐降低;梭菌属Clostridium、芽胞杆菌属Bacillus、地芽胞杆菌属Geobacillus、柯恩氏菌属Cohnella的相对丰度逐渐升高;解脲芽胞杆菌属Ureibacillus、泰氏菌属Tissierella、刺尾鱼菌属Epulopiscium在降解高峰期时相对丰度最高;各时期类芽胞杆菌属Paenibacillus、瘤胃球菌属Ruminococcus的相对丰度无明显变化。上述11个主要菌属均属于厚壁菌门,具有嗜热、耐热、适应广泛pH、降解纤维素或半纤维素的特性。好氧型细菌是降解初期的主要优势功能菌,到中后期厌氧型细菌逐渐增多,并逐步取代好氧型细菌成为降解纤维素的主要细菌。     

一小型温泉中降解淀粉细菌的筛选、鉴定与淀粉酶性质初步分析

为筛选耐热淀粉酶产生菌并揭示其在温泉中的分布情况,从腾冲县腊幸村一小型热泉不同部位采集样品进行微生物分离及鉴定。样品在65℃培养,挑选形态有差异的菌落点种淀粉-台盼蓝平板,共获得34株具有淀粉降解能力的细菌。分子鉴定结果显示,从温泉底部沙土中筛选得到细菌具有较高的生物多样性,9株具有淀粉降解能力的细菌分别属于土芽胞杆菌(Geobacillus)、厌氧芽胞杆菌(Anoxybacillus)和芽胞杆菌(Bacillus)3个属、7个种,菌株间16S rDNA序列均有一定的差异。对编号为201(Geobacillus thermoglucosidasius)和208(Anoxybacillus flavithermus)的菌株胞外淀粉酶进行初步分析,其胞外淀粉酶最适温度分别为60和70℃,均高于淀粉糊化温度,具有一定的应用潜力。     

氯嘧磺隆降解菌的分离鉴定及其降解特性

利用富集培养技术从长期施用氯嘧磺隆的土壤中分离得到1株能够降解氯嘧磺隆的细菌L-7。通过生理生化特性和16SrRNA序列分析,初步鉴定L-7为寡养单胞菌属(Stenotrophomonas sp.)。并分析了氯嘧磺隆的初始浓度、接种量、温度和pH值对L-7菌株降解氯嘧磺隆效果的影响,确定了最佳降解条件。结果表明,该菌在氯嘧磺隆浓度为100mg/L、接种量为5%、pH4.0、温度30°C条件下,接种5d后对氯嘧磺隆的降解效率达到80%以上。     

小花盾叶薯蓣甙的酶降解

从小花盾叶薯蓣(Dioscorea parviflora C. T. Ting)的新鲜根状茎中分离到一个新的呋甾烷型配糖体,命名为小花盾叶薯蓣甙(parvifloside) (1),其结构通过波谱和化学方法鉴定为:(25R)-26-O-β-glucopyranosyl-furost-5-en-3β, 22ξ, 26-triol 3-O-β-D-glucopyranosyl (1→3)-β-D-glucopyranosyl (1→4)-[α-L-rhamnopyranosyl (1→2)]-β-D-glucopyranoside.化合物1在纤维素酶粗酶和β-葡萄糖苷酶中进行水解,得到降解产物2-7.对1的酶解现象进行了讨论.同时,对所分离的甾体皂甙的抗稻瘟霉菌活性进行了初步筛选.     

Bacterial Degradation of EDTA

Degradation of EDTA (ethylenediaminetetraacetic acid) or metal–EDTA complexes by cell suspensions of the bacterial strain DSM 9103 was studied. The activity of EDTA degradation was the highest in the phase of active cell growth and decreased considerably in the stationary phase, after substrate depletion in the medium. Exponential-phase cells were incubated in HEPES buffer (pH 7.0) with 1 mM of uncomplexed EDTA or EDTA complexes with Mg²⁺, Ca²⁺, Mn²⁺, Pb²⁺, Co²⁺, Cd²⁺, Zn²⁺, Cu²⁺, or Fe³⁺. The metal–EDTA complexes (Me–EDTA) studied could be divided into three groups according to their degradability. EDTA complexes with stability constants K below 10¹⁶ (log K < 16), such as Mg–EDTA, Ca–EDTA, and Mn–EDTA, as well as uncomplexed EDTA, were degraded by the cell suspensions at a constant rate to completion within 5–10 h of incubation. Me–EDTA complexes with log K above 16 (Zn–EDTA, Co–EDTA, Pb–EDTA, and Cu–EDTA) were not completely degraded during a 24-h incubation, which was possibly due to the toxic effect of the metal ions released. No degradation of Cd–EDTA or Fe(III)–EDTA by cell suspensions of strain DSM 9103 was observed under the conditions studied.     

Bacterial Degradation of N-Lauroyl-L-valine

Studies were conducted on the degradation of N-lauroyl-L-valine by type cultured bacteria. Many strains could utilize sodium N-lauroyl-L-valinate as carbon and nitrogen sources for their growth. Metabolism of N-lauroyl-L-valine was investigated in detail using Ps. aeruginosa AJ2116. Laurie acid was identified by gas chromatography suggesting cleavage of N-acyl linkage in N-lauroyl-L-valine.

Laurie acid might be metabolized to capric acid (C₁₀) and caprylic acid (C₈) becuase the accumulated substances gave nearly identical peaks with those of authentic fatty acids on gas chromatograms. The experiment using N-lauroyl-L-valine (¹⁴C) indicated that ¹⁴CO₂ was produced as a final product. Valine was not detected because it might be metabolized very rapidly immediately after its release.

It was supposed that the enzymes or enzyme systems degrading N-lauroyl-L-valine might be constitutive from the experiment using two kinds of cells grown in the medium containing N-lauroyl-L-valine or nutrient broth.     

小花盾叶薯蓣甙的酶降解

从小花盾叶薯蓣 (DioscoreaparvifloraC .T .Ting)的新鲜根状茎中分离到一个新的呋甾烷型配糖体 ,命名为小花盾叶薯蓣甙 (parvifloside) (1) ,其结构通过波谱和化学方法鉴定为 :(2 5R)_2 6_O_β_glucopyranosyl_furost_5_en_3β ,2 2 ξ ,2 6_triol 3_O_β_D_glucopyranosyl (1→ 3)_β_D_glucopyranosyl (1→ 4 )_[α_L_rhamnopyranosyl (1→ 2 ) ]_β_D_glucopyra noside。化合物 1在纤维素酶粗酶和 β_葡萄糖苷酶中进行水解 ,得到降解产物 2 - 7。对 1的酶解现象进行了讨论。同时 ,对所分离的甾体皂甙的抗稻瘟霉菌活性进行了初步筛选。     

花色苷的酶降解

综述了降解花色苷的酶类及其降解机理的研究进展.降解花色苷的酶有花色苷酶、多酚氧化酶、过氧化物酶和果胶酶.花色苷酶和果胶酶均能水解花色苷糖苷键产生花色素和糖,花色素很不稳定,因吡喃烊环极易开环可自发转换成无色衍生物.花色苷不能直接作为PPO或POD的底物;PPO和POD氧化、降解花色苷须依赖具邻二酚结构的其他酚类的存在,...     

Enzymatic Degradation of GlycosaminogIycans

Abstract

Glycosarninoglycans (GAGs) play an intricate role in the extracellular matrix (ECM), not only as soluble components and polyelectrolytes, but also by specific interactions with growth factors and other transient components of the ECM. Modifications of GAG chains, such as isomerization, sulfation, and acetylation, generate the chemical specificity of GAGs. GAGS can be depolymerized enzymatically either by eliminative cleavage with lyases (EC 4.2.2.-) or by hydrolytic cleavage with hydrolases (EC 3.2.1.-). Often, these enzymes are specific for residues in the polysaccharide chain with certain modifications. As such, the enzymes can serve as tools for studying the physiological effect of residue modifications and as models at the molecular level of protein-GAG recognition. This review examines the structure of the substrates, the properties of enzymatic degradation, and the enzyme substrate-interactions at a molecular level. The primary structure of several GAGS is organized macro-scopicallyby segregation into alternating blocks of specific sulfation patterns and microscopicallyby formation of oligosaccharide sequences with specific binding functions. Among GAGs, considerable dermatan sulfate, heparin and heparan sulfate show conformational flexibility in solution. They elicit sequence-specific interactions with enzymes that degrade them, as well as with other proteins, however, the effect of conformational flexibility on protein-GAG interactions is not clear. Recent findings have established empirical rules of substrate specificity and elucidated molecular mechanisms of enzyme-substrate interactions for enzymes that degrade GAGs. Here we propose that local formation of polysaccharide secondary structure is determined by the immediate sequence environment within the GAG polymer, and that this secondary structure, in turn, governs the binding and catalytic interactions between proteins and GAGs.     

Aerobic Degradation of Dinitrotoluenes and Pathway for Bacterial Degradation of 2,6-Dinitrotoluene

An oxidative pathway for the mineralization of 2,4-dinitrotoluene (2,4-DNT) by Burkholderia sp. strain DNT has been reported previously. We report here the isolation of additional strains with the ability to mineralize 2,4-DNT by the same pathway and the isolation and characterization of bacterial strains that mineralize 2,6-dinitrotoluene (2,6-DNT) by a different pathway. Burkholderia cepacia strain JS850 and Hydrogenophaga palleronii strain JS863 grew on 2,6-DNT as the sole source of carbon and nitrogen. The initial steps in the pathway for degradation of 2,6-DNT were determined by simultaneous induction, enzyme assays, and identification of metabolites through mass spectroscopy and nuclear magnetic resonance. 2,6-DNT was converted to 3-methyl-4-nitrocatechol by a dioxygenation reaction accompanied by the release of nitrite. 3-Methyl-4-nitrocatechol was the substrate for extradiol ring cleavage yielding 2-hydroxy-5-nitro-6-oxohepta-2,4-dienoic acid, which was converted to 2-hydroxy-5-nitropenta-2,4-dienoic acid. 2,4-DNT-degrading strains also converted 2,6-DNT to 3-methyl-4-nitrocatechol but did not metabolize the 3-methyl-4-nitrocatechol. Although 2,6-DNT prevented the degradation of 2,4-DNT by 2,4-DNT-degrading strains, the effect was not the result of inhibition of 2,4-DNT dioxygenase by 2,6-DNT or of 4-methyl-5-nitrocatechol monooxygenase by 3-methyl-4-nitrocatechol.