Investigation of the Microbial Ecology of Intertidal Hot Springs by Using Diversity Analysis of 16S rRNA and Chitinase Genes

The microbial diversity of intertidal hot springs on the seashore of northwest Iceland was examined by combining directed in situ enrichments, artificial support colonization, and mat sampling. Analysis of 16S rRNA genes revealed the presence of clones related to both marine and terrestrial, thermophilic, mesophilic, and psychrophilic microorganisms scattered among 11 bacterial divisions. No archaea were found. The species composition of the enrichments was affected by the length of the hot periods experienced at low tide and was very different from those found in the biomass. A total of 36 chitinase genes were detected by molecular screening of the samples with degenerate primers for glycoside hydrolase family 18. The chitinase gene diversity was at least twofold higher in the enrichment samples than in the controls, indicating that a much higher diversity of hydrolytic genes can be accessed with this approach.     

Use of low nutrient enrichments to access novel amylase genes in silent diversity of thermophiles

By combining low nutrient enrichments and molecular methods, a high diversity of new amylase genes was detected in a neutral sulphide-rich hot spring in Iceland. Enrichments based on hot spring water and low concentrations of starch were used to select slow-growing, starch-degrading microorganisms. Six enrichments had in total 17 bacterial types detected by 16S rRNA analysis, mostly related to the Thermus-Deinococcus group, green non-sulphur bacteria, gram positives, and uncultivated new candidate divisions. No Archaea were found. The apparent 16S rRNA species composition of the enrichments was very different from that of the microbial mat in the same hot spring. DNA samples obtained from 4 enrichments and from hot spring biomass were screened by PCR for amylase genes in glycoside-hydrolase family 13. Degenerate primers, based on conserved amino acid sequences from multiplealignments of family 13, enabled the detection of 18 amylase sequence types in the enrichments, including -amylases, -glucosidases, 1,4--glucan branching enzymes, cyclomaltodextrin hydrolases, maltogenic amylases and neopullulanases, and unspecified family 13 glycoside-hydrolases. Only one unique neopullulanase sequence, also found in most of the enrichments, was detected in the hot spring biomass DNA. The results suggest that the enrichment method combined with sequence-based screening is an efficient way to access the silent, i.e. not detectable, gene diversity in natural environments.     

Chitinase gene sequences retrieved from diverse aquatic habitats reveal environment-specific distributions

Chitin is an abundant biopolymer whose degradation is mediated primarily by bacterial chitinases. We developed a degenerate PCR primer set to amplify a approximately 900-bp fragment of family 18, group I chitinase genes and used it to retrieve these gene fragments from environmental samples. Clone libraries of presumptive chitinase genes were created for nine water and six sediment samples from 10 aquatic environments including freshwater and saline lakes, estuarine water and sediments, and the central Arctic Ocean. Putative chitinase sequences were also retrieved from the Sargasso Sea metagenome sequence database. We were unable to obtain PCR product with these primers from an alkaline, hypersaline lake (Mono Lake, California). In total, 108 partial chitinase gene sequences were analyzed, with a minimum of 5 and a maximum of 13 chitinase sequences obtained from each library. All chitinase sequences were novel compared to previously identified sequences. Intralibrary sequence diversity was low, while we found significant differences between libraries from different water column samples and between water column and sediment samples. However, identical sequences were retrieved from samples collected at widely distributed locations that did not necessarily represent similar environments, suggesting homogeneity of chitinoclastic communities between some environments.     

Chitinase Gene Sequences Retrieved from Diverse Aquatic Habitats Reveal Environment-Specific Distributions

Chitin is an abundant biopolymer whose degradation is mediated primarily by bacterial chitinases. We developed a degenerate PCR primer set to amplify a ~900-bp fragment of family 18, group I chitinase genes and used it to retrieve these gene fragments from environmental samples. Clone libraries of presumptive chitinase genes were created for nine water and six sediment samples from 10 aquatic environments including freshwater and saline lakes, estuarine water and sediments, and the central Arctic Ocean. Putative chitinase sequences were also retrieved from the Sargasso Sea metagenome sequence database. We were unable to obtain PCR product with these primers from an alkaline, hypersaline lake (Mono Lake, California). In total, 108 partial chitinase gene sequences were analyzed, with a minimum of 5 and a maximum of 13 chitinase sequences obtained from each library. All chitinase sequences were novel compared to previously identified sequences. Intralibrary sequence diversity was low, while we found significant differences between libraries from different water column samples and between water column and sediment samples. However, identical sequences were retrieved from samples collected at widely distributed locations that did not necessarily represent similar environments, suggesting homogeneity of chitinoclastic communities between some environments.     

High-multiplicity of chitinase genes in Streptomyces coelicolor A3(2).

Six different genes for chitinase from ordered cosmids of the chromosome of Streptomyces coelicolor A3(2) were identified by hybridization, using the chitinase genes from other Streptomyces spp. as probes, and cloned. The genes were sequenced and analyzed. The genes, together with an additional chitinase gene obtained from the data bank, can be classified into either family 18 or family 19 of the glycosyl hydrolase classification. The five chitinases that fall into family 18 show diversity in their multiple domain structures as well as in the amino acid sequences of their catalytic domains. The remaining two chitinases are members of family 19 chitinases, since their C-terminus shares more than 70% identity with the catalytic domain of ChiC of Streptomyces griseus, the sole gene for family 19 chitinase so far found in an organism other than higher plants.     

Species Diversity of Uncultured and Cultured Populations of Soil and Marine Ammonia Oxidizing Bacteria

Although molecular techniques are considered to provide a more comprehensive view of species diversity of natural microbial populations, few studies have compared diversity assessed by molecular and cultivation-based approaches using the same samples. To achieve this, the diversity of natural populations of ammonia oxidising bacteria in arable soil and marine sediments was determined by analysis of 16S rDNA sequences from enrichment cultures, prepared using standard methods for this group, and from 16S rDNA cloned from DNA extracted directly from the same environmental samples. Soil and marine samples yielded 31 and 18 enrichment cultures, respectively, which were compared with 50 and 40 environmental clones. There was no evidence for selection for particular ammonia oxidizer clusters by different procedures employed for enrichment from soil samples, although no culture was obtained in medium at acid pH. In soil enrichment cultures, Nitrosospira cluster 3 sequences were most abundant, whereas clones were distributed more evenly between Nitrosospira clusters 2, 3, and 4. In marine samples, the majority of enrichment cultures contained Nitrosomonas, whereas Nitrosospira sequences were most abundant among environmental clones. Soil enrichments contained a higher proportion of identical sequences than clones, suggesting laboratory selection for particular strains, but the converse was found in marine samples. In addition, 16% of soil enrichment culture sequences were identical to those in environmental clones, but only 1 of 40 marine enrichments was found among clones, indicating poorer culturability of marine strains represented in the clone library, under the conditions employed. The study demonstrates significant differences in species composition assessed by molecular and culture-based approaches but indicates also that, employing only a limited range of cultivation conditions, 7% of the observed sequence diversity in clones of ammonia oxidizers from these environments could be obtained in laboratory enrichment culture. Further studies and experimental approaches are required to determine which approach provides better representation of the natural community.     

Soluble di-iron monooxygenase gene diversity in soils, sediments and ethene enrichments

Soluble di-iron monooxygenases (SDIMOs) are key enzymes in the bacterial oxidation of hydrocarbons, and have applications in environmental and industrial biotechnology. SDIMOs from pure cultures are unlikely to represent the total diversity of this enzyme family, so we used polymerase chain reaction to survey the diversity of SDIMO alpha subunit genes in environmental samples, ethene enrichments and ethene-degrading bacterial isolates. From 178 cloned amplicons, 98 restriction fragment length polymorphism types were seen, from which 75 representative SDIMO sequences were obtained; 45 from environmental samples, 25 from enrichments and seven from isolates. The sequences were diverse, including genes similar to ethene (etnC), propene (amoC, pmoC), propane (prmA) and butane (bmoX) monooxygenases, in addition to many novel sequences comprising a new SDIMO group (group 6). Environmental samples showed the highest diversity, with strong representation of group 6 SDIMOs and prmA-like genes. Ethene stimulation of samples resulted in increased frequencies of group 4 SDIMOs (etnC-like). Four ethene-utilizing Mycobacterium isolates (NBB1-NBB4) from enrichments all contained etnC; one isolate (NBB4) also contained three additional SDIMO genes (bmoX-like, amoC-like and group 6). The primers, database, clone libraries and strains reported here provide a resource for future bioremediation and biocatalysis studies, with particular relevance for chlorinated alkene and alkane compounds.     

Determination of a relationship between chitinase activity and microbial diversity in chitin amended compost

By using denaturing gradient gel electrophoresis (DGGE) and simultaneously measuring the enzymatic activity of chitinase, we could link genetic diversity of the indigenous microbial communities with chitinase activity in compost samples. A garden/park waste compost and a source separated organic household waste compost, showed different genetic diversity as measured by PCR-DGGE of total DNA extracted from the composts. The household waste compost had the highest chitinase activity. To increase chitinase activity, the two composts were amended with chitin. This addition induced a change in both the bacterial and fungal genetic diversity when compared to the non-amended compost samples. Likewise, both composts reacted to the addition of chitin with an increase in chitinase activity. Thus, a relationship between genetic diversity and chitinase activity was established for the composts in question. The N-mineralization in the household waste compost was apparently increased by the addition of chitin, while such an effect was not observed in the garden/park waste compost.     

温州市境内城市河流底泥氨氧化菌富集培养物微生物群落结构分析

【背景】城市河流底泥含有丰富的微生物资源,底泥表面更是硝化作用的主要位点之一,其表面微生物在河流生态系统氮的转化过程中发挥着重要作用。【目的】以温州市境内的城市河流水系温瑞塘河茶山段舜岙河和横江河的4条河道作为采样点,比较分析4种不同环境下城市河流表层底泥氨氧化菌富集培养物的微生物群落结构。【方法】通过野外采样及室内培养对底泥中氨氧化功能菌进行富集培养,采用高通量测序技术分析微生物群落的组成、丰度和多样性。【结果】富集培养后主要优势类群为变形菌门(Proteobacteria)和拟杆菌门(Bacteroidetes)。4个样品共涉及氨氧化细菌3个属,分别为亚硝化单胞菌属(Nitrosomonas)、亚硝化螺菌属(Nitrosospira)、亚硝化球菌属(Nitrosococcus),涉及氨氧化古菌1个属为Nitrososphaera,其中所有样品均以Nitrosomonas为主。不同底泥富集样品氨氧化微生物可操作分类单元(Operational taxonomic unit,OTU)组成存在明显差异,栽种有水生植物的河道底泥样品DA2具有最高的氨氧化细菌OTU数量和相对丰度,而存在生活餐饮污染的河道底泥样品DA4具有最高的氨氧化古菌OTU数量和相对丰度;相较于滞留水体,采自相对流动水体的富集样品DA2、DA4具有更高的氨氧化微生物OTU数量和相对丰度。【结论】阐述了4种不同环境下城市河流底泥氨氧化菌富集培养物微生物群落结构的多样性,确定了富集培养之后的优势类群,为氨氧化微生物培养源的选择提供了参考,也为城市河流底泥中氨氧化菌进一步的筛选分离及其生理生态特征的研究提供了科学依据。     

转几丁质酶和葡聚糖酶双价基因棉花对土壤细菌种群多样性的影响

以转几丁质酶和葡聚糖酶双价基因棉花为研究对象,非转基因受体棉花为对照,通过比较可培养细菌数量和基于16S rRNA克隆文库细菌种群分析,评价外源双价基因的导入在苗期、蕾期、花铃期和吐絮期对棉花根际细菌群落多样性的影响。结果表明,可培养细菌的数量不受外源双价基因的影响,随着棉花生育期的交替而变化,以代谢旺盛的花铃期最多。构建的转基因和非转基因不同生育期根际土壤细菌16S rRNA文库容量为2400个克隆,涵盖了细菌的283个属。其中,Acidobacterium是最大优势类群,共包括624个克隆,其次为未知细菌种群和Flavisolibacter。比较转基因和非转基因棉花根际土壤细菌的种群结构,结果显示,同一生育期内前者种群的多样性显著低于后者,二者的共有类群随着生长发育的进行而增多。研究结果说明几丁质酶基因和葡聚糖酶基因对棉花根际细菌种群多样性有着不同程度的削减作用,但是随着种植时间的延长,该差异呈现逐渐缩小的趋势。     

Distribution and phylogenetic analysis of family 19 chitinases in Actinobacteria

In organisms other than higher plants, family 19 chitinase was first discovered in Streptomyces griseus HUT6037, and later, the general occurrence of this enzyme in Streptomyces species was demonstrated. In the present study, the distribution of family 19 chitinases in the class Actinobacteria and the phylogenetic relationship of Actinobacteria family 19 chitinases with family 19 chitinases of other organisms were investigated. Forty-nine strains were chosen to cover almost all the suborders of the class Actinobacteria, and chitinase production was examined. Of the 49 strains, 22 formed cleared zones on agar plates containing colloidal chitin and thus appeared to produce chitinases. These 22 chitinase-positive strains were subjected to Southern hybridization analysis by using a labeled DNA fragment corresponding to the catalytic domain of ChiC, and the presence of genes similar to chiC of S. griseus HUT6037 in at least 13 strains was suggested by the results. PCR amplification and sequencing of the DNA fragments corresponding to the major part of the catalytic domains of the family 19 chitinase genes confirmed the presence of family 19 chitinase genes in these 13 strains. The strains possessing family 19 chitinase genes belong to 6 of the 10 suborders in the order Actinomycetales, which account for the greatest part of the Actinobacteria: Phylogenetic analysis suggested that there is a close evolutionary relationship between family 19 chitinases found in Actinobacteria and plant class IV chitinases. The general occurrence of family 19 chitinase genes in Streptomycineae and the high sequence similarity among the genes found in Actinobacteria suggest that the family 19 chitinase gene was first acquired by an ancestor of the Streptomycineae and spread among the Actinobacteria through horizontal gene transfer.     

Chitinase genes revealed and compared in bacterial isolates, DNA extracts and a metagenomic library from a phytopathogen-suppressive soil

Soil that is suppressive to disease caused by fungal pathogens is an interesting source to target for novel chitinases that might be contributing towards disease suppression. In this study, we screened for chitinase genes, in a phytopathogen-suppressive soil in three ways: (1) from a metagenomic library constructed from microbial cells extracted from soil, (2) from directly extracted DNA and (3) from bacterial isolates with antifungal and chitinase activities. Terminal restriction fragment length polymorphism (T-RFLP) of chitinase genes revealed differences in amplified chitinase genes from the metagenomic library and the directly extracted DNA, but approximately 40% of the identified chitinase terminal restriction fragments (TRFs) were found in both sources. All of the chitinase TRFs from the isolates were matched to TRFs in the directly extracted DNA and the metagenomic library. The most abundant chitinase TRF in the soil DNA and the metagenomic library corresponded to the TRF¹⁰³ of the isolate Streptomyces mutomycini and/or Streptomyces clavifer . There were good matches between T-RFLP profiles of chitinase gene fragments obtained from different sources of DNA. However, there were also differences in both the chitinase and the 16S rRNA gene T-RFLP patterns depending on the source of DNA, emphasizing the lack of complete coverage of the gene diversity by any of the approaches used.     

Molecular detection of bacterial and streptomycete chitinases in the environment

Sets of PCR primers were designed to amplify bacterial chitinases at different levels of specificity. The bacterial chitinase group primers were successful in targeting enzymes classified within the group A glycosyl hydrolases of family 18. The widespread occurrence of group A bacterial chitinases in actinomycetes was demonstrated. Streptomycete chitinase specific primers were designed and a collection of type strains of species changed in the genes Streptomyces were screened and shown to have at least one and usually multiple chitinase genes. The presence of the gene for the chitin binding protein was also demonstrated within the streptomycete type strains. These data indicate that streptomycetes are well equipped to degrade chitin. The detection of group A chitinases in total community DNA is described and a sandy soil shown to contain more than 10 different genes using DGGE to indicate genetic diversity.     

Pronounced seasonal dynamics of freshwater chitinase genes and chitin processing

Seasonal variation in activity of enzymes involved in polymer degradation, including chitinases, has been observed previously in freshwater environments. However, it is not known whether the seasonal dynamics are due to shifts in the activity of bacteria already present, or shifts in community structure towards emergence or disappearance of chitinolytic organisms. We traced seasonal shifts in the chitinase gene assemblage in a temperate lake and linked these communities to variation in chitinase activity. Chitinase genes from 20 samples collected over a full yearly cycle were characterized by pyrosequencing. Pronounced temporal shifts in composition of the chitinase gene pool (beta diversity) occurred along with distinct shifts in richness (alpha diversity) as well as chitin processing. Changes in the chitinase gene pool correlated mainly with temperature, abundance of crustacean zooplankton and phytoplankton blooms. Also changes in the physical structure of the lake, e.g. stratification and mixing were associated with changes in the chitinolytic community, while differences were minor between surface and suboxic hypolimnetic water. The lake characteristics influencing the chitinolytic community are all linked to changes in organic particles and we suggest that seasonal changes in particle quality and availability foster microbial communities adapted to efficiently degrade them.     

Distribution and evolution of chitinase genes in Streptomyces species: involvement of gene-duplication and domain-deletion

Streptomyces coelicolor A3(2) possesses nine genes for family 18 chitinases and two for family 19, showing high multiplicity. By hybridization analyses, distribution of those chitinase genes was investigated in six other Streptomyces species covering the whole phylogenetic range based on 16S rDNA sequences. All strains showed high-multiplicity of chitinase genes, like S. coelicolor A3(2). The phylogeny and gene organization of the family 18 chitinase genes cloned from Streptomyces species so far were then analyzed to investigate the gene evolution. It was concluded that Streptomyces already possessed a variety of chitinase genes prior to branching into many species, and that the ancestral genes of chiA and chiB have been generated by gene-duplication. In the course of the analyses, evidence that the chi30 and chi40 genes of S. thermoviolaceus were derived from their corresponding original chitinase genes by losing gene parts for substrate-binding domains and fibronectin type III-like domains was obtained. It was thus shown that gene-duplication and domain-deletion were implicated in generating the high diversity and multiplicity of chitinase genes in Streptomyces species. This revised version was published online in June 2006 with corrections to the Cover Date.     

Cultivated anaerobic acidophilic/acidotolerant thermophiles from terrestrial and deep-sea hydrothermal habitats

Metabolic and phylogenetic diversity of cultivated anaerobic microorganisms from acidic continental hot springs and deep-sea hydrothermal vents was studied by molecular and microbiological methods. Anaerobic organotrophic enrichment cultures growing at pH 3.5–4.0 and 60 or 85°C with organic energy sources were obtained from samples of acidic hot springs of Kamchatka Peninsula (Pauzhetka, Moutnovski Volcano, Uzon Caldera) and Kunashir Island (South Kurils) as well as from the samples of chimneys of East Pacific Rise (13°N). The analyses of clone libraries obtained from terrestrial enrichment cultures growing at 60°C revealed the presence of archaea of genus Thermoplasma and bacteria of genus Thermoanaerobacter. Bacterial isolates from these enrichments were shown to belong to genera Thermoanaerobacter and Thermoanaerobacterium, being acidotolerant with the pH optimum for growth at 5.5–6.0 and the pH minimum at 3.0. At 85°C, domination of thermoacidophilic archaea of genus Acidilobus in terrestrial enrichments was found by both molecular and microbiological methods. Five isolates belonging to this genus possessed some phenotypic features that were new for this genus, such as flagellation or the ability to grow on monosaccharides or disaccharides. Analyses of clone libraries from the deep-sea thermoacidophilic enrichment cultures showed that the representatives of the genus Thermococcus were present at both 60 and 85°C. From the 60°C deep-sea enrichment, a strain belonging to Thermoanaerobacter siderophilus was isolated. It grew optimally at pH 6.0 with the minimum pH for growth at 3.0 and with salinity optimum at 0–2.5% NaCl and the maximum at 7%, thus differing significantly from the type strain. These data show that fermentative degradation of organic matter may occur at low pH and wide temperature range in both terrestrial and deep-sea habitats and can be performed by acidophilic or acidotolerant thermophilic prokaryotes.     

Selected chitinase genes in cultured and uncultured marine bacteria in the alpha- and gamma-subclasses of the proteobacteria

PCR primers were patterned after chitinase genes in four gamma-proteobacteria in the families Alteromonadaceae and Enterobacteriaceae (group I chitinases) and used to explore the occurrence and diversity of these chitinase genes in cultured and uncultured marine bacteria. The PCR results from 104 bacterial strains indicated that this type of chitinase gene occurs in two major groups of marine bacteria, alpha- and gamma-proteobacteria, but not the Cytophaga-Flavobacter group. Group I chitinase genes also occur in some viruses infecting arthropods. Phylogenetic analysis indicated that similar group I chitinase genes occur in taxonomically related bacteria. However, the overall phylogeny of chitinase genes did not correspond to the phylogeny of 16S rRNA genes, possibly due to lateral transfer of chitinase genes between groups of bacteria, but other mechanisms, such as gene duplication, cannot be ruled out. Clone libraries of chitinase gene fragments amplified from coastal Pacific Ocean and estuarine Delaware Bay bacterioplankton revealed similarities and differences between cultured and uncultured bacteria. We had hypothesized that cultured and uncultured chitin-degrading bacteria would be very different, but in fact, clones having nucleotide sequences identical to those of chitinase genes of cultured alpha-proteobacteria dominated both libraries. The other clones were similar but not identical to genes in cultured gamma-proteobacteria, including vibrios and alteromonads. Our results suggest that a closer examination of chitin degradation by alpha-proteobacteria will lead to a better understanding of chitin degradation in the ocean.     

The diversity of the pathogenic Oomycete (Aphanomyces astaci) chitinase genes within the genotypes indicate adaptation to its hosts

The aim of this work was to evaluate the genetic diversity of the crayfish plague pathogen Aphanomyces astaci (Oomycete) among different isolates and genotypes. Partial chitinase genes were cloned and sequenced from 28 A. astaci isolates including four of the five previously identified RAPD (random amplification of polymorphic DNA)-genotypes. The cloned chitinase sequences (n=176) formed three main groups, CHI1, CHI2 and CHI3, with the CHI2 group then further divided into three subgroups, CHI2A, CHI2B and CHI2C. Some of these chitinases were specific for certain genotypes of A. astaci, as CHI2B and CHI2C were only found from the As-genotype and CHI3 from the Ps-genotypes of A. astaci. Highest diversity rate was observed in the CHI2 group, while the CHI3 group specific for Ps-genotypes was highly homologous. Based on our chitinase data, As- and Pc-genotypes seem to be related, while the two Ps-genotypes were identical to each other, but considerably different from the genotypes As and Pc. These are the first genotype specific differences that are located in the coding region of the chitinase gene of A. astaci and the differences observed here also enable the genotyping of A. astaci. The diversity observed here can also reflect differences in the epidemiological properties of the different genotypes.     

Diversity in methane enrichments from agricultural soil revealed by DGGE separation of PCR amplified 16S rDNA fragments

Denaturing gradient gel electrophoresis (DGGE) profiles of PCR amplified V3 regions of 16S rRNA genes were used to assess the diversity in enrichment cultures with methane as the only carbon and energy source. The enrichments originated from two agricultural soils. One was a sandy soil with low (10%) organic content, the other an organic soil with approximately 50% organic content. DGGE provided a fast evaluation of the distribution of amplifiable sequence types indicating that specific bacterial populations had been enriched from each soil. The DGGE profiles revealed a broader range of amplified V3 fragments in the community derived from organic soil than from sandy soil. Fragments from 19 individual DGGE bands were sequenced and compared with 27 previously published 16S rRNA gene sequences. The sequences confirmed the high diversity with the presence of different methylotrophic populations in each enrichment. No affiliation was found with type I methanotrophs, instead type II methanotroph sequences were found in the enrichments from both soil types. Some of the fragments from the organic soil enrichment were not affiliated with methylotrophs. Most of the sequences clustered distantly on a branch within the α-Proteobacteria. These facts suggested that previously undescribed methylotrophs are abundant in methane enrichments from agricultural soil.