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1.
Nitrifying biofilters are used in aquaria and aquaculture systems to prevent accumulation of ammonia by promoting rapid conversion to nitrate via nitrite. Ammonia-oxidizing archaea (AOA), as opposed to ammonia-oxidizing bacteria (AOB), were recently identified as the dominant ammonia oxidizers in most freshwater aquaria. This study investigated biofilms from fixed-bed aquarium biofilters to assess the temporal and spatial dynamics of AOA and AOB abundance and diversity. Over a period of four months, ammonia-oxidizing microorganisms from six freshwater and one marine aquarium were investigated at 4–5 time points. Nitrogen balances for three freshwater aquaria showed that active nitrification by aquarium biofilters accounted for ≥81–86% of total nitrogen conversion in the aquaria. Quantitative PCR (qPCR) for bacterial and thaumarchaeal ammonia monooxygenase (amoA) genes demonstrated that AOA were numerically dominant over AOB in all six freshwater aquaria tested, and contributed all detectable amoA genes in three aquarium biofilters. In the marine aquarium, however, AOB outnumbered AOA by three to five orders of magnitude based on amoA gene abundances. A comparison of AOA abundance in three carrier materials (fine sponge, rough sponge and sintered glass or ceramic rings) of two three-media freshwater biofilters revealed preferential growth of AOA on fine sponge. Denaturing gel gradient electrophoresis (DGGE) of thaumarchaeal 16S rRNA genes indicated that community composition within a given biofilter was stable across media types. In addition, DGGE of all aquarium biofilters revealed low AOA diversity, with few bands, which were stable over time. Nonmetric multidimensional scaling (NMDS) based on denaturing gradient gel electrophoresis (DGGE) fingerprints of thaumarchaeal 16S rRNA genes placed freshwater and marine aquaria communities in separate clusters. These results indicate that AOA are the dominant ammonia-oxidizing microorganisms in freshwater aquarium biofilters, and that AOA community composition within a given aquarium is stable over time and across biofilter support material types.  相似文献   

2.
Ammonia-oxidizing bacteria (AOB) and ammonia-oxidizing archaea (AOA) play important roles in nitrification in various environments. They may also be key communities for ammonia oxidation in composting systems, although few studies have discussed their presence. We investigated the relative diversity and abundance of AOB and AOA using cloning procedures, denaturing gradient gel electrophoresis analysis, and real-time PCR during several stages in the process of cattle manure composting. Our results revealed that the AOB community structure changed during the process. At the high-temperature stage (>60°C), a member of the Nitrosomonas europaea/eutropha cluster dominated while the uncultured Nitrosomonas spp. cluster appeared after the temperature decreased. Additionally, our analysis indicated that AOA sequences, which were classified into a soil/sediment cluster, were present after the temperature decreased during the composting process. At these stages, the number of the archaeal amoA gene copies (3.2 or 3.9?×?107 copies per gram freeze-dried compost) was significantly higher than that of bacterial amoA gene copies (2.2–7.2?×?106 copies per gram freeze-dried compost). Our results suggest that both AOB and AOA are actively involved in nitrification of composting systems.  相似文献   

3.
The ammonia-oxidizing prokaryote (AOP) community in three groundwater treatment plants and connected distribution systems was analyzed by quantitative real-time PCR and sequence analysis targeting the amoA gene of ammonia-oxidizing bacteria (AOB) and archaea (AOA). Results demonstrated that AOB and AOA numbers increased during biological filtration of ammonia-rich anoxic groundwater, and AOP were responsible for ammonium removal during treatment. In one of the treatment trains at plant C, ammonia removal correlated significantly with AOA numbers but not with AOB numbers. Thus, AOA were responsible for ammonia removal in water treatment at one of the studied plants. Furthermore, an observed negative correlation between the dissolved organic carbon (DOC) concentration in the water and AOA numbers suggests that high DOC levels might reduce growth of AOA. AOP entered the distribution system in numbers ranging from 1.5 × 103 to 6.5 × 104 AOPs ml−1. These numbers did not change during transport in the distribution system despite the absence of a disinfectant residual. Thus, inactive AOP biomass does not seem to be degraded by heterotrophic microorganisms in the distribution system. We conclude from our results that AOA can be commonly present in distribution systems and groundwater treatment, where they can be responsible for the removal of ammonia.Ammonia can be present in source water used for drinking water production or added to treated water with chlorine to form chloramines as a disinfectant. However, the presence of ammonia in drinking water is undesirable because nitrification might lead to toxic levels of nitrite (29) or adverse effects on water taste and odor (4) and might increase heterotrophic bacteria, including opportunistic pathogens (29). Two-thirds of the drinking water in The Netherlands is produced from groundwater. Most of the groundwater used for drinking water production is anoxic with relatively high concentrations of methane, iron, manganese, dissolved organic carbon (DOC), and ammonia. Treatment of anoxic groundwater aims at achieving biologically stable water, because drinking water in The Netherlands is distributed without a disinfectant residual. As a result, a highly efficient nitrification process during rapid medium filtration is required.Nitrification is the microbial oxidation of ammonia to nitrate and consists of two processes: the oxidation of ammonia to nitrite by ammonia-oxidizing prokaryotes (AOP) and the oxidation of nitrite to nitrate by nitrite-oxidizing bacteria (NOB). Recently it was shown that in addition to bacteria, archaea also are capable of ammonia oxidation (13). Since then, ammonia-oxidizing archaea (AOA) have been found in many different ecosystems, including wastewater treatment systems (10, 20, 24). However, it is currently unknown if AOA are present in drinking water treatment processes and distribution systems. Recent studies have focused on nitrification in drinking water treatment (16, 28). In those studies, AOB and NOB were enumerated by traditional most-probable-number (MPN) methods using selective liquid media. However, MPN methods are time-consuming and underestimate the numbers of AOP and NOB (3). Quantitative real-time PCR has been used to quantify AOB in drinking water (12) and might be a useful tool for quantifying AOB and AOA in drinking water.In our study, a real-time PCR method targeting the amoA gene of AOB or AOA was developed to quantify numbers of AOP in drinking water. This real-time PCR method was used together with a phylogenetic analysis of the amoA gene of AOB and AOA to do the following: (i) determine the treatment steps where AOP dominates in the groundwater treatment train of three drinking water production plants in The Netherlands, (ii) quantify the AOP entering the distribution system and determine the fate of AOP during transport in the distribution system, and (iii) elucidate the role of AOA in nitrification during drinking water treatment and in distribution systems.  相似文献   

4.
Ammonia-oxidizing archaea (AOA) and bacteria (AOB) in three types of paddy soils of China before and after rice plantation were investigated by using an integrated approach including geochemistry, 454 pyrosequencing, and quantitative polymerase chain reaction (PCR). The abundances of AOA amoA gene were 1~2 orders of magnitude higher than AOB amoA gene. The types of paddy soils had important impacts on the diversities of both AOA and AOB via clay mineralogy (smectite or illite-rich) and bioavailability of ammonium. The Nitrososphaera subcluster 5 and Nitrosopumilis cluster of AOA, and Nitrosomonas subcluster 5 and Nitrosospira subcluster 3 of AOB were well adapted to soils with high ammonium concentrations. AOA and AOB community structures were different before and after rice plantation, likely due to changes of pH and ammonium fertilization. The Nitrosospira subclusters 2 and 9 were well adapted to acidic paddy soils. However, the sensitivity of AOA and AOB community structures to these factors may be complicated by other geochemical conditions. The results of this study collectively demonstrated that multiple environmental factors, such as clay mineralogy, ammonium content and total organic carbon as well as soil pH, shaped AOA and AOB community structure and abundance.  相似文献   

5.
The cold springs underlain by gas hydrates on the Qinghai-Tibet Plateau (QTP) are similar to deep-sea cold seeps with respect to methane biogeochemistry. Previous studies have shown that ammonia oxidizing bacteria (AOB) and archaea (AOA) are actively present and play important roles in the carbon/nitrogen cycles in cold seeps. Studying AOA and AOB communities in the QTP cold springs will be of great importance to our understanding of carbon and nitrogen cycling dynamics related to the underlying gas hydrates on the QTP. Thus, the abundance and diversity of AOB and AOA in sediments of four cold springs underlain by gas hydrates on the QTP were determined by using quantitative polymerase chain reaction and amoA gene (encoding ammonia monooxygenase involved in ammonia oxidation) phylogenetic analysis. The results showed that the AOB and AOA amoA gene abundances were at 103–104 copies per gram of the sediments in the investigated cold springs. The AOB population consisted of Nitrosospira and Nitrosomonas in contrast with the mere presence of Nitrosospira in marine cold seeps. The AOB diversity was higher in cold springs than in cold seeps. The AOA population was mainly composed of Nitrososphaera, in contrast with the dominance of Nitrosopumilus in cold seeps. The terrestrial origin and high level of dissolved oxygen of the cold springs may be the main factors accounting for the observed differences in AOB and AOA populations between the QTP cold springs and marine cold seeps.  相似文献   

6.
Phylogenetic Diversity of Archaea and Bacteria in a Deep Subsurface Paleosol   总被引:10,自引:0,他引:10  
Abstract A low-biomass paleosol 188 m below the ground surface at the Department of Energy's Hanford Site in south-central Washington State was recovered and maintained at the in situ temperature (17°C) as an intact core or homogenized sediment for 0, 1, 3, 10, and 21 weeks post-sampling. Bacterial and archaeal 16S rRNA genes were amplified by PCR and cloned. Of 746 bacterial and 190 archaeal clones that were categorized by restriction fragment length polymorphism (RFLP), 242 bacterial and 16 archaeal clones were partially sequenced and compared against the small subunit ribosomal RNA database (RDP) and GenBank. Six bacterial and 16 archaeal clones sequences, with little similarity to those in public databases, were sequenced in their entirety, and subjected to more detained phylogenetic analysis. The most frequently occurring clones types were related to Pseudomonas, Bacillus, Micrococcus, Clavibacter, Nocardioides, Burkholderia, Comamonas, and Erythromicrobium. Clone sequences whose RDP similarity value was ≥0.6 consistently grouped with their nearest RDP neighbor during phylogenetic analysis. Six truly novel eubacterial sequences were identified; they consistently cluster with or near the Chloroflexaceae and sequences recovered from the Sargasso Sea. Sixteen unique archaeal RFLP groups were identified from 190 randomly-sampled clones. The novel archaeal rDNA clones formed a coherent clade along the major Crenarchaea branch containing all previously described mesophilic crenarchae clones, but remained firmly associated with 16S rDNA clones previously obtained from a thermal Fe/S spring in Yellowstone National Park. The wealth of group-specific genetic information identified during this study will now allow us to address specific hypotheses related to in situ stimulation of these deep subsurface microorganisms and changes in microbial community composition resulting from subsurface contamination or remediation processes at the Hanford Site. Revised: 21 October 1997; Accepted: 20 November 1997  相似文献   

7.
8.
Nitrification, the aerobic oxidation of ammonia to nitrate via nitrite, has been suggested to have been a central part of the global biogeochemical nitrogen cycle since the oxygenation of Earth. The cultivation of several ammonia-oxidizing archaea (AOA) as well as the discovery that archaeal ammonia monooxygenase (amo)-like gene sequences are nearly ubiquitously distributed in the environment and outnumber their bacterial counterparts in many habitats fundamentally revised our understanding of nitrification. Surprising insights into the physiological distinctiveness of AOA are mirrored by the recognition of the phylogenetic uniqueness of these microbes, which fall within a novel archaeal phylum now known as Thaumarchaeota. The relative importance of AOA in nitrification, compared to ammonia-oxidizing bacteria (AOB), is still under debate. This minireview provides a synopsis of our current knowledge of the diversity and physiology of AOA, the factors controlling their ecology, and their role in carbon cycling as well as their potential involvement in the production of the greenhouse gas nitrous oxide. It emphasizes the importance of activity-based analyses in AOA studies and formulates priorities for future research.  相似文献   

9.
In order to characterize the vertical variation of abundance and community composition of ammonia-oxidizing archaea (AOA) and ammonia-oxidizing bacteria (AOB) in sediments of a eutrophic lake, Lake Taihu, molecular techniques including real-time PCR, clone library, and sequencing were carried out in this study. Abundances of archaeal amoA gene (ranged from 2.34 × 106 to 4.43 × 107 copies [g dry sediment]?1) were higher than those of bacterial amoA gene (ranged from 5.02 × 104 to 6.91 × 106 copies [g dry sediment]?1) for all samples and both of them exhibited negative correlations with the increased depths. Diversities of archaeal and bacterial amoA gene increased with the elevated depths. There were no significant variations of AOB community structures derived from different sediment depths, whereas obvious differences were observed for the AOA community compositions. The information acquired in this study would be useful to elucidate the roles of AOA and AOB in the nitrogen cycling of freshwater ecosystems.  相似文献   

10.
The link between similarity in amino acid sequence for ammonia monooxygenase (AMO) and isotopic discrimination for ammonia oxidation ( l AMO ) was investigated in g -subdivision ammonia-oxidizing bacteria. The isotope effects for ammonia oxidation in pure cultures of the nitrifying strains Nitrosomonas marina , Nitrosomonas C-113a, Nitrosospira tenuis , Nitrosomonas europaea , and Nitrosomonas eutropha ranged from 14.2 to 38.2. The differences in isotope effects could not be readily explained by differential rates of ammonia oxidation, transport of NH 4 + , or accumulation of NH 2 OH or N 2 O among the strains. The major similarities and differences observed in l AMO are, however, paralleled by similarities and differences in amino acid sequences for the f -subunit of AMO (AmoA). Robust differences in l AMO among nitrifying bacteria may be expected to influence the stable isotopic signatures of nitrous oxide (N 2 O) produced in various environments.  相似文献   

11.
The response of soil ammonia-oxidizing bacterial (AOB) and archaeal (AOA) communities to individual environmental variables (e.g., pH, temperature, and carbon- and nitrogen-related soil nutrients) has been extensively studied, but how these environmental conditions collectively shape AOB and AOA distributions in unmanaged agricultural soils across a large latitudinal gradient remains poorly known. In this study, the AOB and AOA community structure and diversity in 26 agricultural soils collected from eastern China were investigated by using quantitative PCR and bar-coded 454 pyrosequencing of the amoA gene that encodes the alpha subunit of ammonia monooxygenase. The sampling locations span over a 17° latitude gradient and cover a range of climatic conditions. The Nitrosospira and Nitrososphaera were the dominant clusters of AOB and AOA, respectively; but the subcluster-level composition of Nitrosospira-related AOB and Nitrososphaera-related AOA varied across the latitudinal gradient. Variance partitioning analysis showed that geography and climatic conditions (e.g., mean annual temperature and precipitation), as well as carbon-/nitrogen-related soil nutrients, contributed more to the AOB and AOA community variations (∼50% in total) than soil pH (∼10% in total). These results are important in furthering our understanding of environmental conditions influencing AOB and AOA community structure across a range of environmental gradients.  相似文献   

12.
Diversity in Chemotaxis Mechanisms among the Bacteria and Archaea   总被引:15,自引:1,他引:14       下载免费PDF全文
The study of chemotaxis describes the cellular processes that control the movement of organisms toward favorable environments. In bacteria and archaea, motility is controlled by a two-component system involving a histidine kinase that senses the environment and a response regulator, a very common type of signal transduction in prokaryotes. Most insights into the processes involved have come from studies of Escherichia coli over the last three decades. However, in the last 10 years, with the sequencing of many prokaryotic genomes, it has become clear that E. coli represents a streamlined example of bacterial chemotaxis. While general features of excitation remain conserved among bacteria and archaea, specific features, such as adaptational processes and hydrolysis of the intracellular signal CheY-P, are quite diverse. The Bacillus subtilis chemotaxis system is considerably more complex and appears to be similar to the one that existed when the bacteria and archaea separated during evolution, so that understanding this mechanism should provide insight into the variety of mechanisms used today by the broad sweep of chemotactic bacteria and archaea. However, processes even beyond those used in E. coli and B. subtilis have been discovered in other organisms. This review emphasizes those used by B. subtilis and these other organisms but also gives an account of the mechanism in E. coli.  相似文献   

13.
Diversity and abundance of ammonia-oxidizing archaea (AOA) and bacteria (AOB) in samples of the northern South China Sea subsurface sediment were assessed by analyzing the amoA gene sequences retrieved from the samples. The microbial diversity was assessed using rarefaction and phylogenetic analyses. The deep-sea subsurface sediments harbored diverse and distinct AOA and AOB communities, but the abundance of AOA was lower than that of AOB, consistent with many other studies about bacteria and archaea in subsurface sediments. Diversity of AOA shown in the OTUs and Shannon index was correlated with the concentration of nitrite in the Pearson analysis, but no obvious relationships between the diversity or abundance of AOB and the physicochemical parameters could be identified in the present study, indicating the concentration of ammonium may not be an important factor to determine the diversity and abundance of ammonia-oxidizing prokaryotes in the subsurface sediments. Additionally, Nitrosomonas-like AOB was found to be dominant in subsurface sediments of the northern South China Sea showing a different adaption strategy comparing with some Nitrosospira-like AOB lineages. Concentration of nitrite was correlated with diversity of AOA, but no correlations between diversity and abundance of AOB and the physicochemical parameters were established in the study. Supplementary materials are available for this article. Go to the publisher's online edition of Geomicrobiology Journal to view the free supplemental files.  相似文献   

14.
To quantify the spatial distribution of ammonia-oxidizing bacteria (AOB) and archaea (AOA) and to determine nitrification activity in soil aggregates along a landscape, soil samples were collected from three landscape positions (shoulder, backslope, and toeslope) at two pasture sites with contrasting climatic conditions. The abundance of AOB and AOA was estimated by quantifying their respective bacterial and archaeal amoA gene copies using real-time polymerase chain reaction. Soil organic C (SOC), total N (TN), and the potential nitrification rate (PNR) were measured in aggregate size ranges (4–1, 1–0.25, and 0.25–0.05 mm). At site 1, a decreasing trend in PNR was observed as the size of aggregates decreased. Both bacterial and archaeal amoA genes were higher in the macroaggregates (4–1 and 1–0.25 mm) than in the microaggregates (0.25–0.05 mm) along the landscape. At site 2, PNR was higher in the smallest size of aggregates. In the 0.25–0.05-mm fraction, the abundance of bacterial and archaeal amoA genes was equal to, or greater than, those found in larger aggregate sizes. The relative abundance of archaeal amoA gene and the PNR correlated with relative SOC and TN contents along the landscapes. The positive relationship between relative archaeal amoA gene abundance and PNR suggests that nitrification in the studied pastures is probably driven by ammonia-oxidizing Thaumarchaeota.  相似文献   

15.
Investigation of the diversity of nirK and nirS in denitrifying bacteria revealed that salinity decreased the diversity in a nitrate-containing saline wastewater treatment system. The predominant nirS clone was related to nirS derived from marine bacteria, and the predominant nirK clone was related to nirK of the genus Alcaligenes.  相似文献   

16.
Autotrophic ammonia-oxidizing communities, which are responsible for the rate-limiting step of nitrification in most soils, have not been studied extensively in semiarid ecosystems. Abundances of soil archaeal and bacterial amoA were measured with real-time polymerase chain reaction along an elevation gradient in northern Arizona. Archaeal amoA was the predominant form of amoA at all sites; however, ratios of archaeal to bacterial amoA ranged from 17 to more than 1,600. Although size of ammonia-oxidizing bacteria populations was correlated with precipitation, temperature, percent sand, and soil C/N, there were no significant relationships between ammonia-oxidizing archaea populations and any of the environmental parameters evaluated in this study. Our results suggest that in these soils, archaea may be the primary ammonia oxidizers, and that ammonia-oxidizing archaea and ammonia-oxidizing bacteria occupy different niches.  相似文献   

17.
The role of ammonia-oxidizing archaea (AOA) in nitrogen cycling in marine sediments remains poorly characterized. In this study, we enriched and characterized AOA from marine sediments. Group I.1a crenarchaea closely related to those identified in marine sediments and “Candidatus Nitrosopumilus maritimus” (99.1 and 94.9% 16S rRNA and amoA gene sequence identities to the latter, respectively) were substantially enriched by coculture with sulfur-oxidizing bacteria (SOB). The selective enrichment of AOA over ammonia-oxidizing bacteria (AOB) is likely due to the reduced oxygen levels caused by the rapid initial growth of SOB. After biweekly transfers for ca. 20 months, archaeal cells became the dominant prokaryotes (>80%), based on quantitative PCR and fluorescence in situ hybridization analysis. The increase of archaeal 16S rRNA gene copy numbers was coincident with the amount of ammonia oxidized, and expression of the archaeal amoA gene was observed during ammonia oxidation. Bacterial amoA genes were not detected in the enrichment culture. The affinities of these AOA to oxygen and ammonia were substantially higher than those of AOB. [13C]bicarbonate incorporation and the presence and activation of genes of the 3-hydroxypropionate/4-hydroxybutyrate cycle indicated autotrophy during ammonia oxidation. In the enrichment culture, ammonium was oxidized to nitrite by the AOA and subsequently to nitrate by Nitrospina-like bacteria. Our experiments suggest that AOA may be important nitrifiers in low-oxygen environments, such as oxygen-minimum zones and marine sediments.Archaea have long been known as extremophiles, since most cultivated archaeal strains were cultivated from extreme environments, such as acidic, hot, and high-salt environments. The view of archaea as extremophiles (i.e., acidophiles, thermophiles, and halophiles) has radically changed by the application of molecular technologies, including PCR in environmental microbiology. Using Archaea-specific PCR primers, novel archaeal 16S rRNA gene sequences were discovered in seawater (23, 27). Following these discoveries, an ever-increasing and unexpectedly high variety of archaeal 16S rRNA gene sequences has been reported from diverse “nonextreme” environments (67). This indicates that archaea are, like bacteria, ubiquitous in the biosphere rather than exclusively inhabiting specific extreme niches. Archaea are abundant in water columns of some oceanic provinces (33, 36) and deep-subsea floor sediments (11, 12, 48). Despite the increasing number of reports of the diversity and abundance of these nonextreme archaea by molecular ecological studies, their physiology and ecological roles have remained enigmatic.Oxidation of ammonia, a trait long thought to be exclusive to the domain Bacteria (13), was recently suggested to be a trait of archaea of the crenarchaeal groups I.1a and I.1b, based on a metagenome analysis (79) and supported by the discovery of archaeal amoA-like genes in environmental shotgun sequencing studies of Sargasso Sea water (80) and genomic analysis of “Candidatus Cenarchaeum symbiosum,” a symbiont of a marine sponge (30). Molecular ecological studies indicated that these ammonia-oxidizing archaea (AOA) are often predominant over ammonia-oxidizing bacteria (AOB) in ocean waters (9, 53, 87), soils (17, 47), and marine sediments (61). Critical evidence for autotrophic archaeal ammonia oxidation was obtained by the characterization of the first cultivated mesophilic crenarchaeon (group I.1a), “Candidatus Nitrosopumilus maritimus SCM1,” from an aquarium (38), and a related archaeon from North Sea water (87) and subsequently by enrichment of thermophilic AOA (22, 31). Whole-genome-based phylogenetic studies recently indicated that the nonthermophilic crenarchaea, including the AOA, likely form a phylum separate from the Crenarchaeota and Euryarchaeota phyla (15, 16, 72). This proposed new phylum was called Thaumarchaeota (15).Microorganisms in marine sediments contribute significantly to global biogeochemical cycles because of their abundance (85). Nitrification is essential to the nitrogen cycle in marine sediments and may be metabolically coupled with denitrification and anaerobic ammonium oxidation, resulting in the removal of nitrogen as molecular nitrogen and the generation of greenhouse gases, such as nitrous oxide (19, 75). Compared with studies on archaeal nitrification in the marine water column, only limited information on archaeal nitrification in marine sediments is available so far. Archaeal amoA genes have been retrieved from marine and coastal sediments (8, 26, 61), and the potentially important role of AOA in nitrification has been suggested based on the abundance of archaeal amoA genes relative to that of bacterial amoA genes in surface marine sediments from Donghae (South Korea) (61). Cultivation of AOA, although difficult (38), remains essential to estimating the metabolic potential of archaea in environments such as soils (47) and marine sediments (61). Here, we report the successful enrichment of AOA of crenarchaeal group I.1a from marine sediments by employing a coculture with sulfur-oxidizing bacteria (SOB) which was maintained for ca. 20 months with biweekly transfers. In this way, we were able to characterize AOA from marine sediments, providing a clue for the role of AOA in the nitrogen cycle of marine sediments.  相似文献   

18.
The abundance and diversity of archaeal ammonia monooxygenase subunit A (amoA) genes from hydrothermal vent chimneys at the Juan de Fuca Ridge were investigated. The majority of the retrieved archaeal amoA sequences exhibited identities of less than 95% to those in the GenBank database. Novel ammonia-oxidizing archaea may exist in the hydrothermal vent environments.Ammonia-oxidizing archaea (AOA) may play important roles in carbon and nitrogen cycles in various temperate environments (5, 7, 10, 12, 16). The frequent detection (23, 24) and successful enrichment (2, 6) of thermophilic AOA from terrestrial hot springs suggested a wide distribution of thermophilic AOA in geothermal environments. High concentrations of NH4+ (1, 9, 11) and high rates of ammonia oxidation (9, 22) have been observed at the Juan de Fuca Ridge. However, the presence of AOA in this deep-sea hydrothermal system has not been reported. Here, the abundance and diversity of AOA in three hydrothermal vent chimneys in the Endeavor segment of the Juan de Fuca Ridge were investigated by targeting the conserved amoA genes. This is also the first report on AOA from deep-sea hydrothermal vent chimneys.These vent chimneys were sulfide structures obtained in the fall of 2005 using the submersible Alvin on board the research vessel Atlantis (dive numbers 4143, 4136, and 4148). Chimney 4148 was an active black smoker venting at around 310°C in the Main Endeavor field (47°56.876′N, 129°5.915′W; depth, 2,192 m). Chimney 4143-1 was an active black smoker venting at 316°C in the Mothra field (47°55.424′N, 129°6.533′W; depth, 2,267 m). The outer layers (samples 4148-1A and 4143-1A) of these chimneys were used in this study. The sample from chimney 4136-1 was from a diffusive field (Clambed field) (47°57.909′N, 129°5.443′W; depth, 2,200 m), where the in situ temperature was measured as 29.2°C. The chimney samples were stored at −20°C on board, transported to the home laboratory on dry ice, and stored at −80°C until analyses were performed.Chimney samples were frozen in liquid nitrogen and milled upon thawing. This procedure was repeated three times to break down the solid sample into small particles, which were then mixed with DNA extraction buffer for DNA isolation as described before (25). The obtained crude DNA was purified by an E-Z N.A. Cycle-Pure kit (Omega Bio-Tek Inc., Norcross, GA). PCR amplifications for the archaeal 16S rRNA gene, the crenarchaeal marine group I (MGI) 16S rRNA gene, the archaeal amoA gene, and the bacterial amoA gene followed procedures previously described (Table (Table1)1) (3, 5, 10, 14). Quantitative PCR (Q-PCR) was performed using a model 7500 real-time system (Applied Biosystems, United Kingdom) and a 20-μl reaction mixture that consisted of 1 μl (1 to 10 ng) of DNA as the template, a 0.15 μM concentration of each primer, and 10 μl of Power SYBR green PCR master mix (Applied Biosystems, United Kingdom) with ROX and SYBR green I. The inserted PCR fragments of clones 4143-1A-71 (from the amoA gene library) and 4136-1-4 (from the archaeal 16S rRNA gene library) were amplified and purified to generate standard DNAs for amoA or archaeal 16S rRNA gene quantification. A serial dilution of standard DNAs was performed to generate calibration curves for sample quantification. A melting curve analysis was performed after amplification, and the cycle threshold was set automatically using system 7500 software, version 1.3.

TABLE 1.

PCR primers and procedures used in this study
Target genePrimerSequence (5′→3′)PCR cycle conditionsReference
Archaeal amoAArch-amoAFSTAATGGTCTGGCTTAGACG5 min at 95°C; 30 cycles consisting of 45 s at 94°C, 1 min at 53°C, and 1 min at 72°C; 15 min at 72°CFrancis et al., 2005 (5)
Arch-amoARGCGGCCATCCATCTGTATGT
Archaeal 16S rRNA21FTTCCGGTTGATCCYGCCRG5 min at 95°C; 30 cycles consisting of 30 s at 94°C, 1 min at 54°C, and 1 min at 72°C; 10 min at 72°CDeLong, 1992 (3)
958RYCCGGCGTTGAMTCCAATT
Archaeal 16S rRNA (for Q-PCR)344FACGGGGCGCAGCAGGCGCGA10 min at 50°C, 2 min at 95°C; 40 cycles consisting of 15 s at 95°C and 1 min at 60°C; 15 s at 95°C, 1 min at 60°C, and 15 s at 95°C to make the melting curveØvreås et al., 1998 (15)
518RATTACCGCGGCTGCTGG
Archaeal amoA (for Q-PCR)amo196FGGWGTKCCRGGRACWGCMAC10 min at 50°C and 2 min at 95°C; 40 cycles consisting of 15 s at 95°C and 1 min at 60°C; 15 s at 95°C, 1 min at 60°C, and 15 s at 95°C to make the melting curveTreusch et al., 2005 (20)
amo277RCRATGAAGTCRTAHGGRTADCC
Bacterial amoAAmoA-1FGGGGTTTCTACTGGTGGT5 min at 95°C; 30 cycles consisting of 30 s at 94°C, 45 s at 54°C-50°C, and 45 s at 72°C; 10 min at 72°CStephen et al., 1998 (19)
AmoA-2RCCCCTCKGSAAAGCCTTCTTCRotthauwe et al., 1997 (17)
Crenarchaeal marine group I 16S rRNA771FACGGTGAGGGATGAAAGCT5 min at 95°C; 30 cycles consisting of 30 s at 95°C, 30 s at 54°C, and 30 s at 72°COchsenreiter et al., 2003 (14)
957RCGGCGTTGACTCCAATTG
Open in a separate windowTriplicate PCR products were pooled and clone libraries constructed following the manufacturer''s instructions (Takara Inc., Dalian, China). PCR clones from the libraries were randomly selected for sequencing (Sangon Inc., China). Phylogenetic trees were generated using the PHYLIP package (4) and the maximum-likelihood, neighbor-joining, and maximum-parsimony methods. Bootstrap analysis was used to estimate the reliability of phylogenetic tree constructions (200 replicates). Trees were created using the program Treeview (version 1.6.6).Positive and specific PCR bands were obtained for the archaeal amoA genes from all the three samples, while no PCR band was obtained for the bacterial amoA gene (for the primers and procedures used, see Table Table1).1). In addition, sample 4136-1 was found by Q-PCR analysis to contain the highest number of archaeal amoA genes (with 7.36 ± 0.37 × 104 copies per g of chimney), followed by samples 4143-1A (with 1.88 ± 0.08 × 104 copies per g of chimney) and 4148-1A (with 1.37 ± 0.07 × 102 copies per g of chimney).Clone libraries of archaeal amoA from the three samples were constructed. A total of 93 clones (33 from sample 4136-1, 30 from sample 4143-1A, and 30 from sample 4148-1A) were sequenced and divided into 33 operational taxonomic units (OTUs) based on 99% nucleotide identity. The majority (81.7%) of the retrieved archaeal amoA OTU sequences exhibited relatively low identity (≤94.56%) to other archaeal amoA sequences deposited in GenBank. The phylogenetic relationships among the retrieved amoA and some published amoA sequences are shown in Fig. Fig.1.1. The chimney archaeal amoA sequences fell into five clusters (chimney group I, chimney group II, sediment A-1, and water column A and B clusters), except the sequence of clone 4143-1A-10, which did not fall into any cluster and exhibited the highest identity (90%) to the sequence of clone HB_B_0805A06, which was derived from coastal sediment (18). Chimney group I contained 52 sequences (30 from sample 4148-1A, 11 from sample 4143-1A, and 11 from sample 4136-1); chimney group II contained 23 sequences (20 from sample 4136-1 and 3 from sample 4143-1A). Fourteen sequences from sample 4143-1A grouped into water column A and B clusters (5); and one sequence from sample 4143-1A grouped into the sediment A-1 cluster (13). The sequences from chimney group I exhibited the highest identity (94%) to clone CR-G3N006, derived from a cold seep of the Japan Sea (13). Sequences in chimney group II exhibited the highest identity to clone OA-MA-122 from a water column of a coastal aquarium biofilter, with 84% nucleotide identity (21). The sequences of chimney group II did not cluster with any other sequences. Although showing low bootstrap values (<50%), the chimney group II sequences always clustered into a separate group (Fig. (Fig.1)1) according to different calculation methods, including the maximum-likelihood, neighbor-joining, and maximum-parsimony methods.Open in a separate windowFIG. 1.Phylogenetic tree showing the affiliations of archaeal amoA gene sequences from chimneys (in bold), sediments, soil, water, and the isolated AOA. Bootstrap values were calculated from 200 replications with 585 characters. Maximum-likelihood (left), distance (middle), and parsimony (right) bootstrap values providing ≥50% support are indicated. The bar represents 100 expected substitutions for the archaeal amoA region analyzed. Bacterial amoA sequences were set as the outgroup.Sample 4136-1 contained the highest number of archaeal amoA gene copies. Q-PCR using primers 344F and 518R (15) showed that sample 4136-1 contained 1.10 ± 0.05 × 106 copies of archaeal 16S rRNA genes per g of chimney. Assuming that each crenarchaeal cell possessed only one copy of the amoA gene (8), the AOA constituted at least 6.1% of the archaeal community in sample 4136-1. To explore the potential sources of these amoA sequences in sample 4136-1, an archaeal 16S rRNA clone library was constructed and a total of 82 clones were sequenced. These sequences divided into 20 OTUs based on 98% nucleotide identity. Fifteen OTUs (accounting 76.8% of the total sequences) belonged to hyperthermophilic Desulfurococcales species, and two OTUs (accounting for 15.9% of the total number of sequences) belonged to hyperthermophilic Thermoproteales species of the Crenarchaeota phylum, whereas three OTUs (accounting 7.32% of the total number of sequences) belonged to Thermococcales species of the Euryarchaeota kingdom (Fig. (Fig.2).2). Members of the crenarchaeal MGI, which was thought to be the source of nonthermophilic AOA (6, 8), were not detected in this library. Therefore, PCR using MGI-specific primers was performed to further detect MGI species (for PCR primers and conditions, see Table Table11 and reference 14). MGI species were easily detected in sample 4143-1A, but not in samples 4136-1 and 4148-1A, by direct PCR amplification. A nested PCR method employing generic archaeal 16S rRNA gene primers was then performed for the first round of PCR followed by MGI-selective PCR primers for the second round of PCR. This procedure created a PCR band of the correct size for MGI species from sample 4136-1; that band was later shown by cloning and sequencing to represent an MGI 16S rRNA gene fragment (see Fig. S1 in the supplemental material). The data implied that some of the amoA genes detected in the chimney samples may have come from MGI species; however, to determine the origin of the amoA genes, especially those in the chimney groups I and II, isolation or enrichment of the organisms would be necessary.Open in a separate windowFIG. 2.Phylogenetic tree showing the affiliations of 16S rRNA gene sequences retrieved from hydrothermal vent chimney 4136-1 (in boldface) with selected reference sequences of the Archaea domain. Bootstrap values were calculated from 200 replications with 790 characters. Maximum-likelihood (left), distance (middle), and parsimony (right) bootstrap values providing ≥50% support are indicated. The bar represents 100 expected substitutions for the archaeal 16S rRNA gene analyzed. Bacterial 16S rRNA sequences were set as the outgroup. HWCGIII, hot water crenarchaeotic group III.  相似文献   

19.
The compositions of archaeal and bacterial populations at different depths (60 m [mixolimnion-chemocline interface], 70 m [chemocline-subchemocline interface], 90 m, and 92 m [the water-sediment interface]) in the anoxic zone of the water column in Lake Pavin, a freshwater permanently stratified mountain lake in France, were determined. Phylogenetic trees were constructed from sequences to assess archaeal and bacterial diversity at the four sites.  相似文献   

20.
Heterotrophic bacteria in sea ice play a key role in carbon cycling, but little is known about the predominant players at the phylogenetic level. In a study of both algal bands and clear ice habitats within summertime Arctic pack ice from the Chukchi Sea, we determined the abundance of total bacteria and actively respiring cells in melted ice samples using epifluorescence microscopy and the stains 4', 6'-diamidino-2-phenylindole 2HCl (DAPI) and 5-cyano-2,3-ditolyl tetrazolium chloride (CTC), respectively. Organic-rich and -poor culturing media were used to determine culturable members by plating (at 0 degrees C and 5 degrees C) and most-probable-number (MPN) analyses (at -1 degrees C). Total bacterial counts ranged from 5.44 x 10(4) ml(-1) in clear ice to 2.41 x 10(6) ml(-1) in algal-band ice samples, with 2-27% metabolically active by CTC stain. Plating and MPN results revealed a high degree of culturability in both types of media, but greater success in oligotrophic media (to 62% of total abundance) and from clear ice samples. The bacterial enumeration anomaly, commonly held to mean 相似文献   

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