Ontology highlight
ABSTRACT:
PROVIDER: PRJNA474004 | ENA |
REPOSITORIES: ENA
Dataset's files
| Action | DRS | |||
|---|---|---|---|---|
| SRR7242780_1.fastq.gz | Fastqsanger.gz | |||
| SRR7242780_2.fastq.gz | Fastqsanger.gz | |||
| SRR7242790_1.fastq.gz | Fastqsanger.gz | |||
| SRR7242790_2.fastq.gz | Fastqsanger.gz | |||
| SRR7242800_1.fastq.gz | Fastqsanger.gz |
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Project description:The effects of long-term experiment on bacterial community
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Project description:Here we have compared adult wildtype (N2) C. elegans gene expression when grown on different bacterial environments/fod sources in an effort to model naturally occuring nematode-bacteria interactions at the Konza Prairie. We hypothesize that human-induced changes to natural environments, such as the addition of nitrogen fertalizer, have effects on the bacterial community in soils and this drives downstream changes in the structure on soil bacterial-feeding nematode community structure. Here we have used transcriptional profiling to identify candidate genes involved in the interaction of nematodes and bacteria in nature.
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Project description:Enclosure experiments are frequently used to investigate the impact of changing environmental conditions on microbial assemblages. Yet, the question how individual members of bacterial communities respond to challenges posed by the incubation itself remained unanswered. We used metaproteomic profiling, 16S rRNA gene analysis and high nucleic acid content analysis to monitor bacterial communities during long-term incubations (55 days) under marine (M1), mesohaline (M2) and oligohaline (M3) conditions with and without the addition of terrestrial dissolved organic matter. Our results showed that early in the experiment (after one week, T2), bacterial communities were highly diverse and their composition differed significantly between marine, mesohaline and oligohaline conditions. Controls (BS) and tDOM-treated samples (FKB) showed notable differences at this stage. In contrast, in the late phase of the experiment (after 55 days, T6), bacterial communities in both, manipulated and untreated marine and mesohaline enclosures were quite similar to each other and were dominated by gammaproteobacterial Spongiibacter. In the oligohaline enclosure, the actinobacterial hgc-I clade was very abundant in this phase. Our findings suggest that individual capacities, e.g. grazing-resistance, antibiotics production, and the ability to access alternative carbon sources may enable Spongiibacter and hgc-I clade members to successfully prevail during long-term incubations. Bacterial community composition in enclosure experiments thus seems to be strongly influenced by the individual inherent bacterial strategies to cope with the incubation as such. Researchers intending to investigate the effects of manipulation on complex microbial communities may therefore want to use short incubation periods or sophisticated systems that avoid these unspecific effects of long-term experiments.
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Project description:High Arctic soils have low nutrient availability, low moisture content and very low temperatures and, as such, they pose a particular problem in terms of hydrocarbon bioremediation. An in-depth knowledge of the microbiology involved in this process is likely to be crucial to understand and optimize the factors most influencing bioremediation. Here, we compared two distinct large-scale field bioremediation experiments, located at Alert (ex situ approach) and Eureka (in situ approach), in the Canadian high Arctic. Bacterial community structure and function were assessed using microarrays targeting the 16S rRNA genes of bacteria found in cold environments and hydrocarbon degradation genes as well as reverse-transcriptase real-time PCR targeting key functional genes. Results indicated a large difference between sampling sites in terms of both soil microbiology and decontamination rates. A rapid reorganization of the bacterial community structure and functional potential as well as rapid increases in the expression of alkane monooxygenases and polyaromatic hydrocarbon ring-hydroxylating-dioxygenases were observed one month after the bioremediation treatment commenced in the Alert soils. In contrast, no clear changes in community structure were observed in Eureka soils, while key gene expression increased after a relatively long lag period (1 year). Such discrepancies are likely caused by differences in bioremediation treatments (i.e. ex situ vs. in situ), weathering of the hydrocarbons, indigenous microbial communities, and environmental factors such as soil humidity and temperature. In addition, this study demonstrates the value of molecular tools for the monitoring of polar bacteria and their associated functions during bioremediation. 38 soil samples from two high arctic locations that were contaminated-treated, contaminated or not contaminated followed for up to 4 years
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Project description:High Arctic soils have low nutrient availability, low moisture content and very low temperatures and, as such, they pose a particular problem in terms of hydrocarbon bioremediation. An in-depth knowledge of the microbiology involved in this process is likely to be crucial to understand and optimize the factors most influencing bioremediation. Here, we compared two distinct large-scale field bioremediation experiments, located at Alert (ex situ approach) and Eureka (in situ approach), in the Canadian high Arctic. Bacterial community structure and function were assessed using microarrays targeting the 16S rRNA genes of bacteria found in cold environments and hydrocarbon degradation genes as well as reverse-transcriptase real-time PCR targeting key functional genes. Results indicated a large difference between sampling sites in terms of both soil microbiology and decontamination rates. A rapid reorganization of the bacterial community structure and functional potential as well as rapid increases in the expression of alkane monooxygenases and polyaromatic hydrocarbon ring-hydroxylating-dioxygenases were observed one month after the bioremediation treatment commenced in the Alert soils. In contrast, no clear changes in community structure were observed in Eureka soils, while key gene expression increased after a relatively long lag period (1 year). Such discrepancies are likely caused by differences in bioremediation treatments (i.e. ex situ vs. in situ), weathering of the hydrocarbons, indigenous microbial communities, and environmental factors such as soil humidity and temperature. In addition, this study demonstrates the value of molecular tools for the monitoring of polar bacteria and their associated functions during bioremediation. 38 soil samples from two high arctic locations that were contaminated-treated, contaminated or not contaminated followed for up to 4 years
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