ArticleApplied and environmental microbiology2008
Feasibility of transferring fluorescent in situ hybridization probes to an 18S rRNA gene phylochip and mapping of signal intensities.
Article in Applied and environmental microbiology, 2008. The graph could read no effect estimate from its abstract, so it casts no vote on the map. Cited by 13 papers.
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Who cites it
13 citing papers in PubMed, 41 citations in OpenAlex.
- Endophytic and ectomycorrhizal, an overlooked dual ecological niche? Insights from natural environments and Russula species.The New phytologist · 2026Article
- Newly Designed Fluorescence In Situ Hybridization Probes Reveal Previously Unknown Endophytic Abilities of Tuber magnatum in Herbaceous Plants.Microbial ecology · 2025Article
- Evolution of the MIDTAL microarray: the adaption and testing of oligonucleotide 18S and 28S rDNA probes and evaluation of subsequent microarray generations with Prymnesium spp. cultures and field samples.Environmental science and pollution research international · 2015Article
- Parallel detection of harmful algae using reverse transcription polymerase chain reaction labeling coupled with membrane-based DNA array.Environmental science and pollution research international · 2014Article
- High genetic diversity and novelty in eukaryotic plankton assemblages inhabiting saline lakes in the Qaidam basin.PloS one · 2014Article
- Specificity of LSU rRNA-targeted oligonucleotide probes for Pseudo-nitzschia species tested through dot-blot hybridisation.Environmental science and pollution research international · 2014Article
- Strengths and weaknesses of microarray approaches to detect Pseudo-nitzschia species in the field.Environmental science and pollution research international · 2013Article
- An evaluation of the applicability of microarrays for monitoring toxic algae in Irish coastal waters.Environmental science and pollution research international · 2013Article
- Molecular probes and microarrays for the detection of toxic algae in the genera Dinophysis and Phalacroma (Dinophyta).Environmental science and pollution research international · 2013Article
- Note: steps taken to optimise probe specificity and signal intensity prior to field validation of the MIDTAL (Microarray for the Detection of Toxic Algae).Environmental science and pollution research international · 2013Article
- Evaluation of the MIDTAL microarray chip for monitoring toxic microalgae in the Orkney Islands, U.K.Environmental science and pollution research international · 2013Article
- Molecular detection, quantification, and diversity evaluation of microalgae.Marine biotechnology (New York, N.Y.) · 2012Review
- Hierarchical oligonucleotide primer extension as a time- and cost-effective approach for quantitative determination of Bifidobacterium spp. in infant feces.Applied and environmental microbiology · 2009Article
Corrections and comments
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Authors and funding
2 authors at 1 institution in 1 country.
Funding
No grant is acknowledged in the PubMed record.
Abstract
DNA microarray technology offers the possibility to analyze microbial communities without cultivation, thus benefiting biodiversity studies. We developed a DNA phylochip to assess phytoplankton diversity and transferred 18S rRNA probes from dot blot or fluorescent in situ hybridization (FISH) analyses to a microarray format. Similar studies with 16S rRNA probes have been done determined that in order to achieve a signal on the microarray, the 16S rRNA molecule had to be fragmented, or PCR amplicons had to be <150 bp in length to minimize the formation of a secondary structure in the molecule so that the probe could bind to the target site. We found different results with the 18S rRNA molecule. Four out of 12 FISH probes exhibited false-negative signals on the microarray; eight exhibited strong but variable signals using full-length 18S RNA molecules. A systematic investigation of the probe's accessibility to the 18S rRNA gene was made using Prymenisum parvum as the target. Fourteen additional probes identical to this target covered the regions not tested with existing FISH probes. Probes with a binding site in the first 900 bp of the gene generated positive signals. Six out of nine probes binding in the last 900 bp of the gene produced no signal. Our results suggest that although secondary structure affected probe binding, the effect is not the same for the 18S rRNA gene and the 16S rRNA gene. For the 16S rRNA gene, the secondary structure is stronger in the first half of the molecule, whereas in the 18S rRNA gene, the last half of the molecule is critical. Probe-binding sites within 18S rRNA gene molecules are important for the probe design for DNA phylochips because signal intensity appears to be correlated with the secondary structure at the binding site in this molecule. If probes are designed from the first half of the 18S rRNA molecule, then full-length 18S rRNA molecules can be used in the hybridization on the chip, avoiding the fragmentation and the necessity for the short PCR amplicons that are associated with using the 16S rRNA molecule. Thus, the 18S rRNA molecule is a more attractive molecule for use in environmental studies where some level of quantification is desired. Target size was a minor problem, whereas for 16S rRNA molecules target size rather than probe site was important.
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