A two-probe proximal chaperone detection system consisting of a species-specific capture probe for the microarray and a labeled, proximal chaperone probe for detection was recently described for direct detection of intact rRNAs from environmental samples on oligonucleotide arrays. In this study, we investigated the physical spacing and nucleotide mismatch tolerance between capture and proximal chaperone detector probes that are required to achieve species-specific 16S rRNA detection for the dissimilatory metal and sulfate reducer 16S rRNAs. Microarray specificity was deduced by analyzing signal intensities across replicate microarrays with a statistical analysis-of-variance model that accommodates well-to-well and slide-to-slide variations in microarray signal intensity. Chaperone detector probes located in immediate proximity to the capture probe resulted in detectable, nonspecific binding of nontarget rRNA, presumably due to base-stacking effects. Species-specific rRNA detection was achieved by using a 22-nt capture probe and a 15-nt detector probe separated by 10 to 14 nt along the primary sequence. Chaperone detector probes with up to three mismatched nucleotides still resulted in species-specific capture of 16S rRNAs. There was no obvious relationship between position or number of mismatches and within-or between-genus hybridization specificity. From these results, we conclude that relieving secondary structure is of principal concern for the successful capture and detection of 16S rRNAs on planar surfaces but that the sequence of the capture probe is more important than relieving secondary structure for achieving specific hybridization.DNA microarrays are currently used for gene expression profiling (18, 25), DNA sequencing (24), disease screening (17), diagnostics (9, 29), and genotyping (14), usually within the context of clinical applications. The extension of microarray technology to the detection and analysis of 16S rRNAs in mixed microbial communities likewise holds tremendous potential for microbial community analysis, pathogen detection, and process monitoring in both basic and applied environmental sciences (7,12,27). The application of microarrays for unattended in-field or point-of-use environmental applications, however, frequently involves requirements to (i) detect many different microorganisms simultaneously, (ii) utilize a bioanalytical detection method that is conducive to automation and/or field deployment, (iii) monitor RNA as a qualitative indicator of microbial activity, and (iv) quantify RNA levels and/or the extent of microbial activity. Such requirements are especially pertinent for monitoring changes in microbial community composition and activity through time and space. Thus, continued use of microarray protocols that rely on PCR amplification represents a significant bottleneck for the routine application and deployment of microarrays in the field and highlights the need to develop sensitive and specific direct RNA detection methods for environmental samples.There are several rep...