Unknown,Transcriptomics,Genomics,Proteomics

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Using transcriptomic tools to evaluate biological effects across effluent gradients at a diverse set of study sites in Minnesota, USA

ABSTRACT: To assess the impact of a municiple effluent across different environments, a gradient design (upstream, downstream, and at effluent) was set up across three waste water treatment plant outflows in three different regions of MN. These three sites represents vastly different land use and contamination profiles. The upstream location at each site was used as a point of comparison to reduce site specific differences in water. Fish were exposed at three sites in three locations for 4 days. The objectives of the study were to 1). determine if biological impact of the effluent could be detected at the downstream site; 2). If the use of the upstream site would allow point source influence to be detected over the ambient level of biological activity; 3). if using functional analyses of transcriptomic results would show similarities between effleunt and downstream sites. The current series contains n=53 microarrays associated with fish exposed at three locations (upstream, effluent, downstream) at 3 different site R, H, E for 4 days until tissues were collected At the specific locations (UP, EF, DS), sexually mature female fathead minnows (SI-SM2) were exposed to location specific water in mini-mobile environmental monitoring units (MMU)14 for a period of 4d, at each of three sites (R, H, E) during the summer and fall of 2010 (SI-SM3). The MMUs allowed for consistency in aeration, temperature, and feeding. In the case of the riverine R and H sites, the MMU was supplied with a continuous flow of location-specific water. Due to logistical constraints, exposures at the lake site (E) were conducted under static renewal conditions within the MMUs. However, the cumulative number of daily water exchanges were equivalent to those in the flow-through studies. After exposure fish were anesthetized (buffered MS-222), and necropsied at a facility near the site, specific tissues were excised and flash frozen in liquid nitrogen, and stored at -80M-BM-0C. Gonads were removed from female and flash-frozen for gene expression analyses using microarray. Ovarian transcripts from six females per location (three locations per site, three sites) were analyzed using a custom 15,000 feature microarray (GEO Platform Accession GPL9248). Data sets for this phase (n=53 microarrays) were normalized independently using Fastlo (Ballman et al., 2004) implemented in R (http://www.r-project.org/), but analyzed using parallel approaches.

ORGANISM(S): Pimephales promelas

SUBMITTER: Jason Berninger

PROVIDER: E-GEOD-53204 | biostudies-arrayexpress |

REPOSITORIES: biostudies-arrayexpress

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Project description:The federally endangered Okaloosa darter (Etheostoma okaloosae) is found almost exclusively on the Eglin Air Force Base in the Choctawhatchee Bay watershed of Florida. Portions of this limited habitat are threatened with erosion of soils, altered hydrology, and impaired water quality. One stream reach in particular, East Turkey Creek, has demonstrated potential water quality problems including poor invertebrate bioassessment scores (IBI), uncharacteristically high conductivity values, and low numbers of Okaloosa darters. General water quality (dissolved oxygen, specific conductance, pH, temperature, and relative turbidity and primary productivity) was characterized in both the potentially impacted East Turkey Creek and a reference stream (Long Creek). Water quality was assessed during a 30 day exposure using passive samplers for both non-polar and polar effluent parameters. Metal loading in the system was assessed via fish tissue burdens in resident Pteronotropis hypseleotris. Additionally, microarray analysis was performed on gonad and liver tissue from fathead minnows, Pimephales promelas, after 48-h exposures to water collected from the two creeks and brought into the laboratory. Gene expression changes were evident at the site below the influence of a wastewater spray field sited along East Turkey Creek, suggesting that anthropogenic compounds in the effluent waters may have affected both liver and testis function and could be related to account the general decrease in populations of the Okaloosa darter. Array hybridizations were performed using a single color design. Four biological replicates consisting of four different individuals were analyzed for each of the treatments (University of Florida control, and each of five sites). Site C was left out of subsequent analysis for publication, due to poor characterization of the site. Two Samples were left out of the normalization/analysis due to QC failure. Therefore, there are only 3 replicates of the "testis, site A water, exposed 48 h." and "liver, site E water, exposed 48 h." groups.

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Project description:Three surface waters in Gainesville, Florida were used in a 48 hour whole effluents exposure to assess gene expression profiles of male fathead minnow liver. Microarray analysis was used to determine changes in gene expression of exposed fish to waters from a site downstream of a wastewater treatment plant (streamwater), a wastewater treatment plant (wastewater), and a lake (stormwater). Differences in gene expression between fish exposed to collected waters and controls were observed. Number of altered genes and biological processes were 1028 and 18 for stormwater; 787 and 19 for streamwater; and: 575 and 12 for wastewater. In general, the effects observed in all exposed fish were related with fatty acid metabolism, DNA repair, oxidation-reduction process, cell wall catabolic process and apoptosis. All exposed fish showed altered expression of genes related with DNA damage repair. In particular fish exposed to stormwater and streamwater showed downregulation of several key intermediates transcripts of cholesterol. The presence and environmental persistence of perfluorinated chemicals (PFCs) in these waters, the resemblance in known effects on transcripts with those found in this study, suggest that the set of genes differentially regulated in fathead minnows after 48 hours of exposure may be attributed to exposure to PFCs. Three surface water sites were chosen for effluent collection in Gainesville, Florida: A lake (stormwater), surface water downstream of a wastewater treatment plant (streamwater), and a wastewater treatment plant effluent used for landscaping irrigation (wastewater). Water from each site was collected two days prior to the fish exposure experiment using Chemfluor ® tubing and a 120 liters steel barrels coated with polyester resin (gel coat) to avoid cross-contamination. Three barrels for each effluent were collected during day 1. Water from the barrel was transported to the laboratory and pumped into four fiberglass cylinders in the aquatic toxicology facility. Water from each cylinder was then pumped into four replicate aquariums per treatment and kept for 1 day without fish (pre-treatment). On day 2, four male fathead minnows from a common tank were transferred to each replicate aquarium and kept for 48 hours, with one 75% water change after first 24 hours. The exposure system consisted of 40 L glass aquaria. Each exposure was conducted in quadruplicate and each aquarium contained the four male fish in 25 L of treatment water . The water used in the control treatment was carbon filtered, dechlorinated tap water. The positions of the treatment tanks were randomized and test initiation times were staggered to ensure an exposure/sampling interval of 48 h. The fish were not fed during the experiment. The temperature range of the water was 24-26 °C with a photoperiod of 16 h light: 8 h dark. Liver was isolate from 4 males indviduals for each treatment except for control group (3 individuals).

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Using transcriptomic tools to evaluate biological effects across effluent gradients at a diverse set of study sites in Minnesota, USA

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