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Exposure of C. elegans to AOBr-containing surface water samples and to a M. aeruginosa batch culture

ABSTRACT: Elevated levels of adsorbable organic bromine compounds (AOBr) have been detected in German lakes, and cyanobacteria like Microcystis, which are known for the synthesis of microcystins, are one of the main producers of natural organobromines. However, very little is known about how environmental realistic concentrations of organobromines impact invertebrates. Here, the nematode C. elegans was exposed to AOBr-containing surface water samples and to a Microcystis aeruginosa enriched batch culture (MC-BA) and compared to single organobromines and microcystin-LR exposures. Stimulatory effects were observed in certain life trait variables, which were particularly pronounced in nematodes exposed to MC-BA. A whole genome DNA-microarray revealed that MC-BA led to the differential expression of more than 2000 genes, many of which are known to be involved in metabolic, neurologic, and morphologic processes. Moreover, the up-regulation of cyp- and the down-regulation of abu-genes suggested the presence of chronic stress. However, the nematodes were not marked by negative phenotypic responses. The observed difference in MC-BA and microcystin-LR (which impacted lifespan, growth and reproduction) exposed nematodes was hypothesized to be likely due to other compounds within the batch culture. Most likely the exposure to low concentrations of organobromines appears to buffer the effects of toxic substances, like microcystin-LR.

ORGANISM(S): Caenorhabditis elegans

PROVIDER: GSE68709 | GEO | 2015/05/12

SECONDARY ACCESSION(S): PRJNA283484

REPOSITORIES: GEO

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Project description:Zebrafish (Danio rerio) were obtained from the Zebrafish Research Facility maintained in the Center for Environmental Biotechnology at the University of Tennessee. Fish husbandry, spawning, and experimental procedures were conducted with approval from the University of Tennessee Institutional Animal Care and Use Committee (Protocol #1690-1007). Water for holding fish and conducting experiments (hereafter referred to as fish water) consisted of MilliQ water (Millipore, Bedford, MA) with ions added: 19 mg/L NaHCO3, 1 mg/L sea salt (Instant Ocean Synthetic Sea Salt, Mentor, OH), 10 mg/L CaSO4, 10 mg/L MgSO4, 2 mg/L KCl. Embryos were obtained by spawning adult fish with no history of contaminant exposure. Fertilization of embryos took place at the same time (Â± 15 min.), such that larvae used in experiments were of similar age at the time of exposure. All activities (maintenance of adult fish, spawning, and experiments) were conducted in an environmental chamber with a temperature of 27Â± 1 ÂºC and 14:10h light:dark photoperiod. Experiment Overall Design: At 72 h post-fertilization, zebrafish larvae were exposed to lyophilized Microcystis and purified MC-LR at concentrations of 100 and 1,000 Âµg/L. Controls consisted of zebrafish system water (negative control) and zebrafish system water containing 0.05% ethanol (vehicle control). Larvae from both control groups as well as 100 Âµg/L MC-LR, 1,000 Âµg/L MC-LR, and lyophilized Microcystis were exposed in groups of 50 with three replicates and were sacrificed after 96 hours for total RNA extraction and subsequent microarray analysis. All larvae were exposed in beakers containing 100 ml of solution. Experiment Overall Design: Water samples for microcystin analysis and water quality measurements were taken during the experiment, and mortality and behavioral observations were recorded at 24-hour intervals. Microcystin analysis was conducted by protein phosphatase inhibition assay. Measured concentrations of microcystin-LR were 140 Â± 12 SD (low concentration) and 1,703 Â± 71 SD (high concentration). The concentration of microcystin-LR in the lyophilized Microcystis treatment was 4.5 Âµg/L. Water quality parameters measured included dissolved oxygen (6.7 mg/L), pH (6.9), total alkalinity (36 mg/L as CaCO3), total hardness (18 mg/L as CaCO3), and ammonia (<0.2 mg/L). No significant mortality or behavioral changes in larvae were observed during the exposure.

Project description:Microcystins (MCs) are cyclic hepatotoxins produced worldwide by various species of cyanobacteria. Their structure includes two variable amino acids (AAs) and most of the studies focused on the most toxic variant: the microcystin LR (MC-LR). However, more than 80 MC variants have been described to date. Despite ingestion being the major pathway of human exposure, few in vivo studies have demonstrated macroscopic effects on the gastro-intestinal tract, but no data are available on the affected pathways by several variants on intestinal cells. Here, using a non-selective method, we investigated for the first time the effect of MC-RR and MC-LR on the human intestinal cell line Caco-2 and compared their response at the pangenomic scale. The cells were incubated for 4 hrs or 24 hrs with the same range of sub-lethal concentrations of MC-RR or MC-LR. Low effects were observed for both variants after a short-term exposure. On the contrary, dose-dependent modulations of the genes transcription levels were noticed with MC-RR and MC-LR after 24 hrs. Furthermore, the genomic profiles induced by both variants were similar suggesting a common toxicity mechanism but with higher modulation following MC-LR than MC-RR exposure. However, the functional annotation revealed major differences between the variants effects. Indeed, the well-known MC-LR affected mainly two pathways, the oxidative stress response and the cell cycle regulation, which did not elicit significant alteration following MC-RR exposure. This work is the first comparative description of the MC-LR and MC-RR effects on a human intestinal cell model. It allowed us to suggest differences in the mechanism of toxicity for MC-RR and MC-LR. These results illustrate that the toxicity of MC variants remains a key point for risk assessment. Differentiated Caco-2 cells were exposed to microcystins in free FCS culture medium for either 4 or 24 hours. Sub-lethal concentrations of 10, 50 and 100 M-BM-5M of MC-LR or MC-RR were chosen for 4 hours, while 1, 5 and 10 M-BM-5M were selected for 24 hours. For each condition (including the controls), the solvent concentration was fixed to 2% EtOH for MC-LR and 1.5% of 80% MeOH for MC-RR. Four to five culture replicates per condition were done.

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Exposure of C. elegans to AOBr-containing surface water samples and to a M. aeruginosa batch culture

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