TY - JOUR A1 - Almeida, Â. A1 - Freitas, R. A1 - Calisto, V. A1 - Esteves, V. I. A1 - Schneider, Rudolf A1 - Soares, A. M. V. M. A1 - Figueira, E. A1 - Campos, B. A1 - Barata, C. T1 - Effects of carbamazepine and cetirizine under an ocean acidification scenario on the biochemical and transcriptome responses of the clam Ruditapes philippinarum N2 - Several works evaluated the toxicity of pharmaceutical drugs and climate related changes in invertebrates but few explored the combined effects of both stressors, namely considering their mode of action (MoA). Carbamazepine (CBZ) and cetirizine (CTZ) are pharmaceutical drugs detected in the environment and the toxicity derived from the combined effects of these drugs with ocean acidification (OA) is poorly explored. Thus, the present study investigated the biochemical parameters related to an oxidative stress response and the transcription of genes related to the MoA of CBZ (1.0 mg/L) and CTZ (0.6 mg/L) in the clam Ruditapes philippinarum chronically exposed (28 days) to control (7.8) and low (7.5) pH conditions. The results obtained showed that despite the clams accumulated both drugs, at low pH the clams exposed to CTZ decreased drug concentration and BCF values (CTZ uptake: 2.0 ± 0.5 ng/g fresh weight; BCF: 3.8 ± 0.9) in comparison with clams exposed to control pH (CTZ uptake: 2.9 ± 0.3 ng/g fresh weight; BCF: 5.5 ± 0.6). No oxidative stress was induced by the exposure to CBZ or CTZ at each pH level, but the transcription of several genes related with the MoA (neurotransmission, immunity and biomineralization) was altered by low pH, drug exposure and the combination of both stressors. At both pH conditions, CBZ increased the transcription of GABA receptor gene (neurotransmission) and CTZ led to a decrease of Perlucin gene (biomineralization) transcription. The transcription of MyD88 gene (immunity) decreased at low pH (7.5) combined with drug exposure (CBZ or CTZ). Thus, it was highlighted that the interaction of drug exposure and low pH conditions can change bivalves’ sensitivity to drugs or alter drugs toxicity. KW - Carbamazepine KW - Biomarker KW - ELISA KW - Biochemische Parameter PY - 2018 DO - https://doi.org/10.1016/j.envpol.2017.12.121 SN - 0269-7491 VL - 235 SP - 857 EP - 868 PB - Elsevier Ltd. CY - Amsterdam, NL AN - OPUS4-44739 LA - eng AD - Bundesanstalt fuer Materialforschung und -pruefung (BAM), Berlin, Germany ER - TY - JOUR A1 - Mugani, R. A1 - El Khalloufi, F. A1 - Kasada, M. A1 - Redouane, E. M. A1 - Haida, M. A1 - Aba, R. P. A1 - Essadki, Y. A1 - Zerrifi, S. E. A. A1 - Herter, Sven-Oliver A1 - Hejjaj, A. A1 - Aziz, F. A1 - Ouazzani, N. A1 - Azevedo, J. A1 - Campos, A. A1 - Putschew, A. A1 - Grossart, H.-P. A1 - Mandi, L. A1 - Vasconcelos, V. A1 - Oudra, B. T1 - Monitoring of toxic cyanobacterial blooms in Lalla Takerkoust reservoir by satellite imagery and microcystin transfer to surrounding farms N2 - Cyanobacterial harmful algal blooms (CyanoHABs) threaten public health and freshwater ecosystems worldwide. In this study, our main goal was to explore the dynamics of cyanobacterial blooms and how microcystins (MCs) move from the Lalla Takerkoust reservoir to the nearby farms. We used Landsat imagery, molecular analysis, collecting and analyzing physicochemical data, and assessing toxins using HPLC. Our investigation identified two cyanobacterial species responsible for the blooms: Microcystis sp. and Synechococcus sp. Our Microcystis strain produced three MC variants (MC-RR, MC-YR, and MC-LR), with MC-RR exhibiting the highest concentrations in dissolved and intracellular toxins. In contrast, our Synechococcus strain did not produce any detectable toxins. To validate our Normalized Difference Vegetation Index (NDVI) results, we utilized limnological data, including algal cell counts, and quantified MCs in freeze-dried Microcystis bloom samples collected from the reservoir. Our study revealed patterns and trends in cyanobacterial proliferation in the reservoir over 30 years and presented a historical map of the area of cyanobacterial infestation using the NDVI method. The study found that MC-LR accumulates near the water surface due to the buoyancy of Microcystis. The maximum concentration of MC-LR in the reservoir water was 160 μg/L. In contrast, 4 km downstream of the reservoir, the concentration decreased by a factor of 5.39 to 29.63 μg/L, indicating a decrease in MC-LR concentration with increasing distance from the bloom source. Similarly, the MC-YR concentration decreased by a factor of 2.98 for the same distance. Interestingly, the MC distribution varied with depth, with MC-LR dominating at the water surface and MC-YR at the reservoir outlet at a water depth of 10 m. Our findings highlight the impact of nutrient concentrations, environmental factors, and transfer processes on bloom dynamics and MC distribution. We emphasize the need for effective management strategies to minimize toxin transfer and ensure public health and safety. KW - Cyanotoxin KW - HPLC-MS/MS KW - Surface water PY - 2024 UR - https://nbn-resolving.org/urn:nbn:de:kobv:b43-623672 DO - https://doi.org/10.1016/j.hal.2024.102631 SN - 1568-9883 VL - 135 SP - 1 EP - 14 PB - Elsevier CY - Amsterdam AN - OPUS4-62367 LA - eng AD - Bundesanstalt fuer Materialforschung und -pruefung (BAM), Berlin, Germany ER - TY - JOUR A1 - Selbmann, L. A1 - Benkő, Z. A1 - Coleine, C. A1 - de Hoog, S. A1 - Donati, C. A1 - Druzhinina, I. A1 - Emri, T. A1 - Ettinger, C. L. A1 - Gladfelter, A. S. A1 - Gorbushina, Anna A1 - Grigoriev, I. V. A1 - Grube, M. A1 - Gunde-Cimerman, N. A1 - Karányi, Z. A. A1 - Kocsis, B. A1 - Kubressoian, T. A1 - Miklós, I. A1 - Miskei, M. A1 - Muggia, L. A1 - Northen, T. A1 - Novak-Babič, M. A1 - Pennacchio, C. A1 - Pfliegler, W. P. A1 - Pòcsi, I. A1 - Prigione, V. A1 - Riquelme, M. A1 - Segata, N. A1 - Schumacher, Julia A1 - Shelest, E. A1 - Sterflinger, K. A1 - Tesei, D. A1 - U’Ren, J. M. A1 - Varese, G. C. A1 - Vázquez-Campos, X. A1 - Vicente, V. A. A1 - Souza, E. M. A1 - Zalar, P. A1 - Walker, A. K. A1 - Stajich, J. E. T1 - Shed Light in the DaRk LineagES of the Fungal Tree of Life—STRES N2 - The polyphyletic group of black fungi within the Ascomycota (Arthoniomycetes, Dothideomycetes, and Eurotiomycetes) is ubiquitous in natural and anthropogenic habitats. Partly because of their dark, melanin-based pigmentation, black fungi are resistant to stresses including UV- and ionizing-radiation, heat and desiccation, toxic metals, and organic pollutants. Consequently, they are amongst the most stunning extremophiles and poly-extreme-tolerant organisms on Earth. Even though ca. 60 black fungal genomes have been sequenced to date, [mostly in the family Herpotrichiellaceae (Eurotiomycetes)], the class Dothideomycetes that hosts the largest majority of extremophiles has only been sparsely sampled. By sequencing up to 92 species that will become reference genomes, the “Shed light in The daRk lineagES of the fungal tree of life” (STRES) project will cover a broad collection of black fungal diversity spread throughout the Fungal Tree of Life. Interestingly, the STRES project will focus on mostly unsampled genera that display different ecologies and life-styles (e.g., ant- and lichen-associated fungi, rock-inhabiting fungi, etc.). With a resequencing strategy of 10- to 15-fold depth coverage of up to ~550 strains, numerous new reference genomes will be established. To identify metabolites and functional processes, these new genomic resources will be enriched with metabolomics analyses coupled with transcriptomics experiments on selected species under various stress conditions (salinity, dryness, UV radiation, oligotrophy). The data acquired will serve as a reference and foundation for establishing an encyclopedic database for fungal metagenomics as well as the biology, evolution, and ecology of the fungi in extreme environments. KW - Adaptation KW - Black fungi KW - Dothideomycetes KW - Eurotiomycetes KW - Extremophiles KW - Genomics KW - Metabolomics KW - Secondary metabolites KW - Stress conditions KW - Transcriptomics PY - 2020 UR - https://nbn-resolving.org/urn:nbn:de:kobv:b43-519328 DO - https://doi.org/10.3390/life10120362 VL - 10 IS - 12 SP - 362 PB - MDPI CY - Basel AN - OPUS4-51932 LA - eng AD - Bundesanstalt fuer Materialforschung und -pruefung (BAM), Berlin, Germany ER -