To meet the specified objective, photolysis kinetics and the impact of dissolved organic matter (DOM) and reactive oxygen species (ROSs) scavengers on the rates of photolysis, the formation of photoproducts, and the resulting photo-enhanced toxicity to Vibrio fischeri were determined for four neonicotinoids. Analysis of the photodegradation of imidacloprid and imidaclothiz revealed the importance of direct photolysis (photolysis rate constants: 785 x 10⁻³ and 648 x 10⁻³ min⁻¹, respectively). In contrast, the photodegradation of acetamiprid and thiacloprid was predominantly governed by photosensitization mediated by hydroxyl radical reactions and transformations (photolysis rate constants: 116 x 10⁻⁴ and 121 x 10⁻⁴ min⁻¹, respectively). All four neonicotinoid insecticides demonstrated elevated toxicity to Vibrio fischeri when exposed to light, implying that the resulting photolytic products are more toxic than their respective parent compounds. read more Incorporating DOM and ROS scavengers influenced the photochemical transformation rates of parent compounds and their intermediaries, resulting in a spectrum of photolysis rates and photo-enhanced toxicity in the four insecticides, originating from disparate photochemical processes. Gaussian calculations, combined with the analysis of intermediate chemical structures, demonstrated variations in photo-enhanced toxicity mechanisms across the four neonicotinoid insecticides. Molecular docking analysis served to elucidate the toxicity mechanism operating in parent compounds and their photolytic derivatives. Following this, a theoretical model was utilized to portray the diversity of toxicity responses to each of the four neonicotinoids.
The discharge of nanoparticles (NPs) into the environment triggers interactions with co-occurring organic pollutants, producing a compound toxic impact. A more realistic examination of the possible toxic effects of nanoparticles and coexisting pollutants on aquatic life forms is essential. Across three karst natural water sources, we analyzed the synergistic toxicity of TiO2 nanoparticles (TiO2 NPs) and three types of organochlorines (OCs)—pentachlorobenzene (PeCB), 33',44'-tetrachlorobiphenyl (PCB-77), and atrazine—on algae (Chlorella pyrenoidosa). TiO2 NPs and OCs, when present individually in natural water, displayed less toxicity than in OECD medium; their combined toxicity, although showing variations from that of OECD medium, exhibited a general similarity. The combined and individual toxicities reached their highest levels in UW. The correlation analysis established a primary connection between TOC, ionic strength, Ca2+, and Mg2+ in natural water and the observed toxicities of TiO2 NPs and OCs. The toxic effects of PeCB and atrazine, combined with TiO2 NPs, were found to be synergistic in their impact on algae. The binary mixture of TiO2 NPs and PCB-77 demonstrated an antagonistic toxicity profile against algae. Organic compound uptake by algae increased due to the presence of TiO2 nanoparticles. PeCB and atrazine fostered a rise in the accumulation of algae with TiO2 nanoparticles, in contrast to PCB-77. The preceding findings suggest that karst natural waters, characterized by diverse hydrochemical properties, played a role in the observed variations in toxic effects, structural and functional damage, and bioaccumulation between TiO2 NPs and OCs.
Aflatoxin B1 (AFB1) contamination poses a risk to aquafeed safety. The gills of fish are indispensable for their breathing. read more Nonetheless, limited studies have sought to understand how aflatoxin B1 in the diet influences the gills. The present study investigated the consequences of AFB1 exposure on the structural and immune barriers in the gills of grass carp. Elevated dietary AFB1 levels resulted in a surge of reactive oxygen species (ROS), protein carbonyl (PC), and malondialdehyde (MDA), ultimately triggering oxidative damage. Dietary AFB1 had a contrary effect on antioxidant enzyme activity by decreasing their activities, the relative expression of related genes (with the exception of MnSOD), and levels of glutathione (GSH) (P < 0.005). This effect was, at least in part, mediated by the NF-E2-related factor 2 (Nrf2/Keap1a). On top of that, aflatoxin B1 in the diet contributed to the disruption of DNA integrity. Excluding Bcl-2, McL-1, and IAP, apoptosis-related genes showed a statistically significant upregulation (P < 0.05), potentially indicating a contribution of p38 mitogen-activated protein kinase (p38MAPK) to the upregulation of apoptosis. Significant reductions were seen in the relative expression (P < 0.005) of genes related to tight junctions (TJs), excluding ZO-1 and claudin-12, suggesting a regulatory role of myosin light chain kinase (MLCK) in tight junction function. Dietary AFB1, in its entirety, compromised the structural integrity of the gill. The presence of AFB1 was associated with increased gill susceptibility to F. columnare, increased prevalence of Columnaris disease, and reduced antimicrobial substance production (P < 0.005) in grass carp gills. This was coupled with upregulation of genes related to pro-inflammatory factors (excluding TNF-α and IL-8), the pro-inflammatory response possibly linked to the activity of nuclear factor-kappa B (NF-κB). During this period, anti-inflammatory factors in the grass carp gills were found to be downregulated (P < 0.005) after being exposed to F. columnare, with the target of rapamycin (TOR) as a potential contributing element. Subsequent to F. columnare challenge, AFB1 was found to worsen the impairment of the immune barrier in the gills of grass carp, as the data indicated. Based on observations of Columnaris disease in grass carp, the maximum acceptable level of AFB1 in the diet was 3110 grams per kilogram.
The presence of copper contamination could potentially hinder collagen synthesis in fish. To investigate this hypothesis, the economically important fish, silver pomfret (Pampus argenteus), underwent exposure to three differing copper (Cu2+) concentrations for up to 21 days, simulating natural copper exposure. Prolonged and escalating copper exposure resulted in widespread vacuolization, cell death, and tissue disintegration, evident in hematoxylin and eosin, and picrosirius red staining, with altered collagen types and abnormal accumulations observed in liver, intestinal, and muscular tissues. In order to deepen the study of copper-related collagen metabolism disorders, we cloned and studied the key collagen metabolism regulatory gene, timp, from silver pomfret. A full-length timp2b cDNA sequence of 1035 base pairs included an open reading frame of 663 base pairs, which codes for a protein consisting of 220 amino acids. Copper treatment demonstrably elevated the expression levels of AKTS, ERKs, and FGFR genes, while simultaneously lowering the mRNA and protein expression levels of Timp2b and MMPs. In conclusion, a silver pomfret muscle cell line (PaM) was first developed, subsequently used with PaM Cu2+ exposure models (450 µM Cu2+ for 9 hours) to explore the regulatory role of the timp2b-mmps system. In the model, manipulating timp2b levels via RNA interference (timp2b-) or overexpression (timp2b+), we discovered that downregulation of MMPs and upregulation of AKT/ERK/FGF were worsened in the timp2b- group, while the timp2b+ group experienced some amelioration. The results suggest long-term copper exposure in fish can lead to tissue damage and altered collagen metabolism, which could be triggered by changes in AKT/ERK/FGF expression, affecting the TIMP2B-MMPs system's impact on the balance of the extracellular matrix. This research explored the interplay between copper and fish collagen, revealing its regulatory mechanisms, ultimately contributing to a deeper understanding of copper pollution's toxicity.
A crucial factor for selecting sensible lake pollution reduction technologies originating within the lake is a complete and scientific assessment of the benthic ecosystem's health. Current assessments, although relying on biological indicators, are insufficient in capturing the nuances of benthic ecosystems, encompassing factors like eutrophication and heavy metal contamination, which can potentially lead to one-sided evaluation results. In the North China Plain, Baiyangdian Lake, the largest shallow mesotrophic-eutrophic lake, was examined in this study, which used a combined approach of chemical assessment index and biological integrity index to assess its biological condition, trophic state, and heavy metal contamination. The indicator system's design incorporated three biological assessments—the benthic index of biotic integrity (B-IBI), the submerged aquatic vegetation index of biological integrity (SAV-IBI), and the microbial index of biological integrity (M-IBI)—and three chemical assessments, including dissolved oxygen (DO), the comprehensive trophic level index (TLI), and the index of geoaccumulation (Igeo). A filtering process, incorporating range, responsiveness, and redundancy tests, was employed on 23 B-IBI, 14 SAV-IBI, and 12 M-IBI attributes, prioritizing core metrics exhibiting strong correlations with disturbance gradients or excellent discriminatory power between impaired and reference sites. Significant discrepancies were found in the assessment outcomes for B-IBI, SAV-IBI, and M-IBI regarding their reactions to human activities and seasonal fluctuations, particularly prominent seasonal variations within the submerged plant communities. A conclusive assessment of the benthic ecosystem's health status is difficult to achieve when relying solely on data from a single biological community. The score of chemical indicators, when measured against biological indicators, is comparatively lower. DO, TLI, and Igeo measurements are indispensable supplements to benthic ecosystem health assessments in lakes exhibiting both eutrophication and heavy metal contamination. read more The benthic ecosystem health of Baiyangdian Lake, evaluated using a new integrated assessment, was found to be fair, yet the northern section adjoining the Fu River's inflow displayed a poor condition, signifying anthropogenic stress, leading to eutrophication, heavy metal contamination, and impairment of the biological community.