Publications by authors named "Jia-Zhang Chen"

Microorganisms are sensitive to changes in the external environment and are often used as indicators to monitor and reflect water quality. Using Illumina MiSeq sequencing, the characteristics of the microbial community in Shihou Lake water at different time points were analyzed and the key environmental factors affecting the bacterial community were identified. The microbial community diversity in Shihou Lake water was rich and showed significant differences over time.

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Tilapia were exposed to 0, 0.2, 2, 20, 200 µg/L methomyl for 30 days, and then transferred to methomyl-free water for 18 days. Caspase-8 in serum, apoptosis rate, microstructure and ultra-microstructure of testis were checked after methomyl exposure and at 18 days after transferring to methomyl-free water.

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Tilapia were exposed to sub-lethal concentrations of 0, 0.2, 2, 20 or 200 μg/L for 30 days, then transferred to methomyl-free water for 18 days. E , T, 11-KTand VTG in serum were examined.

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Tilapia were exposed to sublethal methomyl concentrations of 0, 0.2, 2, 20 or 200 μg/L for 30 days, and then transferred to methomyl-free water for 18 days. The sexual steroid hormones 17β-estradiol (E2), testosterone (T), and 11-ketotestosterone (11-KT) in tilapia testes were examined at 0, 6, 12, 18, 24 and 30 days after methomyl exposure, and at 18 days after fish were transferred to methomyl-free water.

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Article Synopsis
  • At low concentrations (0.2 and 2 μg/L), there were no significant changes in gene expression linked to their endocrine system, while higher concentrations (20 and 200 μg/L) caused notable disruptions in hormone-related genes, leading to reproductive issues.
  • Recovery tests indicated that the harmful effects from 20 μg/L of methomyl were reversible, but those from 200 μg/L resulted in irreversible endocrine disruption in male tilapia.
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The changes of microbial community in aquaculture systems under the effects of stocking densities and seasonality were investigated in tilapia ponds. Total DNAs were extracted from the water samples, 16S rRNA gene was amplified and the bacterial community analyzed by Illumina high-throughput sequencing obtaining 3486 OTUs, from a total read of 715,842 sequences. Basing on the analysis of bacterial compositions, richness, diversity, bacterial 16S rRNA gene abundance, water sample comparisons and existence of specific bacterial taxa within three fish ponds in a 4 months period, the study conclusively observed that the dominant phylum in all water samples were similar, and they included; Proteobacteria, Cyanobacteria, Bacteroidetes, Actinobacteria, Planctomycetes and Chlorobi, distributed in different proportions in the different months and ponds.

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  • The study researched how the antioxidant enzymes superoxide dismutase (SOD) and catalase (CAT) in Nile tilapia respond to exposure to different concentrations of the pesticide methomyl over 30 days.
  • Results indicated that SOD and CAT activities were significantly impacted at higher methomyl concentrations (2, 20, and 200 μg/L), while the lowest concentration (0.2 μg/L) did not show a significant effect, suggesting it might be a safe level.
  • After transferring the fish to methomyl-free water, SOD recovery was only observed at the lower concentration (2 μg/L), while CAT effects were reversible across all tested concentrations, indicating that CAT is more resilient to
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The chronic effect of methomyl on the antioxidant system in tilapia (Oreochromis niloticus) was investigated. Fish were exposed to sub-lethal concentrations of 0.2, 2, 20 and 200μgL(-1) for 30 days, and then transferred to methomyl-free water for 18 days.

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Tilapia were exposed to sublethal concentrations of 0, 0.2, 2, 20, or 200 μg/L for 30 days, and then transferred to methomyl-free water for 18 days. GST, GPx, GR, GSH, and GSSG in tilapia serum were examined at 0, 6, 12, 18, 24, and 30 days after methomyl exposure and at 18 days after transferring to methomyl-free water.

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Article Synopsis
  • Tilapia were exposed to varying concentrations of methomyl (0, 0.2, 2, 20, or 200 μg/L) for 30 days, followed by a recovery period of 18 days in clean water, to study the impact on renal antioxidants.
  • Exposure to 0.2 μg/L did not show significant effects, indicating it as a no-observed-adverse-effect level (NOAEL), while higher levels (2, 20, 200 μg/L) led to increased oxidative stress markers such as SOD, CAT, and GST.
  • Recovery from oxidative damage was observed at 20 μg/L, but the effects of the highest concentration (200 μg
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