National Engineering Research Center of Marine Facilities Aquaculture, Zhejiang Ocean University, Zhoushan 316022, PR China.
Postgraduate Work Department, Zhejiang Ocean University, Zhoushan 316022, PR China.
Fish Shellfish Immunol. 2018 Jan;72:1-8. doi: 10.1016/j.fsi.2017.09.077. Epub 2017 Oct 24.
Zebrafish were exposed to 0, 2.5 and 5 μg/L cadmium (Cd) for 10 weeks, and then each group was exposed to 26 °C(control) and 32 °C (high temperature) for 7 days. 22 indicators were compared between 26 °C and 32 °C in the spleen, including body weight, LPO and NO levels, activity levels of Cu/Zn-SOD, CAT and iNOS, MTs protein levels, and mRNA levels of Nrf2, Cu/Zn-SOD, CAT, HSF1, HSF2, HSP70, MTF-1, MTs, IL-6, IL-10, IL-1β, TNF-α, iNOS and NF-κB. Most indicators were not significantly affected by heat in fish from no Cd pollution. However, almost all of indicators were responsive to heat in fish pre-exposed to Cd. Several indicators were sensitive to heat in fish pre-exposed to 2.5 μg/L Cd such as iNOS activities, and mRNA levels of iNOS and IL-10. Most other indicators were sensitive to heat in fish pre-exposed to 5 μg/L. The mRNA levels of HSP70 and MTF-1 were up-regulated by heat in fish pre-exposed to 0, 2.5 and 5 μg/L Cd. However, the magnitude of increase was the greatest in fish pre-exposed to 5 μg/L Cd. These differences between control and high temperature would serve as biomarkers to distinguish healthy from Cd-polluted group. The findings imply that metal pollution history should be carefully considered when screening heat biomarkers in fish.
斑马鱼在暴露于 0、2.5 和 5μg/L 镉(Cd)10 周后,分别暴露于 26°C(对照)和 32°C(高温)7 天。在脾脏中比较了 26°C 和 32°C 之间的 22 个指标,包括体重、LPO 和 NO 水平、Cu/Zn-SOD、CAT 和 iNOS 的活性水平、MTs 蛋白水平、Nrf2、Cu/Zn-SOD、CAT、HSF1、HSF2、HSP70、MTF-1、MTs、IL-6、IL-10、IL-1β、TNF-α、iNOS 和 NF-κB 的 mRNA 水平。在无镉污染的鱼类中,大多数指标不受高温的影响。然而,在预先暴露于 Cd 的鱼类中,几乎所有指标都对高温有反应。一些指标在预先暴露于 2.5μg/L Cd 的鱼类中对高温敏感,如 iNOS 活性和 iNOS 和 IL-10 的 mRNA 水平。其他大多数指标在预先暴露于 5μg/L Cd 的鱼类中对高温敏感。在预先暴露于 0、2.5 和 5μg/L Cd 的鱼类中,HSP70 和 MTF-1 的 mRNA 水平受热上调。然而,在预先暴露于 5μg/L Cd 的鱼类中,增加的幅度最大。这些在对照和高温之间的差异将作为生物标志物,用于区分健康和镉污染组。这些发现表明,在筛选鱼类中的热生物标志物时,应仔细考虑金属污染史。