Laboratory of Marine Biology and Ecology, Third Institute of Oceanography, Ministry of Natural Resources, Xiamen, 361005, China; Field Station of Coastal Wetland Ecosystem Research and Observation in Beibu Bay, Ministry of Natural Resources, Beihai, 536015, China.
Laboratory of Marine Biology and Ecology, Third Institute of Oceanography, Ministry of Natural Resources, Xiamen, 361005, China.
Ecotoxicol Environ Saf. 2020 Apr 1;192:110271. doi: 10.1016/j.ecoenv.2020.110271. Epub 2020 Feb 7.
Pollution with total petroleum hydrocarbons (TPHs) is a global concern and particularly in coastal environments. Polycyclic aromatic hydrocarbons (PAHs) are regarded as the most toxic components of TPHs and they can also be derived from other sources. Fangcheng Port is considered as a representative emerging coastal city in China, but the status, sources, and hazards to organisms and humans with respect to contamination with PAHs and TPHs are unknown in the coastal regions of this area. Therefore, in this study, we cloned cytochrome P450 family genes (CYP1A1, CYP3A, and CYP4) and heat shock protein 70 gene (HSP70) in the clam Meretrix meretrix as well as optimizing the method for measuring the 7-ethoxyresorufin O-deethylase activity. These molecular indicators and four specific physiological indexes were found to be appropriate biomarkers for indicating the harmful effects of PAHs and TPHs on clams after exposure to the crude oil water-soluble fraction. In field monitoring surveys, we found that the 2- and 3-ring PAHs were dominant in the clams whereas the 4- to 6-ring PAHs were dominant in the sediments at each site. The PAH levels (3.63-12.77 ng/g wet weight) in wild clams were lower, whereas the TPH levels (13.25-70.50 μg/g wet weight) were higher compared with those determined previous in China and elsewhere. The concentrations of PAHs and TPHs in the sediments (19.20-4215.76 ng/g and 3.65-866.40 μg/g dry weight) were moderate compared with those in other global regions. Diagnostic ratio analysis demonstrated that the PAHs were derived mainly from pyrogenic sources. The TPHs may have come primarily from industrial effluents, land and maritime transportation, or fishing activities. The Integrated Biomarker Response version 2 indexes indicated that the clams collected from site S5 exhibited the most harmful effects due to contamination by PAHs and TPHs. Human health risk assessments demonstrated that the risks due to PAHs and TPHs following the consumption of clams can be considered acceptable. Our results suggest that continuous monitoring of contamination by PAHs and TPHs is recommended in this emerging coastal city as well as assessing their human health risks.
多环芳烃(PAHs)被认为是总石油烃(TPHs)中最具毒性的成分,它们也可能来自其他来源。防城港市被认为是中国新兴的沿海城市的代表,但该地区沿海地区的 PAHs 和 TPH 污染状况、来源、对生物和人类的危害尚不清楚。因此,在本研究中,我们克隆了贻贝 Meretrix meretrix 中的细胞色素 P450 家族基因(CYP1A1、CYP3A 和 CYP4)和热休克蛋白 70 基因(HSP70),并优化了 7-乙氧基荧蒽 O-脱乙基酶活性的测定方法。这些分子指标和四个特定的生理指标被发现是指示贻贝暴露于原油水溶性馏分后 PAHs 和 TPH 有害影响的合适生物标志物。在现场监测调查中,我们发现 2 环和 3 环 PAHs 在贻贝中占优势,而 4 环至 6 环 PAHs 在每个地点的沉积物中占优势。与中国和其他地区以前的研究相比,野生贻贝中的 PAH 水平(3.63-12.77ng/g 湿重)较低,而 TPH 水平(13.25-70.50μg/g 湿重)较高。与其他全球地区相比,沉积物中的 PAH 和 TPH 浓度(19.20-4215.76ng/g 和 3.65-866.40μg/g 干重)处于中等水平。诊断比分析表明,PAHs 主要来源于热成因源。TPHs 可能主要来自工业废水、陆地和海上运输或渔业活动。综合生物标志物反应版本 2 指数表明,由于 PAHs 和 TPHs 的污染,S5 站点采集的贻贝表现出最有害的影响。人类健康风险评估表明,食用贻贝后 PAHs 和 TPHs 带来的风险可以被认为是可以接受的。我们的研究结果表明,建议在这个新兴的沿海城市继续监测 PAHs 和 TPHs 的污染情况,并评估其对人类健康的风险。