National Agricultural Scientific Observing and Experimental Station for Fisheries Resources and Environment, Guangzhou, Scientific Observing and Experimental Station of Fishery Resources and Environment in the Middle and Lower Reaches of Pearl River, Key Laboratory of Prevention and Control for Aquatic Invasive Alien Species, Fishery Ecological Environment Monitoring Center of Pearl River Basin, Ministry of Agriculture and Rural Affairs, Guangdong Provincial Key Laboratory of Aquatic Animal Immunology and Sustainable Aquaculture, Pearl River Fisheries Research Institute, Chinese Academy of Fishery Sciences, Guangzhou 510380, China.
Chinese Academy of Inspection and Quarantine Greater Bay Area, Zhongshan 528437, China.
Sci Total Environ. 2024 Jun 15;929:172362. doi: 10.1016/j.scitotenv.2024.172362. Epub 2024 Apr 20.
Pollution-induced declines in fishery resources restrict the sustainable development of fishery. As a kind of typical environmental pollutant, the mechanism of polycyclic aromatic hydrocarbons (PAHs) facilitating fishery resources declines needs to be fully illustrated. To determine how PAHs have led to declines in fishery resources, a systematic toxicologic analysis of the effects of PAHs on aquatic organisms via food-web bioaccumulation was performed in the Pearl River and its estuary. Overall, PAH bioaccumulation in aquatic organisms was correlated with the trophic levels along food-web, exhibiting as significant positive correlations were observed between PAHs concentration and the trophic levels of fishes in the Pearl River Estuary. Additionally, waterborne PAHs exerted significant direct effects on dietary organisms (P < 0.05), and diet-borne PAHs subsequently exhibited significant direct effects on fish (P < 0.05). However, an apparent block effect was found in dietary organisms (e.g., zooplankton) where 33.49 % of the total system throughput (TST) was retained at trophic level II, exhibiting as the highest PAHs concentration, bioaccumulation factor (BAF), and biomagnification factor (BMF) of ∑PAHs in zooplankton were at least eight-fold greater than those in fishes in both the Pearl River and its estuary, thereby waterborne PAHs exerted either direct or indirect effects on fishes that ultimately led to food-web simplification. Regardless of the block effect of dietary organisms, a general toxic effect of PAHs on aquatic organisms was observed, e.g., Phe and BaP exerted lethal effects on phytoplankton Chlorella pyrenoidosa and zooplankton Daphnia magna, and decreased reproduction in fishes Danio rerio and Megalobrama hoffmanni via activating the NOD-like receptors (NLRs) signaling pathway. Consequently, an assembled aggregate exposure pathway for PAHs revealed that increases in waterborne PAHs led to bioaccumulation of PAHs in aquatic organisms along food-web, and this in turn decreased the reproductive ability of fishes, thus causing decline in fishery resources.
污染导致渔业资源减少,限制了渔业的可持续发展。多环芳烃 (PAHs) 作为一种典型的环境污染物,其促进渔业资源减少的机制需要充分说明。为了确定 PAHs 如何导致渔业资源减少,对珠江及其河口通过食物网生物积累对水生生物的 PAHs 影响进行了系统的毒理学分析。总的来说,水生生物中 PAH 的生物积累与食物网中的营养级有关,珠江河口鱼类的 PAH 浓度与营养级呈显著正相关。此外,水相 PAHs 对摄食生物有显著的直接影响(P<0.05),饮食来源的 PAHs 随后对鱼类有显著的直接影响(P<0.05)。然而,在摄食生物(如浮游动物)中发现了明显的阻断效应,其中 33.49%的总系统通量(TST)在营养级 II 中保留,表现为浮游动物中∑PAHs 的浓度、生物积累因子(BAF)和生物放大因子(BMF)至少比珠江及其河口鱼类高 8 倍,从而水相 PAHs 对鱼类产生了直接或间接的影响,最终导致食物网简化。无论摄食生物的阻断效应如何,都观察到 PAHs 对水生生物的一般毒性作用,例如,Phe 和 BaP 对浮游植物蛋白核小球藻和浮游动物大型溞都有致死作用,并且通过激活 NOD 样受体(NLRs)信号通路,降低鱼类斑马鱼和鳙鱼的繁殖能力。因此,PAHs 的综合暴露途径表明,水相 PAHs 的增加导致了沿食物网在水生生物中 PAHs 的生物积累,这反过来又降低了鱼类的繁殖能力,从而导致渔业资源减少。