生物多样性 ›› 2025, Vol. 33 ›› Issue (4): 24208. DOI: 10.17520/biods.2024208
张明燡1,2,3, 王晓梅1,2,3,4*, 郑言鑫1,2,3, 吴楠1,2,3,5, 李东浩4,6, 樊恩源6, 李娜7, 单秀娟7, 于涛1,2,3, 赵春暖1,2,3, 李波1,2,3, 徐帅1,2,3, 吴玉萍1,2,3, 任利群1,2,3
Mingyi Zhang1,2,3, Xiaomei Wang1,2,3,4*, Yanxin Zheng1,2,3, Nan Wu1,2,3,5, Donghao Li4,6, Enyuan Fan6, Na Li7, Xiujuan Shan7, Tao Yu1.2.3, Chunnuan Zhao1,2,3, Bo Li1,2,3, Shuai Xu1,2,3, Yuping Wu1,2,3, Liqun Ren1,2,3
1 Changdao Enhancement and Experiment Station, Chinese Academy of Fishery Sciences, Yantai, Shandong, 265800, China
2 Engineering Technology Research Center of Shellfish and Algae Breeding, Chinese Academy of Fishery Sciences, Yantai, Shandong, 265800, China
3 Island and Reef Fisheries Research Center, Chinese Academy of Fishery Sciences, Yantai, Shandong, 265800, China
4 Chinese Academy of Fishery Sciences, Beijing, 100141, China
5 School of Fisheries, Ludong University, Yantai, Shandong, 264039, China
6 China Astronautics Standards Institute, Beijing, 100141, China
7 Yellow Sea Fisheries Research Institute, Chinese Academy of Fishery Sciences, Qingdao, Shandong, 266071, China
摘要: 受人类活动等因素影响, 黄河口牡蛎礁生态系统退化严重。本文选取该区域典型牡蛎礁分布区, 就牡蛎资源、浮游藻类、浮游动物及底栖动物开展调查, 了解不同分布区牡蛎种类组成、生长特征、环境状况, 分析牡蛎礁生态功能。调查结果显示, 在黄河口各牡蛎礁分布区, KL1 (平均壳高6.16 ± 1.63 mm)和KL2 (4.70 ± 6.86 mm)基本均为幼体;WD (平均壳高45.69 ± 22.41 mm)多为成体牡蛎, HK (平均壳高19.68 ± 13.64 mm)牡蛎数量最多;共采集牡蛎样本147个, 种类以长牡蛎(Crassostrea gigas)、近江牡蛎(Crassostrea ariakensis)为主。浮游藻类共采集3门36种, 浮游动物共采集到4门12种, 底栖动物共采集5门84种, 有礁区甲壳动物优势种显著高于无礁区(P<0.05), 丰度生物量曲线统计量W值有礁区(-0.144)>无礁区(-0.207), 有礁区底栖动物群落结构受扰动程度低于无礁区。研究表明, 与其他区域相比, 黄河口牡蛎资源量整体偏低, 不同区域牡蛎资源量和分布特点不同, 黄河口底栖动物群落结构已受环境和人类活动影响, 牡蛎礁降低底栖动物受干扰程度, 发挥维护生物群落结构稳定的作用。因此, 建议在黄河口根据不同区域牡蛎资源现状, 因地制宜开展科学修复, 通过栖息地功能重建, 促进黄河口区域生态环境恢复, 同时加强宣传, 减少人为破坏和干扰。