中文核心期刊华东师范大学学报(自然科学版) ›› 2026, Vol. 2026 ›› Issue (3): 110-123.doi: 10.3969/j.issn.1000-5641.2026.03.009
• 生物多样性与生态响应 • 上一篇
钟鹏权1, 王维2, 张嘉伟1,2, 李徐1, 周子清1, 王苗勋1, 许媛1,3,*(
)
收稿日期:2025-01-15
接受日期:2025-11-02
出版日期:2026-05-25
发布日期:2026-05-27
通讯作者:
许媛
E-mail:yxu@sklec.ecnu.edu.cn
基金资助:
Pengquan ZHONG1, Wei WANG2, Jiawei ZHANG1,2, Xu LI1, Ziqing ZHOU1, Miaoxun WANG1, Yuan XU1,3,*(
)
Received:2025-01-15
Accepted:2025-11-02
Online:2026-05-25
Published:2026-05-27
Contact:
Yuan XU
E-mail:yxu@sklec.ecnu.edu.cn
摘要:
为评价长江口崇明东滩盐沼湿地水滨三棱草生态修复工程对底栖生物群落的影响, 采用主坐标分析 (PCoA)、相似性百分比 (SIMPER) 等方法, 对生态修复区与邻近的天然水滨三棱草区底栖纤毛虫群落结构及多样性进行4个季度的对比研究. 结果如下: ① 修复后沉积物中值粒径、有机质含量及铵盐含量显著上升; ② 修复区与天然区的底栖纤毛虫群落物种组成存在显著差异; 盐度、磷酸盐含量、pH、氧化还原电位及小型底栖动物生物量是其主要驱动因素; ③ 天然区底栖纤毛虫群落α多样性显著高于修复区; 盐度、沉积物粒径、硅酸盐、铵盐及有机质含量是其多样性的主要驱动因素. 综上, 修复区的纤毛虫群落组成仍与天然区存在显著差异, 其多样性显著低于天然区, 或需要更长时间才能恢复.
中图分类号:
钟鹏权, 王维, 张嘉伟, 李徐, 周子清, 王苗勋, 许媛. 长江口滨海湿地生态修复工程对底栖纤毛虫群落的影响[J]. 华东师范大学学报(自然科学版), 2026, 2026(3): 110-123.
Pengquan ZHONG, Wei WANG, Jiawei ZHANG, Xu LI, Ziqing ZHOU, Miaoxun WANG, Yuan XU. Effects of the ecological restoration project in the coastal wetlands of the Yangtze River Estuary on benthic ciliate communities[J]. J* E* C* N* U* N* S*, 2026, 2026(3): 110-123.
表1
崇明东滩环境因子的单位、平均值、标准偏差和范围"
| 区域 | 盐度/‰ | SED/μm | TOC/% | TN/% | ORP/mV | |||||||||
| 平均值± 标准差 | 范围 | 平均值± 标准差 | 范围 | 平均值± 标准差 | 范围 | 平均值± 标准差 | 范围 | 平均值± 标准差 | 范围 | |||||
| 修复区 | 13±6 | 5~23 | 18.34±9.18 | 5.09~34.85 | 0.75±0.40 | 0.14~1.39 | 0.10±0.05 | 0.03~0.20 | 406.64±67.80 | 203.70~534.00 | ||||
| 天然区 | 3±5 | 0~13 | 43.01±8.36 | 24.16~53.53 | 0.12±0.08 | 0.07~0.41 | 0.03±0.01 | 0.02~0.06 | 430.02±66.58 | 306.30~593.80 | ||||
| 区域 | pH | Chl a/(μg/g) | BA/(109 ind/mL) | MEB/(μg C/mL) | NH4+/(μmol/L) | |||||||||
| 平均值± 标准差 | 范围 | 平均值± 标准差 | 范围 | 平均值± 标准差 | 范围 | 平均值± 标准差 | 范围 | 平均值± 标准差 | 范围 | |||||
| 修复区 | 7.88±0.45 | 7.05~9.07 | 5.33±2.27 | 1.23~10.52 | 1.65±0.75 | 0.49~3.35 | 51.48±28.6 | 9.48~157.56 | 28.36±31.57 | 2.95~144.75 | ||||
| 天然区 | 8.32±0.60 | 7.45~9.45 | 3.76±1.95 | 0.92~7.40 | 1.75±0.81 | 0.40~3.60 | 40.59±25.11 | 13.55~136.63 | 3.23±2.65 | 0.02~10.30 | ||||
| 区域 | NO3–/(μmol/L) | NO2–/(μmol/L) | PO43–/(μmol/L) | SiO32–/(μmol/L) | ||||||||||
| 平均值± 标准差 | 范围 | 平均值± 标准差 | 范围 | 平均值± 标准差 | 范围 | 平均值± 标准差 | 范围 | |||||||
| 修复区 | 10.16±14.19 | 0.13~42.06 | 0.96±1.24 | 0.05~4.85 | 1.48±1.53 | 0.20~9.37 | 68.63±37.08 | 2.40~121.02 | ||||||
| 天然区 | 40.74±33.32 | 0.32~86.05 | 0.86±0.67 | 0.04~2.24 | 0.92±0.44 | 0.38~1.80 | 91.98±42.61 | 40.79~150.82 | ||||||
表3
底栖纤毛虫群落优势种组合"
| 类型 | 样点 | 优势物种组合 |
| 修复区 | R1 | 阿克洛裸口虫(Holophrya aklitolophon) (45.12%), 苏珊娜甲吸管虫(Loricophrya susannae) (19.74%), 卡佩裸口虫(Holophrya caspica) (9.79%) |
| R2 | 苏珊娜甲吸管虫 (25.79%), 阿克洛裸口虫 (23.21%), 卡佩裸口虫 (10.73%), 福摩萨吸管虫(Thecacineta fumosae) (8.26%), 细小哈特曼虫(Hartmannula angustipilosa) (5.93%) | |
| 天然区 | N | 阿克洛裸口虫 (13.85%), 马里兰伪膜袋虫(Pseudocyclidium marylandi) (12.58%), 食藻伪斜管虫(Pseudochilodonopsis algivora) (10.31%), 食藻裸口虫(Holophrya alviolata) (9.67%), 卡佩裸口虫 (7.37%), 盐扁丝虫(Platynematum salinarum) (6.76%), 波戈漫游虫(Litonotus bergeri) (5.65%) |
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