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海南省三亚市红树林湿地海洋线虫群落特征及其影响因子

杨幼晨 张德梅 慕芳红 华尔

杨幼晨,张德梅,慕芳红,等. 海南省三亚市红树林湿地海洋线虫群落特征及其影响因子[J]. 海洋学报,2024,46(11):91–105 doi: 10.12284/hyxb2024118
引用本文: 杨幼晨,张德梅,慕芳红,等. 海南省三亚市红树林湿地海洋线虫群落特征及其影响因子[J]. 海洋学报,2024,46(11):91–105 doi: 10.12284/hyxb2024118
Yang Youchen,Zhang Demei,Mu Fanghong, et al. Characteristics and their influencing factors of marine nematode communities in mangrove wetlands of Sanya City, Hainan Province[J]. Haiyang Xuebao,2024, 46(11):91–105 doi: 10.12284/hyxb2024118
Citation: Yang Youchen,Zhang Demei,Mu Fanghong, et al. Characteristics and their influencing factors of marine nematode communities in mangrove wetlands of Sanya City, Hainan Province[J]. Haiyang Xuebao,2024, 46(11):91–105 doi: 10.12284/hyxb2024118

海南省三亚市红树林湿地海洋线虫群落特征及其影响因子

doi: 10.12284/hyxb2024118
基金项目: 国家自然科学基金(41976100)。
详细信息
    作者简介:

    杨幼晨(2000— ),女,河南省南阳市人,研究方向为底栖生态学。E-mail:21220613002@stu.ouc.edu.cn

    通讯作者:

    华尔,副教授,主要从事底栖生态学研究。E-mail:huaer@ouc.edu.cn

  • 中图分类号: Q178.53

Characteristics and their influencing factors of marine nematode communities in mangrove wetlands of Sanya City, Hainan Province

  • 摘要: 本研究于2020年11月在海南亚龙湾青梅港红树林自然保护区和三亚河红树林自然保护区采集沉积物样品,开展了海洋线虫的群落特征及影响因子研究。研究结果显示,青梅港红树林海洋线虫平均丰度为(80.4 ± 40.3) ind./cm2,三亚河红树林的为(96.7 ± 55.6) ind./cm2,两处红树林湿地海洋线虫平均丰度为(88.5 ± 47.1) ind./cm2,海洋线虫丰度在两红树林湿地间存在显著差异。共鉴定海洋线虫77种,隶属于56属,21科7目。青梅港红树林的优势属为新色矛线虫属(Neochromadora)、微口线虫属(Terschellingia)、拟单宫线虫属(Paramonohystera)、吞咽线虫属(Daptonema)、链环线虫属(Desmodora),以刮食性线虫为优势摄食类型;三亚河红树林的优势属为微口线虫属(Terschellingia)、萨巴线虫属(Sabatieria)、游咽线虫属(Eleutherolaimus)、拟齿线虫属(Parodontophora)和折咽线虫属(Ptycholaimellus),以选择性沉积食性线虫为主;两红树林湿地共同的优势属为微口线虫属。海洋线虫群落结构在两红树林均具空间差异,海洋线虫群落在两红树林之间分化,但差异并不显著。沉积物有机质含量和脱镁叶绿酸含量是影响三亚河红树林海洋线虫丰度和群落结构的重要因素;红树植被类型的差异可能在一定程度上对青梅港红树林海洋线虫的丰度及群落结构产生影响;沉积物粒度特征、海水pH值和盐度等的差异可解释两处红树林选定站点海洋线虫群落的分化。此外,青梅港红树林存在污水工程、港口建设和旅游业的发展,三亚河红树林存在人为砍伐、筑堤、盐田开辟、养虾池废水排放,两地存在的不同污染也可能是导致红树林海洋线虫群落分化的原因。
  • 图  1  研究区域采样站点

    Fig.  1  Sampling sites of the study area

    图  2  研究站点环境因子主成分分析(PCA)

    Fig.  2  Principal component analysis (PCA) result of environmental factors in the study sites

    图  3  两个红树林湿地海洋线虫的垂直分布

    Fig.  3  Vertical distribution of marine nematodes in the two mangrove wetlands

    图  4  两个红树林湿地海洋线虫群落的非度量多维度分析

    Fig.  4  Metric multidimensional scaling plot of marine nematode communities in the two mangrove wetlands

    图  5  两个红树林湿地海洋线虫的摄食类型组成

    Fig.  5  Proportion of feeding types of marine nematodes in the two mangrove wetlands

    表  1  研究站点环境因子

    Tab.  1  Environmental factors of study sites

    研究区域 采样点 pH DO/
    (mg∙L−1)
    T/℃ S σi Md/μm OM/% Chl-a/
    (μg∙g−1)
    Pheo-a/
    (μg∙g−1)
    TY/% Tannin/
    (mg∙g−1)
    青梅港 Q1 7.87 5.37 28.38 3.13 1.30 332.48 2.03 0.29 0.69 1.44 20.41
    Q2 1.32 358.79 0.80 0.99 1.30 0.66 33.70
    Q3 7.91 5.69 28.80 3.88 1.32 426.92 8.38 0.17 0.43 1.63 20.22
    Q4 1.36 360.33 1.64 0.32 0.99 2.01 19.70
    Q5 7.68 5.27 30.04 3.72 2.93 41.49 7.13 0.41 1.75 57.33 21.70
    Q6 1.36 392.35 1.33 0.43 1.45 2.00 20.09
    平均 7.82 5.44 29.07 3.58 1.60 318.73 3.55 0.43 1.10 10.84 22.64
    三亚河 S1 8.21 6.14 26.91 14.12 2.34 119.96 5.86 0.50 1.73 27.08 41.45
    S2 1.12 153.43 3.99 0.79 1.50 23.48 27.70
    S3 1.61 115.76 3.18 0.25 0.76 19.87 20.74
    S4 8.12 5.64 26.81 13.05 2.42 118.27 2.73 0.63 1.98 27.54 23.96
    S5 2.83 100.71 9.52 0.52 2.75 33.42 24.22
    S6 3.08 64.70 9.05 0.86 3.77 49.30 19.06
    平均 8.17 5.89 26.86 13.59 2.23 112.14 5.72 0.59 2.08 30.11 26.19
      注:pH:酸碱度;DO:溶解氧含量;T:温度;S:盐度;σi:分选系数;Md:中值粒径;OM:有机质含量;Chl-a:叶绿素含量;Pheo-a:脱镁叶绿酸含量;TY:粉砂黏土含量;Tannin:单宁含量。
    下载: 导出CSV

    表  2  两个红树林湿地的海洋线虫丰度

    Tab.  2  Abundance of marine nematodes in the two mangrove wetlands

    研究站点 丰度/
    (ind.∙cm−2)
    研究站点 丰度/
    (ind.∙cm−2)
    Q1 61.0 ± 23.2 S1 144.4 ± 39.3
    Q2 125.5 ± 88.1 S2 122.4 ± 92.3
    Q3 74.8 ± 52.2 S3 139.4 ± 73.5
    Q4 134.5 ± 65.4 S4 122.1 ± 72.3
    Q5 42.9 ± 23.8 S5 23.0 ± 23.3
    Q6 43.6 ± 43.3 S6 28.7 ± 23.9
    平均 80.4 ± 40.3 平均 96.7 ± 55.6
    下载: 导出CSV

    表  3  两个红树林湿地的海洋线虫优势属(优势度≥5%)

    Tab.  3  Dominant genera of marine nematodes in the two mangrove wetlands (dominance ≥5%)

    青梅港 属名 Q1 Q2 Q3 Q4 Q5 Q6
    Basiria 22.42% 6.90%
    Daptonema 5.76% 20.33% 28.93% 8.72%
    Desmodora 5.02% 30.30% 8.52%
    Haliplectus 9.09%
    Linhomoeus 22.55%
    Neochromadora 43.89% 30.67% 23.94% 15.95% 22.44%
    Paracanthonchus 26.36%
    Paracyatholaimus 10.48% 5.76%
    Paramonohystera 22.27% 13.57% 8.85%
    Sabatieria 7.55%
    Terschellingia 71.74% 18.71% 52.20% 19.93%
    Trissonchulus 5.21%
    Viscosia 6.55%
    三亚河 属名 S1 S2 S3 S4 S5 S6
    Chromadorella 5.49%
    Daptonema 7.40% 5.05% 6.25% 10.99%
    Eleutherolaimus 6.40% 13.01% 8.87% 7.05%
    Haliplectus 6.25%
    Metadesmolaimus 8.40% 5.00%
    Oxystomina 6.25% 7.69%
    Parodontophora 6.08% 8.94% 7.15% 6.33%
    Ptycholaimellus 10.69% 7.31% 5.45%
    Sabatieria 10.23% 13.82% 11.57% 14.33% 11.41%
    Southerniella 15.00%
    Terschellingia 42.00% 33.06% 38.67% 72.21% 50.00% 13.19% 44.71%
    Theristus 7.50%
    Trissonchulus 26.37%
    下载: 导出CSV

    表  4  两个红树林湿地的海洋线虫优势种(优势度≥5%)

    Tab.  4  Dominant species of marine nematodes in the two mangrove wetlands (dominance ≥5%)

    青梅港 种名 Q1 Q2 Q3 Q4 Q5 Q6
    Basiria sp. 22.42% 6.90%
    Daptonema sp.1 5.02% 7.54% 13.21% 5.05%
    Daptonema sp.2 6.01% 10.69%
    Daptonema sp.5 6.54%
    Desmodora sp.1 28.07% 7.63%
    Haliplectus sp.1 9.09%
    Linhomoeus sp. 22.55%
    Neochromadora sp.1 43.89% 28.81% 23.94% 15.95% 22.03%
    Paracanthonchus sp. 26.36%
    Paracyatholaimus sp.1 6.99%
    Paramonohystera sp. 22.27% 13.57% 8.87%
    Sabatieria sp.1 7.55%
    T. longicaudata 45.84% 22.55% 42.77% 14.18%
    Terschellingia sp.2 25.90% 9.43% 5.78%
    Viscosia sp.1 6.55%
    三亚河 种名 S1 S2 S3 S4 S5 S6
    Chromadorella sp. 5.49%
    Daptonema sp.1 5.25% 5.49%
    Eleutherolaimus sp.1 6.40% 25.20% 8.87% 7.05%
    Haliplectus sp.2 5.00%
    Metadesmolaimus sp. 8.40% 5.00%
    Oxystomina sp. 6.25% 7.69%
    Parodontophora sp. 6.08% 8.94% 7.15% 6.33%
    Ptycholaimellus sp.2 7.34% 5.21%
    Sabatieria sp.1 10.23% 25.20% 11.57% 69.11% 11.37%
    Southerniella sp. 15.00%
    T. longicaudata 38.36% 25.20% 33.46% 69.11% 46.25% 12.09% 40.09%
    Terschellingia sp.2 7.05%
    Theristus sp.1 7.50%
    Trissonchulus sp.1 6.59%
    Trissonchulus sp.2 19.78%
    下载: 导出CSV

    表  5  海洋线虫丰度与环境因子的相关性分析结果

    Tab.  5  Results of correlation analysis between abundance of marine nematodes and environmental factors

    站点 σi Md OM Chl-a Pheo-a TY Tannin
    青梅港 −0.511 0.449 −0.366 0.371 −0.347 −0.52 0.466
    三亚河 −0.727 0.729 −0.912* −0.352 −0.851* −0.795 0.452
    两个红树林湿地的代表站点 0.294 −0.565 0.434 0.097 −0.233 0.46 0.408
      注:*表示在0.05水平(双侧)上显著相关。σi:分选系数;Md:中值粒径;OM:有机质含量;Chl-a:叶绿素含量;Pheo-a:脱镁叶绿酸含量;TY:粉砂黏土含量;Tannin:单宁含量。
    下载: 导出CSV

    表  6  海洋线虫群落结构DistLM检验结果

    Tab.  6  Results of the DIistLM sequential test for marine nematode community structure

    环境变量 校准R2 均方 F p Prop Cumul
    青梅港 OM 0.015004 2318.4 0.92609 0.443 0.188 0.188
    Md 0.013858 2717 1.1171 0.343 0.22032 0.40831
    TY 0.19255 3313.7 1.6639 0.277 0.26871 0.67702
    三亚河 Pheo-a 0.30297 4152.6 3.1733 0.011* 0.44237 0.44237
    OM 0.45797 2181.6 2.1438 0.116 0.23241 0.67478
    TY 0.6141 1603.9 2.2137 0.180 0.17086 0.84564
    σi 0.65706 805.18 1.2506 0.445 0.085774 0.93141
    青梅港和三亚河代表站点 TY 0.24332 4773.3 2.6078 0.053 0.39466 0.39466
      注:Prop:解释差异的比例;F:统计量;Cumul:累计比例。统计上显著的相关性用粗体表示。*表示p < 0.05。
    下载: 导出CSV
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  • 收稿日期:  2024-02-24
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