安庆西江长江江豚迁地群体分布格局及影响因子

梁海英, 蔺丹清, 严燕, 陈宇宽, 张四刚, 应聪萍, 王炜祺, 李凡, 刘凯

梁海英, 蔺丹清, 严燕, 陈宇宽, 张四刚, 应聪萍, 王炜祺, 李凡, 刘凯. 安庆西江长江江豚迁地群体分布格局及影响因子[J]. 水生生物学报. DOI: 10.7541/2025.2024.0477
引用本文: 梁海英, 蔺丹清, 严燕, 陈宇宽, 张四刚, 应聪萍, 王炜祺, 李凡, 刘凯. 安庆西江长江江豚迁地群体分布格局及影响因子[J]. 水生生物学报. DOI: 10.7541/2025.2024.0477
LIANG Hai-Ying, LIN Dan-Qing, YAN Yan, CHEN Yu-Kuan, ZHANG Si-Gang, YING Cong-Ping, WANG Wei-Qi, LI Fan, LIU Kai. EX-SITU POPULATION DISTRIBUTION PATTERN AND KEY INFLUENCING FACTORS OF YANGTZE FINLESS PORPOISE IN THE XIJIANG OXBOW OF ANQING CITY[J]. ACTA HYDROBIOLOGICA SINICA. DOI: 10.7541/2025.2024.0477
Citation: LIANG Hai-Ying, LIN Dan-Qing, YAN Yan, CHEN Yu-Kuan, ZHANG Si-Gang, YING Cong-Ping, WANG Wei-Qi, LI Fan, LIU Kai. EX-SITU POPULATION DISTRIBUTION PATTERN AND KEY INFLUENCING FACTORS OF YANGTZE FINLESS PORPOISE IN THE XIJIANG OXBOW OF ANQING CITY[J]. ACTA HYDROBIOLOGICA SINICA. DOI: 10.7541/2025.2024.0477
梁海英, 蔺丹清, 严燕, 陈宇宽, 张四刚, 应聪萍, 王炜祺, 李凡, 刘凯. 安庆西江长江江豚迁地群体分布格局及影响因子[J]. 水生生物学报. CSTR: 32229.14.SSSWXB.2024.0477
引用本文: 梁海英, 蔺丹清, 严燕, 陈宇宽, 张四刚, 应聪萍, 王炜祺, 李凡, 刘凯. 安庆西江长江江豚迁地群体分布格局及影响因子[J]. 水生生物学报. CSTR: 32229.14.SSSWXB.2024.0477
LIANG Hai-Ying, LIN Dan-Qing, YAN Yan, CHEN Yu-Kuan, ZHANG Si-Gang, YING Cong-Ping, WANG Wei-Qi, LI Fan, LIU Kai. EX-SITU POPULATION DISTRIBUTION PATTERN AND KEY INFLUENCING FACTORS OF YANGTZE FINLESS PORPOISE IN THE XIJIANG OXBOW OF ANQING CITY[J]. ACTA HYDROBIOLOGICA SINICA. CSTR: 32229.14.SSSWXB.2024.0477
Citation: LIANG Hai-Ying, LIN Dan-Qing, YAN Yan, CHEN Yu-Kuan, ZHANG Si-Gang, YING Cong-Ping, WANG Wei-Qi, LI Fan, LIU Kai. EX-SITU POPULATION DISTRIBUTION PATTERN AND KEY INFLUENCING FACTORS OF YANGTZE FINLESS PORPOISE IN THE XIJIANG OXBOW OF ANQING CITY[J]. ACTA HYDROBIOLOGICA SINICA. CSTR: 32229.14.SSSWXB.2024.0477

安庆西江长江江豚迁地群体分布格局及影响因子

基金项目: 国家重点研发计划(2022YFF1301604); 中国水产科学研究院中央级公益性科研院所基本科研业务费专项资金(2023TD11); 省级财政项目“安徽省重点水域水生生物资源监测”(2023AHNYNC016XQ)资助
详细信息
    作者简介:

    梁海英(2000—), 女, 硕士研究生; 主要从事水生生态保护方向研究。E-mail: m220150558@st.shou.edu.cn

    通信作者:

    刘凯, E-mail: liuk@ffrc.cn

  • 中图分类号: S932.8

EX-SITU POPULATION DISTRIBUTION PATTERN AND KEY INFLUENCING FACTORS OF YANGTZE FINLESS PORPOISE IN THE XIJIANG OXBOW OF ANQING CITY

Funds: Supported by the National Key R&D Program of China (2022YFF1301604); Central Public-interest Scientific Institution Basal Research Fund, CAFS (2023TD11); Provincial Fiscal-funded Project "Monitoring of Aquatic Biological Resources in Key Water Areas of Anhui Province" (2023AHNYNC016XQ).
    Corresponding author:
  • 摘要:

    为掌握安庆西江长江江豚迁地群体分布格局、活动规律及关键影响因子, 研究综合主动及被动声学技术于2023年开展了覆盖4个季节的周年调查。被动声学调查结果显示, 西江长江江豚活动强度存在明显的时空特征。就不同区段而言, 利用固定式水下高频声音事件记录仪在西江上、中、下段分别记录到127297、56566和58115个长江江豚脉冲串, 表明长江江豚迁地群体在西江上段水域活动强度最高, 中段和下段水域差异不显著(P>0.05)。细分到各个季节, 冬季、春季和秋季均为在上段水域活动强度最高, 长江江豚脉冲串占比依次为55.64%、58.34%和57.15%; 夏季则为下段水域最高, 占比为56.05%; 冬季和秋季均为下段水域活动强度最低, 脉冲串占比依次为17.7%和18.7%; 春季和夏季均为中段活动强度最低, 脉冲串占比依次为17.6%和16.47%。就各季节活动强度而言, 冬季和秋季日均分别记录到3814和2840个长江江豚脉冲串, 春季和夏季日均分别记录到978和1099个脉冲串, 冬季活动强度显著大于春季、夏季和秋季(P<0.05)。主动声学调查结果显示, 秋季鱼类平均密度最高约为598尾/1000 m3; 春季则最低约为55尾/1000 m³, 夏季和秋季鱼类密度显著大于冬季和春季(P<0.05)。空间分析结果显示, 4个季节上段水域均有鱼类集群, 冬季和春季上段水域的鱼类平均密度最高, 夏季和秋季则为中段水域最高。上述研究表明, 西江长江江豚迁地群体对栖息地利用具有显著的时间和空间特征, 鱼类资源分布格局和最大水面宽度是影响长江江豚对西江栖息地利用的主要因子, 迁地群体最偏好整个周年均有鱼类集群的上段水域。研究分析了长江江豚在相对封闭的迁地水域时空分布特征, 可以为长江江豚迁地保护群体科学管护及迁地水域栖息地修复提供技术支持, 亦可为后续新建迁地保护水域提供参考依据。

    Abstract:

    In order to deeply explore the distribution pattern, activity mode, and key influencing factors of the migrating finless porpoises in Xijiang Oxbow, Anqing City, we conducted an annual investigation covering 4seasons in 2023, comprehensively applying active and passive acoustic techniques. The results of the passive acoustic investigation showed that the activity intensity of finless porpoises in Xijiang Oxbow has significant spatiotemporal characteristics. Regarding different sections, using a fixd underwater high-frequency acoustic event recorder, 127297, 56566, and 58115 pulse trains of Yangtze finless porpoise were recorded in the upper, middle and lower sections of the Xijiang Oxbow by using fixed underwater high-frequency acoustic event recorders, indicating that the activity intensity of Yangtze finless porpoise translocation population was the highest in the upper section, and there was no significant difference between the middle and lower sections (P>0.05). Subdivided into each season, the activity intensity of winter, spring, and autumn was the highest in the upper waters, and the proportion of the pulse train of Yangtze finless porpoise was 55.64%, 58.34%, and 57.15%, respectively. In summer, the lower water area was the highest, accounting for 56.05%. In winter and autumn, the activity intensity in the upper water area was the lowest, and the proportion of pulse train was 17.7% and 18.7%, respectively. In spring and summer, the activity intensity in the middle water area was the lowest, and the proportion of pulse train was 17.6% and 16.47%, respectively. In terms of seasonal activity intensity, 3814 and 2840 pulse trains were recorded in winter and autumn, respectively, compared to 978 and 1099 pulse trains in spring and summer. This suggests that the activity intensity in winter was significantly higher than that in spring, summer, and autumn (P<0.05). The results of active acoustic survey showed that the average density of fish was approximately 598 ind /1000 m3 in autumn and 55 ind /1000 m³ in spring, with significantly higher densities in summer and autumn compared to that in winter and spring (P<0.05). The spatial analysis indicated that there were fish clusters in the upper waters across all seasons. The highest average fish density was observed in the upper waters of winter and spring, while that in the middle waters exhibited the highest density in summer and autumn. The above research demonstrate that the habitat utilization of the ex-situ finless porpoise populations in the Xijiang Oxbow has significant temporal and spatial characteristics. The distribution pattern of fish resources and the width of the water surface are the main factors affecting the difference of habitat utilization of the Yangtze River finless porpoise. The ex-situ populations prefer the upper water with fish clusters every year. This study provides valuable insights into the spatiotemporal distribution characteristics of Yangtze finless porpoise in the relatively closed ex-situ waters, which can provide technical support for the scientific management and habitat restoration of translocated conservation groups. Additionally, it serves as a reference for the subsequent establishment of new ex-situ conservation waters in the future.

  • 图  1   西江水域采样点分布图

    Figure  1.   Distribition of sampling points in Xijiang Oxbow

    图  2   T-tag提取的长江江豚脉冲串

    SPL. 声压; TD. 时间差; PI. 脉冲间间隔

    Figure  2.   Pulse signal of Yangtze finless porpoise extracted by T-tag

    SPL. Sound pressure; TD. Time difference; PI. Inter click interval

    图  3   目视考察结果

    Figure  3.   Visual inspection results

    图  4   西江水域长江江豚脉冲串记录数量

    U. 上段河道 Upper section of river; M. 中段河道 Middle section of river; L. 下段河道 Lower section of river

    Figure  4.   Recorded number of Yangtze finless porpoise pulse trains records in Xijiang Oxbow

    图  5   西江长江江豚分布与体长小于20 cm鱼类平均密度关系

    Figure  5.   Relationship between the distribution of finless porpoises in the Xijiang Oxbow and the average density of fish with a body length of less than 20 cm

    图  6   各季节西江鱼类和长江江豚分布格局

    a—d. 冬季、春季、夏季、秋季鱼类分布格局; e—h. 冬季、春季、夏季、秋季长江江豚分布格局

    Figure  6.   Distribution pattern of fish and Yangtze finless porpoise in the Xijiang Oxbow in each season

    a—d. Pattern of fish distribution in winter, spring, summer, and autumn; e—h. Distribution patterns of the Yangtze River finless porpoises in winter, spring, summer, and autumn

    表  1   西江生境参数

    Table  1   Habitat parameters of Xijiang Oxbow

    季节Season 冬Winter 春Spring 夏Summer 秋Autumn F P
    水段River section U M L U M L U M L U M L
    最大水面宽度
    Max width of the water surface (m)
    326 437 300 343 454 290 437 510 445 449 472 399 45.191 0.000***
    平均水面宽度
    Mean width of the water surface (m)
    307 421 252 318 432 265 352 471 318 330 438 299 3.592 0.071*
    水温Temperature (℃) 8.4 8.27 8.28 19.52 19.33 19.77 33.95 31.67 31.78 26.63 26.3 26.28 0.000 1.000
    水深Depth (m) 4 4 6 5 5 7 5 5 7 5 5 7 13.271 0.002***
    河道弯曲率River bend rate 1.07 1.11 1.34 1.07 1.11 1.34 1.07 1.11 1.34 1.07 1.11 1.34 0.000 0.000***
    注: U. 上段河道 Upper section of river; M. 中段河道 Middle section of river; L. 下段河道 Lower section of river; 下同The same applies below
    下载: 导出CSV

    表  2   各段记录脉冲串数量

    Table  2   T-tag records the number of pulse trains

    季节
    Season
    调查时间段
    Investigation
    period
    调查天数
    Investigation
    day
    河段
    River
    section
    脉冲串
    总数量
    Total
    number
    of pulse
    train
    脉冲串
    数量
    Number of
    pulse
    trains (d)
    冬Winter 2023.1.7—
    2023.2.4
    27 U 57302 2122
    M 27451 1017
    L 18233 675
    春Spring 2023.4.12—
    2023.5.22
    30 U 17111 570
    M 5159 172
    L 7057 235
    夏Summer 2023.7.9—
    2023.8.15
    30 U 9054 302
    M 5434 181
    L 18487 616
    秋Autumn 2023.9.22—
    2023.10.19
    27 U 43830 1623
    M 18522 686
    L 14338 531
    下载: 导出CSV

    表  3   目视考察观测到的长江江豚群次、数量、最大群体

    Table  3   Visual inspection of the observrd population, quantity, and the maximum population of Yangtze finless porpoises

    考察季节
    Season
    考察日期
    Data
    长江江豚
    群次
    Number of
    groups
    observed
    目击率
    Encounter rate
    (群次/km)
    长江江豚
    数量
    Number of
    porpoises
    observed
    最大群体
    The maximum
    grop size
    春Spring2023—
    05—17
    121.33254
    秋Autumn2023—
    09—01
    70.7871
    下载: 导出CSV

    附表  S1   西江鱼类资源调查渔获物结果Appendix 1 Fishery resource survey and catch results in Xijiang Oxbow

    目Order 科Famliy种类Species数量Number
    冬季Winter春季Spring夏季Summer秋季Spring
    上段中段下段上段中段下段上段中段下段上段中段下段
    鲱形目Clupeiformes 鳀科Engraulidae短颌鲚Coilia brachygnathus117NANANANANANANANANA
    福建小鳔鮈Microphysogobio fukiensis1NANANANANANANANANANANA
    蒙古鲌Culter mongolicus11128236077421916166
    似鳊Pseudobrama simoni1NANA67671021145111
    棒花鱼Abbottina rivularis1123NANANA2NANANANANA
    光唇蛇鮈Saurogobio gymnocheilus1NANANANANA2NANANANANA
    蛇鮈Saurogobio dabryi3428136NANANANANANA
    Hypophthalmichthys molitrixNANA210581801923197519720
    兴凯鱊Acheilognathus chankaensisNANA1NANANA15174NA21
    贝氏䱗Hemiculter bleekeriNANANA154146382101NANANANA
    达氏鲌Culter dabryiNANANANA112739243516913
    花䱻Hemibarbus maculatusNANANANANA1NANANANANANA
    翘嘴鲌Culter alburnusNANANA12343136511134957
    镇江片唇鮈Platysmacheilus zhenjiangensisNANANA4106NANANANANANA
    Hemiculter leucisculusNANANA5142NANA2NANANA
    草鱼Ctenopharyngodon idellusNANANANANA751731
    Elopichthys bambusaNANANA3142351NA4
    Cyprinus carpioNANANA113NANANANANANA
    麦穗鱼Pseudorasbora parvaNANANA112119933
    飘鱼Pseudolaubuca sinensisNANANA131NANANA327
    团头鲂Megalobrama amblycephalaNANANA4NA24133NA4
    细鳞鲴Xenocypris microlepisNANANA15115715347239
    银鲴Xenocypris argenteaNANANA28411NA21NA
    Aristichthys nobilisNANANA623489752NA314
    圆吻鲴Distoechodon tumirostrisNANANA121NANANANANANA
    Megalobrama mantschuricusNANANANA219511NANA
    Carassius auratusNANANANA11NANA131NA
    银鮈Squalidus argentatusNANANANA3NA2NA3NA74
    Parabramis pekinensisNANANANA23323NANA4
    黑鳍鳈Sarcocheilichthys nigripinnisNANANANA14NANANANANANA
    拟尖头鲌Culter oxycephaloidesNANANA1810NANA3NANANA
    Ochetobius elongatusNANANANANA2NANA1NANANA
    青鱼Mylopharyngodon piceusNANANANA22522NANA3
    红鳍原鲌Cultrichthys erythropterusNANANANA11NANANA9311
    赤眼鳟Squaliobarbus curriculusNANANANANANA2NA21NANA
    中华鳑鲏Rhodeus sinensisNANANANANANA152123NANANA
    寡鳞飘鱼Pseudolaubuca engraulisNANANANANANA9413NANANA
    点纹银鮈Squalidus wolterstorffiNANANANANANANANANA111
    大鳍鱊Acheilognathus macropterusNANANA321NANANA1854
    黄尾鲴Xenocypris davidiNANANANANANANANANANANA2
    亚口鱼科Catostomidae胭脂鱼Myxocyprinus asiaticusNANANANANANANA1NANA4NA
    虾虎鱼目Gobiiformes 虾虎鱼科Gobiidae子陵吻虾虎鱼Rhinogobius giurinusNA1221532654623162041
    合鳃鱼目Synbranchiformes 刺鳅科Mastacembelidae中华刺鳅Sinobdella sinensisNANANA112NANANANANANA
    鲈形目Perciformes 鮨科Serranidae斑鳜Siniperca scherzeriNANANANA1NANANANANANANA
    Siniperca chuatsiNANA1NA641NA2NANANA
    鳢科Channidae乌鳢Channa argusNANANANANANANANANA1NA1
    鲿科Bagridae黄颡鱼Pelteobagrus fulvidracoNANANANANA1NANANANANANA
    长须黄颡鱼Pelteobagrus eupogonNANANANANANA2NANANANANA
    粗唇鮠Leiocassis crassilabrisNANANANANA1NANANANANANA
    注: NA表示此次调查未采集到
    下载: 导出CSV

    表  4   鱼类资源声学调查结果

    Table  4   Acoustic survey of fish resources

    季节Season 冬Winter 春Spring 夏Summer 秋Autumn F P
    最大密度(尾/1000 m3)
    Maximum value (ind./1000 m3)
    733.7 230.98 743.8 978.13
    最小密度(尾/1000 m3)
    Minimum value (ind./1000 m3)
    3.21 3.96 3.12 128.46
    平均密度(尾/1000 m3)
    Mean density (ind./1000 m3) (mean±SE)
    64.82±13.00 54.59±13.83 138.59±29.09 597.94±60.05 67.84 0.000***
    下载: 导出CSV

    表  5   参数估计表

    Table  5   Parameter estimation table

    参数
    Parameter
    系数
    Coefficient
    标准差SDWaldP95%置信区间下界
    Lower bound of 95% confidence interval
    95%置信区间上界
    Upper 95% confidence interval
    截距Intercept5139.483895.161.740.19–2494.8812773.85
    最大河道宽度
    Max River width (m)
    10.014.874.220.04**0.4619.56
    平均河道宽度
    Mean River width (m)
    25.6619.161.790.18–63.2211.90
    温度Temperature (℃)–7.1242.940.030.87–91.2877.04
    水深Depth–772.50401.813.700.05–1560.0415.04
    河道弯曲率B5182.523709.041.960.16–2087.0712452.11
    下载: 导出CSV
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