
生物多样性 ›› 2025, Vol. 33 ›› Issue (8): 25123. DOI: 10.17520/biods.2025123 cstr: 32101.14.biods.2025123
收稿日期:2025-04-02
接受日期:2025-05-30
出版日期:2025-08-20
发布日期:2025-09-17
通讯作者:
*E-mail: dapan@njnu.edu.cn
基金资助:
Ruxiao Wang(
), Boyang Shi(
), Da Pan*(
)(
), Hongying Sun(
)
Received:2025-04-02
Accepted:2025-05-30
Online:2025-08-20
Published:2025-09-17
Contact:
*E-mail: dapan@njnu.edu.cn
Supported by:摘要:
淡水蟹类是底栖大型无脊椎动物代表类群之一, 也是判断生态系统健康与否的关键指示生物, 但其物种多样性和遗传多样性并未得到有效保护。据此, 本研究以中国特有的华溪蟹属(Sinopotamon)淡水蟹类为例, 基于详尽的野外调查与文献资料汇总, 构建了该类群的物种分布数据库, 利用空间广义线性混合模型来评估影响其物种多样性与遗传多样性的关键环境因素; 通过将物种多样性和遗传多样性格局与现有保护地进行叠加分析, 以识别其多样性热点和保护空缺区域。研究结果表明, 华溪蟹属物种多样性分布中心位于云贵高原东北缘至浙闽丘陵之间的地区, 其物种多样性整体上呈现出由长江流域向南北边缘逐渐稀少的特点; 遗传多样性呈现出空间不均匀分布的特征, 山地区域的遗传多样性相对较高。物种多样性和遗传多样性之间存在显著的正相关关系, 海拔和年平均降水量等环境因子对两者具有显著的正向影响。华溪蟹属物种多样性和遗传多样性格局呈现显著的空间聚集性, 其热点主要分布于中国中南部的山地丘陵地带, 在该地区识别出4个保护空缺区域; 南岭山脉东段被识别为遗传多样性特有的热点区域。本文研究结果显示, 山地生态系统及暖湿气候在华溪蟹属淡水蟹物种多样性和遗传多样性的形成过程中发挥了关键作用。本研究强调了结合物种多样性和遗传多样性来规划自然保护区的必要性, 为中国淡水生态系统的未来生物多样性保护管理与决策提供了数据支撑和科学依据。
王儒晓, 史博洋, 潘达, 孙红英 (2025) 中国特有华溪蟹属淡水蟹多样性格局及其保护空缺. 生物多样性, 33, 25123. DOI: 10.17520/biods.2025123.
Ruxiao Wang, Boyang Shi, Da Pan, Hongying Sun (2025) Biodiversity patterns and conservation gaps of the endemic freshwater crab genus Sinopotamon in China. Biodiversity Science, 33, 25123. DOI: 10.17520/biods.2025123.
图1 华溪蟹属物种分布点位及地理分布区。(A)华溪蟹属物种分布点(黑色圆点)及分子取样点(红色圆点); (B)华溪蟹属物种分布区内分布的主要山脉(修改自刘明光, 2010); (C)华溪蟹属物种分布区内的生物多样性优先保护区域(绿色斑块; 引自生态环境部, https://www.mee.gov.cn/gkml/hbb/bgg/201601/t20160105_321061.htm)与国家级自然保护区(蓝色斑块; 引自生态环境部, https://www.mee.gov.cn/ywgz/zrstbh/zrbhdjg/201905/P020190514616282907461.pdf)。
Fig. 1 Distribution sites and geographical range of Sinopotamon species. (A) Distribution sites of Sinopotamon species (black dots) and molecular sampling localities (red dots); (B) Major mountain ranges within the distribution area of Sinopotamon (modified from Liu, 2010); (C) Biodiversity priority conservation areas (green patches; modified from Ministry of Ecology and Environment, https://www.mee.gov.cn/gkml/hbb/bgg/201601/t20160105_321061.htm) and national nature reserves (blue patches; data from Ministry of Ecology and Environment, https://www.mee.gov.cn/ywgz/zrstbh/zrbhdjg/201905/P020190514616282907461.pdf) within the distribution range of Sinopotamon species.
图2 华溪蟹属淡水蟹物种丰富度和遗传多样性空间分布格局。(A)以1° × 1°网格为操作单元的物种丰富度格局; (B)以1° × 1°网格为操作单元的遗传多样性格局; (C)以2° × 2°网格为操作单元的物种丰富度格局; (D)以2° × 2°网格为操作单元的遗传多样性格局。S1-S3: 物种多样性分布中心; G1-G5: 遗传多样性分布中心。
Fig. 2 Spatial patterns of species richness and genetic diversity for freshwater crabs of the genus Sinopotamon. (A) Species richness patterns based on 1° × 1° grid; (B) Genetic diversity patterns based on 1° × 1° grid; (C) Species richness patterns based on 2° × 2° grid; (D) Genetic diversity patterns based on 2° × 2° grid. S1-S3, Centers of species diversity; G1-G5, Centers of genetic diversity.
| 物种 Species | 分布点位数量 No. of distribution points | 序列数量 No. of sequences | 核苷酸多样性 Nucleotide diversity (π) | 物种 Species | 分布点位数量 No. of distribution points | 序列数量 No. of sequences | 核苷酸多样性 Nucleotide diversity (π) |
|---|---|---|---|---|---|---|---|
| 尖叶华溪蟹 S. acutum | 132 | 10 | 0.05163 | 浏阳华溪蟹 S. liuyangense | 5 | 5 | 0.03215 |
| 安徽华溪蟹 S. anhuiense | 4 | 6 | 0.05184 | 隆林华溪蟹 S. longlinense | 1 | 4 | 0.02150 |
| 安远华溪蟹 S. anyuanense | 19 | 16 | 0.04329 | 娄底华溪蟹 S. loudiense | 9 | 9 | 0.04019 |
| 白岩华溪蟹 S. baiyanense | 3 | 6 | 0.03639 | 麻阳华溪蟹 S. mayangense | 2 | 5 | 0.05047 |
| 保康华溪蟹 S. baokangense | 1 | 3 | 0.02617 | 闽东华溪蟹 S. mindongense | 4 | 6 | 0.05184 |
| 双叶华溪蟹 S. bilobatum | 12 | 6 | 0.03988 | 南岭华溪蟹 S. nanlingense | 10 | 6 | 0.05097 |
| 茶陵华溪蟹 S. chalingense | 5 | 5 | 0.05271 | 矮小华溪蟹 S. nanum | 20 | 12 | 0.03767 |
| 长安华溪蟹 S. changanense | 7 | 2 | 0.00100 | 宁岗华溪蟹 S. ninggangense | 4 | 4 | 0.05452 |
| 浙江华溪蟹 S. chekiangense | 40 | 12 | 0.04959 | 斜缘华溪蟹 S. obliquum | 16 | 10 | 0.04623 |
| 城口华溪蟹 S. chengkuense | 3 | 14 | 0.04780 | 小华溪蟹 S. parvum | 2 | 4 | 0.01121 |
| 赤水华溪蟹 S. chishuiense | 8 | 3 | 0.00125 | 屏山华溪蟹 S. pingshanense | 7 | 8 | 0.05367 |
| 叉肢华溪蟹 S. cladopodum | 48 | 10 | 0.04341 | 平原华溪蟹 S. planum | 29 | 4 | 0.02056 |
| 隆突华溪蟹 S. convexum | 7 | 8 | 0.04840 | 融水华溪蟹 S. rongshuiense | 21 | 6 | 0.04112 |
| 光泽华溪蟹 S. davidi | 50 | 18 | 0.05677 | 陕西华溪蟹 S. shensiense | 57 | 14 | 0.04377 |
| 窄小华溪蟹 S. decrescentum | 5 | 7 | 0.04361 | 四股桥华溪蟹 S. siguqiaoense | 7 | 4 | 0.04860 |
| 锯齿华溪蟹 S. denticulatum | 23 | 8 | 0.04493 | 直立华溪蟹 S. styxum | 24 | 7 | 0.03151 |
| 凹肢华溪蟹指名亚种 S. depressum depressum | 33 | 5 | 0.05059 | 圆顶华溪蟹 S. teritisum | 29 | 10 | 0.03007 |
| 凹肢华溪蟹商城亚种 S. depressum shangchengense | 5 | 3 | 0.03975 | 肿胀华溪蟹 S. turgidum | 4 | 10 | 0.03626 |
| 峨边华溪蟹 S. ebianense | 12 | 2 | 0.03738 | 不等叶华溪蟹 S. unaequum | 10 | 3 | 0.04523 |
| 峨眉华溪蟹 S. emeiense | 4 | 7 | 0.04700 | 万载华溪蟹 S. wanzaiense | 27 | 6 | 0.04586 |
| 瘦肢华溪蟹 S. exiguum | 26 | 8 | 0.04433 | 巫山华溪蟹 S. wushanense | 5 | 9 | 0.04460 |
| 福建华溪蟹 S. fukienense | 108 | 13 | 0.04671 | 湘西华溪蟹 S. xiangxiense | 30 | 17 | 0.04935 |
| 复兴华溪蟹 S. fuxingense | 10 | 6 | 0.04810 | 新宁华溪蟹 S. xingningense | 3 | 6 | 0.04735 |
| 汉阳华溪蟹 S. hanyangense | 11 | 7 | 0.03818 | 兴山华溪蟹 S. xingshanense | 21 | 5 | 0.03551 |
| 河南华溪蟹 S. honanense | 64 | 9 | 0.04720 | 休宁华溪蟹 S. xiuningense | 1 | 3 | 0.03863 |
| 会同华溪蟹 S. huitongense | 10 | 6 | 0.04125 | 修水华溪蟹 S. xiushuiense | 4 | 5 | 0.03925 |
| 江口华溪蟹 S. jiangkuoense | 16 | 7 | 0.03810 | 雅安华溪蟹 S. yaanense | 9 | 12 | 0.05248 |
| 将乐华溪蟹 S. jianglenense | 18 | 3 | 0.03701 | 长江华溪蟹陕县亚种 S. yangtsekiense shanxianense | 7 | 2 | 0 |
| 绛县华溪蟹 S. jiangxianense | 6 | 12 | 0.04486 | 长江华溪蟹桐柏亚种 S. yangtsekiense tongbaiense | 25 | 2 | 0.04486 |
| 九江华溪蟹 S. jiujiangense | 10 | 7 | 0.05714 | 长江华溪蟹指名亚种 S. yangtsekiense yangtsekiense | 85 | 13 | 0.04007 |
| 绩溪华溪蟹 S. jixiense | 6 | 2 | 0.10093 | 黟县华溪蟹 S. yixianense | 6 | 5 | 0.00112 |
| 凯里华溪蟹 S. kenliense | 6 | 4 | 0.04268 | 岳阳华溪蟹 S. yueyangense | 6 | 7 | 0.03792 |
| 灌县华溪蟹 S. kwanhsienense | 12 | 4 | 0.03240 | 玉山华溪蟹 S. yushanense | 3 | 6 | 0.04922 |
| 兰氏华溪蟹 S. lansi | 96 | 11 | 0.04330 | 遵义华溪蟹 S. zunyiense | 5 | 5 | 0.03178 |
| 莲花华溪蟹 S. linhuaense | 3 | 6 | 0.05670 | 总计 Total | 291 | 490 | - |
表1 华溪蟹属69个物种的分布点位数量和16S rDNA序列数量及其核苷酸多样性
Table 1 Distribution localities, number of 16S rDNA sequences, and nucleotide diversity of 69 species of the genus Sinopotamon
| 物种 Species | 分布点位数量 No. of distribution points | 序列数量 No. of sequences | 核苷酸多样性 Nucleotide diversity (π) | 物种 Species | 分布点位数量 No. of distribution points | 序列数量 No. of sequences | 核苷酸多样性 Nucleotide diversity (π) |
|---|---|---|---|---|---|---|---|
| 尖叶华溪蟹 S. acutum | 132 | 10 | 0.05163 | 浏阳华溪蟹 S. liuyangense | 5 | 5 | 0.03215 |
| 安徽华溪蟹 S. anhuiense | 4 | 6 | 0.05184 | 隆林华溪蟹 S. longlinense | 1 | 4 | 0.02150 |
| 安远华溪蟹 S. anyuanense | 19 | 16 | 0.04329 | 娄底华溪蟹 S. loudiense | 9 | 9 | 0.04019 |
| 白岩华溪蟹 S. baiyanense | 3 | 6 | 0.03639 | 麻阳华溪蟹 S. mayangense | 2 | 5 | 0.05047 |
| 保康华溪蟹 S. baokangense | 1 | 3 | 0.02617 | 闽东华溪蟹 S. mindongense | 4 | 6 | 0.05184 |
| 双叶华溪蟹 S. bilobatum | 12 | 6 | 0.03988 | 南岭华溪蟹 S. nanlingense | 10 | 6 | 0.05097 |
| 茶陵华溪蟹 S. chalingense | 5 | 5 | 0.05271 | 矮小华溪蟹 S. nanum | 20 | 12 | 0.03767 |
| 长安华溪蟹 S. changanense | 7 | 2 | 0.00100 | 宁岗华溪蟹 S. ninggangense | 4 | 4 | 0.05452 |
| 浙江华溪蟹 S. chekiangense | 40 | 12 | 0.04959 | 斜缘华溪蟹 S. obliquum | 16 | 10 | 0.04623 |
| 城口华溪蟹 S. chengkuense | 3 | 14 | 0.04780 | 小华溪蟹 S. parvum | 2 | 4 | 0.01121 |
| 赤水华溪蟹 S. chishuiense | 8 | 3 | 0.00125 | 屏山华溪蟹 S. pingshanense | 7 | 8 | 0.05367 |
| 叉肢华溪蟹 S. cladopodum | 48 | 10 | 0.04341 | 平原华溪蟹 S. planum | 29 | 4 | 0.02056 |
| 隆突华溪蟹 S. convexum | 7 | 8 | 0.04840 | 融水华溪蟹 S. rongshuiense | 21 | 6 | 0.04112 |
| 光泽华溪蟹 S. davidi | 50 | 18 | 0.05677 | 陕西华溪蟹 S. shensiense | 57 | 14 | 0.04377 |
| 窄小华溪蟹 S. decrescentum | 5 | 7 | 0.04361 | 四股桥华溪蟹 S. siguqiaoense | 7 | 4 | 0.04860 |
| 锯齿华溪蟹 S. denticulatum | 23 | 8 | 0.04493 | 直立华溪蟹 S. styxum | 24 | 7 | 0.03151 |
| 凹肢华溪蟹指名亚种 S. depressum depressum | 33 | 5 | 0.05059 | 圆顶华溪蟹 S. teritisum | 29 | 10 | 0.03007 |
| 凹肢华溪蟹商城亚种 S. depressum shangchengense | 5 | 3 | 0.03975 | 肿胀华溪蟹 S. turgidum | 4 | 10 | 0.03626 |
| 峨边华溪蟹 S. ebianense | 12 | 2 | 0.03738 | 不等叶华溪蟹 S. unaequum | 10 | 3 | 0.04523 |
| 峨眉华溪蟹 S. emeiense | 4 | 7 | 0.04700 | 万载华溪蟹 S. wanzaiense | 27 | 6 | 0.04586 |
| 瘦肢华溪蟹 S. exiguum | 26 | 8 | 0.04433 | 巫山华溪蟹 S. wushanense | 5 | 9 | 0.04460 |
| 福建华溪蟹 S. fukienense | 108 | 13 | 0.04671 | 湘西华溪蟹 S. xiangxiense | 30 | 17 | 0.04935 |
| 复兴华溪蟹 S. fuxingense | 10 | 6 | 0.04810 | 新宁华溪蟹 S. xingningense | 3 | 6 | 0.04735 |
| 汉阳华溪蟹 S. hanyangense | 11 | 7 | 0.03818 | 兴山华溪蟹 S. xingshanense | 21 | 5 | 0.03551 |
| 河南华溪蟹 S. honanense | 64 | 9 | 0.04720 | 休宁华溪蟹 S. xiuningense | 1 | 3 | 0.03863 |
| 会同华溪蟹 S. huitongense | 10 | 6 | 0.04125 | 修水华溪蟹 S. xiushuiense | 4 | 5 | 0.03925 |
| 江口华溪蟹 S. jiangkuoense | 16 | 7 | 0.03810 | 雅安华溪蟹 S. yaanense | 9 | 12 | 0.05248 |
| 将乐华溪蟹 S. jianglenense | 18 | 3 | 0.03701 | 长江华溪蟹陕县亚种 S. yangtsekiense shanxianense | 7 | 2 | 0 |
| 绛县华溪蟹 S. jiangxianense | 6 | 12 | 0.04486 | 长江华溪蟹桐柏亚种 S. yangtsekiense tongbaiense | 25 | 2 | 0.04486 |
| 九江华溪蟹 S. jiujiangense | 10 | 7 | 0.05714 | 长江华溪蟹指名亚种 S. yangtsekiense yangtsekiense | 85 | 13 | 0.04007 |
| 绩溪华溪蟹 S. jixiense | 6 | 2 | 0.10093 | 黟县华溪蟹 S. yixianense | 6 | 5 | 0.00112 |
| 凯里华溪蟹 S. kenliense | 6 | 4 | 0.04268 | 岳阳华溪蟹 S. yueyangense | 6 | 7 | 0.03792 |
| 灌县华溪蟹 S. kwanhsienense | 12 | 4 | 0.03240 | 玉山华溪蟹 S. yushanense | 3 | 6 | 0.04922 |
| 兰氏华溪蟹 S. lansi | 96 | 11 | 0.04330 | 遵义华溪蟹 S. zunyiense | 5 | 5 | 0.03178 |
| 莲花华溪蟹 S. linhuaense | 3 | 6 | 0.05670 | 总计 Total | 291 | 490 | - |
图3 以1° × 1° (A)和2° × 2° (B)网格为操作单元的物种丰富度与遗传多样性之间的单变量线性回归
Fig. 3 Univariate linear regressions between species richness and genetic diversity for freshwater crabs of the genus Sinopotamon based on 1° × 1° (A) and 2° × 2° (B) grids
| 环境变量 Environmental variables | 物种丰富度 Species richness | 遗传多样性 Genetic diversity | ||||
|---|---|---|---|---|---|---|
| 估计值 Estimate | 标准误 SE | t | 估计值 Estimate | 标准误 SE | t | |
| 截距 Intercept | -2.27E-16 | 0.06564 | -3.45E-15 | -3.61E-19 | 0.07223 | 4.99E-18 |
| 海拔 Altitude (ALT) | 0.681 | 0.144 | 4.730 | 0.179 | 0.082 | 1.960 |
| 年平均降水量 Mean annual precipitation (MAP) | 0.590 | 0.156 | 3.790 | 0.203 | 0.079 | 2.590 |
| 年温差 Temperature annual range (TAR) | 0.355 | 0.124 | 2.880 | -0.149 | 0.136 | -1.090 |
| 最湿季度均温 Mean temperature of wettest quarter (MTWQ) | 0.251 | 0.115 | 2.180 | -0.072 | 0.127 | -0.571 |
| 坡向 Aspect (ASP) | -0.048 | 0.079 | -0.607 | -0.105 | 0.087 | -1.210 |
| 降水量变异系数 Precipitation seasonality (PS) | -0.101 | 0.102 | -0.987 | -0.019 | 0.112 | -0.173 |
| 等温性 Isothermality (ISO) | -0.367 | 0.083 | -4.420 | -0.180 | 0.091 | -1.970 |
表2 1° × 1°网格分辨率下环境变量对华溪蟹属物种丰富度和遗传多样性影响的空间广义线性混合模型结果。粗体表示估计系数的95%置信区间明显偏离零。
Table 2 Results of spaGLMMs analyses evaluating the effects of environmental variables on species richness and genetic diversity of the genus Sinopotamon based on 1° × 1° grid. Bold font indicates that 95% confidence intervals of the estimated coefficients significantly deviated from zero.
| 环境变量 Environmental variables | 物种丰富度 Species richness | 遗传多样性 Genetic diversity | ||||
|---|---|---|---|---|---|---|
| 估计值 Estimate | 标准误 SE | t | 估计值 Estimate | 标准误 SE | t | |
| 截距 Intercept | -2.27E-16 | 0.06564 | -3.45E-15 | -3.61E-19 | 0.07223 | 4.99E-18 |
| 海拔 Altitude (ALT) | 0.681 | 0.144 | 4.730 | 0.179 | 0.082 | 1.960 |
| 年平均降水量 Mean annual precipitation (MAP) | 0.590 | 0.156 | 3.790 | 0.203 | 0.079 | 2.590 |
| 年温差 Temperature annual range (TAR) | 0.355 | 0.124 | 2.880 | -0.149 | 0.136 | -1.090 |
| 最湿季度均温 Mean temperature of wettest quarter (MTWQ) | 0.251 | 0.115 | 2.180 | -0.072 | 0.127 | -0.571 |
| 坡向 Aspect (ASP) | -0.048 | 0.079 | -0.607 | -0.105 | 0.087 | -1.210 |
| 降水量变异系数 Precipitation seasonality (PS) | -0.101 | 0.102 | -0.987 | -0.019 | 0.112 | -0.173 |
| 等温性 Isothermality (ISO) | -0.367 | 0.083 | -4.420 | -0.180 | 0.091 | -1.970 |
| 莫兰指数 Moran’s I | 预期指数 Expected index | 方差 Variance | Z | P | |
|---|---|---|---|---|---|
| 物种丰富度 Species richness | 0.3784651 | -0.005813953 | 0.0018715 | 205.4628 | 3.26E-19 |
| 遗传多样性 Genetic diversity | 0.4036666 | -0.005813953 | 0.0018401 | 222.6705 | 6.75E-22 |
表3 1° × 1°网格分辨率下华溪蟹属物种丰富度和遗传多样性分布格局的空间自相关分析结果
Table 3 Results of spatial autocorrelation analyses of species richness and genetic diversity distribution patterns in the genus Sinopotamon based on 1° × 1° grid
| 莫兰指数 Moran’s I | 预期指数 Expected index | 方差 Variance | Z | P | |
|---|---|---|---|---|---|
| 物种丰富度 Species richness | 0.3784651 | -0.005813953 | 0.0018715 | 205.4628 | 3.26E-19 |
| 遗传多样性 Genetic diversity | 0.4036666 | -0.005813953 | 0.0018401 | 222.6705 | 6.75E-22 |
图4 华溪蟹属淡水蟹类热点地区与保护空缺区域的空间分布格局。(A)以1° × 1°网格为操作单元的物种丰富度格局; (B)以1° × 1°网格为操作单元的遗传多样性格局。红色网格代表热点区域, 绿色网格代表保护地区域。黑色虚线代表主要的保护空缺区域。CI表示置信区间。
Fig. 4 Spatial distribution patterns of biodiversity hotspots and conservation gaps for freshwater crabs of Sinopotamon. (A) Species richness patterns based on 1° × 1° grid; (B) Genetic diversity patterns based on 1° × 1° grid. Red grids represent biodiversity hotspots, green grids represent protected areas, and black dashed lines indicate major conservation gap areas. CI represents confidence interval.
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