
Biodiv Sci ›› 2026, Vol. 34 ›› Issue (5): 25394. DOI: 10.17520/biods.2025394 cstr: 32101.14.biods.2025394
• Original Papers: Animal Diversity • Previous Articles Next Articles
Tianqi He1, Dongdong Zhai1,2,*(
), Fangtao Cai1, Dong Wang1, Yuanyuan Chen1,2, Hongyan Liu1,2(
), Fei Xiong1,2(
), Mingdian Liu3,*(
), Xinbin Duan3
Received:2025-10-09
Accepted:2026-01-12
Online:2026-05-20
Published:2026-06-28
Contact:
Dongdong Zhai, Mingdian Liu
Supported by:Tianqi He, Dongdong Zhai, Fangtao Cai, Dong Wang, Yuanyuan Chen, Hongyan Liu, Fei Xiong, Mingdian Liu, Xinbin Duan. Characteristics of fish community structure in the lower mainstream of the Lancang River and risk assessment of alien fish invasion[J]. Biodiv Sci, 2026, 34(5): 25394.
Fig. 1 Map of fish sampling sites in the lower mainstream of the Lancang River. MTX, Matai Town; DQ, Lancang River Bridge; NZD, Nuozhadu Town; SMG, Simaogang Town; JH, Jinghong City; NLH, Nanla River Estuary.
Fig. 2 Fish species composition in the lower mainstream of the Lancang River. (a) Proportion of fish species number by order in the lower mainstream of the Lancang River; (b) Proportion of fish species number by family in the lower mainstream of the Lancang River; (c) Proportion of fish abundance by order in the lower mainstream of the Lancang River; (d) Proportion of fish abundance by family in the lower mainstream of the Lancang River.
| 名称 Name | 优势种 Dominant species | 丰水期优势种 Dominant species in the high-flow period | 枯水期优势种 Dominant species in the low-flow period | 不同采样点优势种 Dominant species in different sampling sites | |||||
|---|---|---|---|---|---|---|---|---|---|
| 马台乡 MTX | 澜沧江大桥 DQ | 糯扎渡 NZD | 思茅港 SMG | 景洪 JH | 南腊河口 NLH | ||||
| 䱗 Hemiculter leucisculus* | + | + | + | + | + | + | + | ||
| 花身副丽鱼 Parachromis managuensis* | + | + | + | + | + | + | |||
| 齐氏罗非鱼 Coptodon zillii* | + | + | + | + | + | ||||
| 尼罗罗非鱼 Oreochromis niloticus* | + | + | + | + | |||||
| 鳙 Hypophthalmichthys nobilis* | + | ||||||||
| 高体鳑鲏 Rhodeus ocellatus* | + | + | |||||||
| 马口鱼 Opsariichthys bidens | + | ||||||||
| 罗碧鱼 Paralaubuca barroni | + | ||||||||
| 真吻虾虎鱼 Rhinogobius similis* | + | ||||||||
| 棒花鱼 Abbottina rivularis* | + | ||||||||
| 黄颡鱼 Pelteobagrus fulvidraco* | + | ||||||||
| 长臀鲃 Mystacoleucus marginatus | + | ||||||||
| 红鳍原鲌 Cultrichthys erythropterus* | + | ||||||||
| 短吻鱼 Sikukia gudgeri | + | ||||||||
| 鲤 Cyprinus carpio* | + | ||||||||
| 云南吻孔鲃 Poropuntius huangchuchieni | + | ||||||||
| 中华鲱鲇 Clupisoma sinense | + | ||||||||
Table 1 Dominant fish species in the lower mainstream of the Lancang River
| 名称 Name | 优势种 Dominant species | 丰水期优势种 Dominant species in the high-flow period | 枯水期优势种 Dominant species in the low-flow period | 不同采样点优势种 Dominant species in different sampling sites | |||||
|---|---|---|---|---|---|---|---|---|---|
| 马台乡 MTX | 澜沧江大桥 DQ | 糯扎渡 NZD | 思茅港 SMG | 景洪 JH | 南腊河口 NLH | ||||
| 䱗 Hemiculter leucisculus* | + | + | + | + | + | + | + | ||
| 花身副丽鱼 Parachromis managuensis* | + | + | + | + | + | + | |||
| 齐氏罗非鱼 Coptodon zillii* | + | + | + | + | + | ||||
| 尼罗罗非鱼 Oreochromis niloticus* | + | + | + | + | |||||
| 鳙 Hypophthalmichthys nobilis* | + | ||||||||
| 高体鳑鲏 Rhodeus ocellatus* | + | + | |||||||
| 马口鱼 Opsariichthys bidens | + | ||||||||
| 罗碧鱼 Paralaubuca barroni | + | ||||||||
| 真吻虾虎鱼 Rhinogobius similis* | + | ||||||||
| 棒花鱼 Abbottina rivularis* | + | ||||||||
| 黄颡鱼 Pelteobagrus fulvidraco* | + | ||||||||
| 长臀鲃 Mystacoleucus marginatus | + | ||||||||
| 红鳍原鲌 Cultrichthys erythropterus* | + | ||||||||
| 短吻鱼 Sikukia gudgeri | + | ||||||||
| 鲤 Cyprinus carpio* | + | ||||||||
| 云南吻孔鲃 Poropuntius huangchuchieni | + | ||||||||
| 中华鲱鲇 Clupisoma sinense | + | ||||||||
Fig. 3 Non-metric multidimensional scaling (NMDS) ordination diagram of fish community structure in the lower mainstream of the Lancang River. MTX, Matai Town; DQ, Lancang River Bridge; NZD, Nuozhadu Town; SMG, Simaogang Town; JH, Jinghong City; NLH, Nanla River Estuary. MTX1 represents the high-flow period of 2023 in MTX, MTX2 represents the low-flow period of 2023 in MTX, MTX3 represents the high-flow period of 2024 in MTX, and MTX4 represents the low-flow period of 2024 in MTX, the rest can be deduced by analogy.
| 马台乡 MTX | 澜沧江大桥 DQ | 糯扎渡 NZD | 思茅港 SMG | 景洪 JH | 南腊河口 NLH | |
|---|---|---|---|---|---|---|
| 马台乡 MTX | 0.127 | 0.151 | 0.031* | 0.002* | 0.029* | |
| 澜沧江大桥 DQ | 2.372 | 0.428 | 0.028* | 0.026* | 0.024* | |
| 糯扎渡 NZD | 1.731 | 0.816 | 0.030* | 0.032* | 0.033* | |
| 思茅港 SMG | 3.859 | 5.606 | 4.922 | 0.030* | 0.027* | |
| 景洪 JH | 5.311 | 9.603 | 8.222 | 3.670 | 0.028* | |
| 南腊河口 NLH | 6.462 | 8.411 | 6.553 | 5.628 | 6.634 |
Table 2 Results of pairwise permutational multivariate analysis of variance (PERMANOVA) on fish community structure among sampling sites in the lower mainstream of the Lancang River. The lower triangle represents F-values, the upper triangle represents P-values.
| 马台乡 MTX | 澜沧江大桥 DQ | 糯扎渡 NZD | 思茅港 SMG | 景洪 JH | 南腊河口 NLH | |
|---|---|---|---|---|---|---|
| 马台乡 MTX | 0.127 | 0.151 | 0.031* | 0.002* | 0.029* | |
| 澜沧江大桥 DQ | 2.372 | 0.428 | 0.028* | 0.026* | 0.024* | |
| 糯扎渡 NZD | 1.731 | 0.816 | 0.030* | 0.032* | 0.033* | |
| 思茅港 SMG | 3.859 | 5.606 | 4.922 | 0.030* | 0.027* | |
| 景洪 JH | 5.311 | 9.603 | 8.222 | 3.670 | 0.028* | |
| 南腊河口 NLH | 6.462 | 8.411 | 6.553 | 5.628 | 6.634 |
| 马台乡 MTX | 澜沧江大桥 DQ | 糯扎渡 NZD | 思茅港 SMG | 景洪 JH | 南腊河口 NLH | |
|---|---|---|---|---|---|---|
| 马台乡 MTX | 30.5 | 156.3 | 184.4 | 266.9 | 363.2 | |
| 澜沧江大桥 DQ | 0.29 | 125.8 | 153.9 | 236.4 | 332.7 | |
| 糯扎渡 NZD | 0.46 | 0.33 | 28.1 | 110.6 | 206.9 | |
| 思茅港 SMG | 0.73 | 0.73 | 0.79 | 82.5 | 178.8 | |
| 景洪 JH | 0.80 | 0.82 | 0.92 | 0.73 | 96.3 | |
| 南腊河口 NLH | 0.97 | 0.96 | 0.98 | 0.95 | 0.91 |
Table 3 Pairwise Bray-Curtis dissimilarity (below the diagonal) and waterway distance (above the diagonal, km) among sampling sites
| 马台乡 MTX | 澜沧江大桥 DQ | 糯扎渡 NZD | 思茅港 SMG | 景洪 JH | 南腊河口 NLH | |
|---|---|---|---|---|---|---|
| 马台乡 MTX | 30.5 | 156.3 | 184.4 | 266.9 | 363.2 | |
| 澜沧江大桥 DQ | 0.29 | 125.8 | 153.9 | 236.4 | 332.7 | |
| 糯扎渡 NZD | 0.46 | 0.33 | 28.1 | 110.6 | 206.9 | |
| 思茅港 SMG | 0.73 | 0.73 | 0.79 | 82.5 | 178.8 | |
| 景洪 JH | 0.80 | 0.82 | 0.92 | 0.73 | 96.3 | |
| 南腊河口 NLH | 0.97 | 0.96 | 0.98 | 0.95 | 0.91 |
Fig. 4 Box plots of the proportion of fish species in different ecological types at each sampling site in the lower mainstream of the Lancang River. MTX, Matai Town; DQ, Lancang River Bridge; NZD, Nuozhadu Town; SMG, Simaogang Town; JH, Jinghong City; NLH, Nanla River Estuary. Different letters (a, b, c) indicate significant differences among groups at P < 0.05.
Fig. 6 Spatial distribution map of the proportion of alien fish species and quantity to the species and quantity of catches in the lower mainstream of the Lancang River. MTX, Matai Town; DQ, Lancang River Bridge; NZD, Nuozhadu Town; SMG, Simaogang Town; JH, Jinghong City; NLH, Nanla River Estuary. Different letters (a, b, c) indicate significant differences among groups at P < 0.05.
Fig. 7 Temporal variation diagram of the proportions of alien fish species and their quantities in the total catch (by species and quantity) at different sampling sites in the lower mainstream of the Lancang River. MTX, Matai Town; DQ, Lancang River Bridge; NZD, Nuozhadu Town; SMG, Simaogang Town; JH, Jinghong City; NLH, Nanla River Estuary; HFP, High-flow period; LFP, Low-flow period.
Fig. 8 Receiver operating characteristic (ROC) curve for invasive fish risk assessment in the lower mainstream of the Lancang River. BRA is basic risk assessment (BRA) score of AS-ISK; CCA is climate change assessment (CCA) score of AS-ISK; AUC is area under the ROC curve.
| 物种 Species | 评估结果 Assessment results | 置信因子 Confidence factor | |||||
|---|---|---|---|---|---|---|---|
| BRA得分 BRA score | 入侵风险 Invasion risk | BRA + CCA 得分 BRA + CCA score | 入侵风险 Invasion risk | BRA | CCA | BRA + CCA | |
| 齐氏罗非鱼 Coptodon zillii* | 39 | 高风险 High risk | 40.5 | 高风险 High risk | 0.83 | 0.64 | 0.76 |
| 尼罗罗非鱼 Oreochromis niloticus* | 37.5 | 高风险 High risk | 38 | 高风险 High risk | 0.85 | 0.63 | 0.77 |
| 花身副丽鱼 Parachromis managuensis* | 37 | 高风险 High risk | 35 | 高风险 High risk | 0.78 | 0.62 | 0.74 |
| 下口鲇 Hypostomus plecostomus* | 35 | 高风险 High risk | 37 | 高风险 High risk | 0.86 | 0.68 | 0.8 |
| 莫桑比克罗非鱼 Oreochromis mossambicus* | 32 | 高风险 High risk | 30 | 高风险 High risk | 0.81 | 0.62 | 0.75 |
| 䱗 Hemiculter leucisculus* | 25 | 高风险 High risk | 24 | 高风险 High risk | 0.88 | 0.61 | 0.74 |
| 麦穗鱼 Pseudorasbora parva* | 25 | 高风险 High risk | 22 | 中风险 Medium risk | 0.75 | 0.57 | 0.68 |
| 麦瑞加拉鲮 Cirrhinus mrigala* | 23 | 高风险 High risk | 19 | 中风险 Medium risk | 0.77 | 0.68 | 0.71 |
| 真吻虾虎鱼 Rhinogobius similis | 22 | 中风险 Medium risk | 22 | 中风险 Medium risk | 0.76 | 0.64 | 0.72 |
| 条纹鲮脂鲤 Prochilodus lineatus* | 21 | 中风险 Medium risk | 20 | 中风险 Medium risk | 0.79 | 0.68 | 0.72 |
| 云斑尖塘鳢 Oxyeleotris marmorata | 21 | 中风险 Medium risk | 19 | 中风险 Medium risk | 0.69 | 0.62 | 0.63 |
| 短盖肥脂鲤 Piaractus brachypomus* | 19 | 中风险 Medium risk | 19 | 中风险 Medium risk | 0.73 | 0.64 | 0.68 |
| 鲤 Cyprinus carpio* | 18 | 中风险 Medium risk | 19 | 中风险 Medium risk | 0.82 | 0.64 | 0.75 |
| 草鱼 Ctenopharyngodon idella* | 18 | 中风险 Medium risk | 16 | 中风险 Medium risk | 0.79 | 0.61 | 0.65 |
| 黄颡鱼 Pelteobagrus fulvidraco | 18 | 中风险 Medium risk | 17 | 中风险 Medium risk | 0.81 | 0.64 | 0.73 |
| 大鳞副泥鳅 Paramisgurnus dabryanus | 18 | 中风险 Medium risk | 16 | 中风险 Medium risk | 0.78 | 0.64 | 0.76 |
| 棒花鱼 Abbottina rivularis | 17 | 中风险 Medium risk | 20 | 中风险 Medium risk | 0.73 | 0.64 | 0.65 |
| 鲢 Hypophthalmichthys molitrix* | 17 | 中风险 Medium risk | 18 | 中风险 Medium risk | 0.84 | 0.67 | 0.78 |
| 褐吻虾虎鱼 Rhinogobius brunneus | 17 | 中风险 Medium risk | 18 | 中风险 Medium risk | 0.72 | 0.59 | 0.64 |
| 鳙 Hypophthalmichthys nobilis* | 16 | 中风险 Medium risk | 16 | 中风险 Medium risk | 0.83 | 0.68 | 0.76 |
| 瓦氏黄颡鱼 Pelteobagrus vachelli | 16 | 中风险 Medium risk | 17 | 中风险 Medium risk | 0.73 | 0.62 | 0.66 |
| 红鳍原鲌 Cultrichthys erythropterus | 16 | 中风险 Medium risk | 14 | 中风险 Medium risk | 0.71 | 0.62 | 0.64 |
| 高体鳑鲏 Rhodeus ocellatus | 16 | 中风险 Medium risk | 19 | 中风险 Medium risk | 0.76 | 0.67 | 0.72 |
| 低眼无齿𩷶Pangasianodon hypophthalmus | 15 | 中风险 Medium risk | 16 | 中风险 Medium risk | 0.71 | 0.62 | 0.66 |
| 光泽黄颡鱼 Pelteobagrus nitidus | 14 | 中风险 Medium risk | 12 | 中风险 Medium risk | 0.72 | 0.6 | 0.65 |
Table 4 Results of the risk assessment for alien fish invasion in the lower mainstream of the Lancang River
| 物种 Species | 评估结果 Assessment results | 置信因子 Confidence factor | |||||
|---|---|---|---|---|---|---|---|
| BRA得分 BRA score | 入侵风险 Invasion risk | BRA + CCA 得分 BRA + CCA score | 入侵风险 Invasion risk | BRA | CCA | BRA + CCA | |
| 齐氏罗非鱼 Coptodon zillii* | 39 | 高风险 High risk | 40.5 | 高风险 High risk | 0.83 | 0.64 | 0.76 |
| 尼罗罗非鱼 Oreochromis niloticus* | 37.5 | 高风险 High risk | 38 | 高风险 High risk | 0.85 | 0.63 | 0.77 |
| 花身副丽鱼 Parachromis managuensis* | 37 | 高风险 High risk | 35 | 高风险 High risk | 0.78 | 0.62 | 0.74 |
| 下口鲇 Hypostomus plecostomus* | 35 | 高风险 High risk | 37 | 高风险 High risk | 0.86 | 0.68 | 0.8 |
| 莫桑比克罗非鱼 Oreochromis mossambicus* | 32 | 高风险 High risk | 30 | 高风险 High risk | 0.81 | 0.62 | 0.75 |
| 䱗 Hemiculter leucisculus* | 25 | 高风险 High risk | 24 | 高风险 High risk | 0.88 | 0.61 | 0.74 |
| 麦穗鱼 Pseudorasbora parva* | 25 | 高风险 High risk | 22 | 中风险 Medium risk | 0.75 | 0.57 | 0.68 |
| 麦瑞加拉鲮 Cirrhinus mrigala* | 23 | 高风险 High risk | 19 | 中风险 Medium risk | 0.77 | 0.68 | 0.71 |
| 真吻虾虎鱼 Rhinogobius similis | 22 | 中风险 Medium risk | 22 | 中风险 Medium risk | 0.76 | 0.64 | 0.72 |
| 条纹鲮脂鲤 Prochilodus lineatus* | 21 | 中风险 Medium risk | 20 | 中风险 Medium risk | 0.79 | 0.68 | 0.72 |
| 云斑尖塘鳢 Oxyeleotris marmorata | 21 | 中风险 Medium risk | 19 | 中风险 Medium risk | 0.69 | 0.62 | 0.63 |
| 短盖肥脂鲤 Piaractus brachypomus* | 19 | 中风险 Medium risk | 19 | 中风险 Medium risk | 0.73 | 0.64 | 0.68 |
| 鲤 Cyprinus carpio* | 18 | 中风险 Medium risk | 19 | 中风险 Medium risk | 0.82 | 0.64 | 0.75 |
| 草鱼 Ctenopharyngodon idella* | 18 | 中风险 Medium risk | 16 | 中风险 Medium risk | 0.79 | 0.61 | 0.65 |
| 黄颡鱼 Pelteobagrus fulvidraco | 18 | 中风险 Medium risk | 17 | 中风险 Medium risk | 0.81 | 0.64 | 0.73 |
| 大鳞副泥鳅 Paramisgurnus dabryanus | 18 | 中风险 Medium risk | 16 | 中风险 Medium risk | 0.78 | 0.64 | 0.76 |
| 棒花鱼 Abbottina rivularis | 17 | 中风险 Medium risk | 20 | 中风险 Medium risk | 0.73 | 0.64 | 0.65 |
| 鲢 Hypophthalmichthys molitrix* | 17 | 中风险 Medium risk | 18 | 中风险 Medium risk | 0.84 | 0.67 | 0.78 |
| 褐吻虾虎鱼 Rhinogobius brunneus | 17 | 中风险 Medium risk | 18 | 中风险 Medium risk | 0.72 | 0.59 | 0.64 |
| 鳙 Hypophthalmichthys nobilis* | 16 | 中风险 Medium risk | 16 | 中风险 Medium risk | 0.83 | 0.68 | 0.76 |
| 瓦氏黄颡鱼 Pelteobagrus vachelli | 16 | 中风险 Medium risk | 17 | 中风险 Medium risk | 0.73 | 0.62 | 0.66 |
| 红鳍原鲌 Cultrichthys erythropterus | 16 | 中风险 Medium risk | 14 | 中风险 Medium risk | 0.71 | 0.62 | 0.64 |
| 高体鳑鲏 Rhodeus ocellatus | 16 | 中风险 Medium risk | 19 | 中风险 Medium risk | 0.76 | 0.67 | 0.72 |
| 低眼无齿𩷶Pangasianodon hypophthalmus | 15 | 中风险 Medium risk | 16 | 中风险 Medium risk | 0.71 | 0.62 | 0.66 |
| 光泽黄颡鱼 Pelteobagrus nitidus | 14 | 中风险 Medium risk | 12 | 中风险 Medium risk | 0.72 | 0.6 | 0.65 |
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