Published January 22, 2024
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Table 2 in Risk screening of non-native freshwater fishes in Yunnan Province, China
Authors/Creators
- 1. State Key Laboratory of Lake Science and Environment, Nanjing Institute of Geography and Limnology, Chinese Academy of Sciences, & University of Chinese Academy of Sciences, Beijing 100049, China
- 2. State Key Laboratory of Lake Science and Environment, Nanjing Institute of Geography and Limnology, Chinese Academy of Sciences,
Description
Table 2. Non-native freshwater fish species assessed with the Aquatic Species Invasiveness Screening Kit (AS-ISK) for Yunnan Province
| Species name | A priori categorisation | Screening component | Confidence | |||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|
| BRA | BRA+CCA | CL | CF | |||||||||
| Score | Outcome | Score | Outcome | Delta | Total | BRA | CCA | Total | BRA | CCA | ||
| Acheilognathus chankaensis | N | 10 | Medium | 8 | Medium | −2 | 3.4 | 3.4 | 3.5 | 0.85 | 0.85 | 0.88 |
| Acheilognathus macropterus | N | −2 | Low | −4 | Low | −2 | 3.3 | 3.3 | 3.2 | 0.81 | 0.82 | 0.79 |
| Acipenser baerii | Y | 26 | High | 32 | High | 6 | 3.0 | 3.0 | 2.8 | 0.74 | 0.74 | 0.71 |
| Ameiurus nebulosus | Y | 29 | High | 35 | High | 6 | 3.0 | 3.0 | 2.8 | 0.75 | 0.76 | 0.71 |
| Anguilla anguilla | N | 0 | Low | −2 | Low | −2 | 3.0 | 3.0 | 3.0 | 0.77 | 0.77 | 0.75 |
| Anguilla japonica | N | −2 | Low | −4 | Low | −2 | 3.1 | 3.2 | 3.0 | 0.79 | 0.80 | 0.75 |
| Carassius cuvieri | Y | 24 | High | 28 | High | 4 | 3.1 | 3.1 | 2.8 | 0.78 | 0.79 | 0.71 |
| Clarias gariepinus | Y | 39.5 | High | 47.5 | High | 8 | 3.1 | 3.1 | 2.8 | 0.77 | 0.78 | 0.71 |
| Ctenopharyngodon idella | Y | 29.5 | High | 33.5 | High | 4 | 3.3 | 3.3 | 3.2 | 0.83 | 0.84 | 0.79 |
| Cultrichthys erythropterus | N | 22.5 | High | 24.5 | High | 2 | 3.2 | 3.3 | 3.0 | 0.81 | 0.82 | 0.75 |
| Gambusia affinis | Y | 39 | High | 41 | High | 2 | 3.1 | 3.1 | 3.0 | 0.78 | 0.78 | 0.75 |
| Hypomesus olidus | N | 16 | Medium | 16 | Medium | 0 | 3.2 | 3.2 | 3.0 | 0.79 | 0.80 | 0.75 |
| Hypophthalmichthys molitrix | Y | 24 | High | 30 | High | 6 | 3.3 | 3.3 | 3.0 | 0.83 | 0.84 | 0.75 |
| Hypophthalmichthys nobilis | Y | 26 | High | 32 | High | 6 | 3.3 | 3.4 | 3.0 | 0.84 | 0.85 | 0.75 |
| Hyporhamphus intermedius | N | 7 | Medium | 7 | Medium | 0 | 3.2 | 3.2 | 3.0 | 0.80 | 0.80 | 0.75 |
| Hypostomus plecostomus | Y | 51 | High | 59 | High | 8 | 3.0 | 3.0 | 3.0 | 0.75 | 0.74 | 0.75 |
| Ictalurus punctatus | Y | 36.5 | High | 42.5 | High | 6 | 3.0 | 3.0 | 2.7 | 0.75 | 0.76 | 0.67 |
| Labeo rohita | N | 10 | Medium | 14 | Medium | 4 | 3.1 | 3.2 | 3.0 | 0.79 | 0.79 | 0.75 |
| Megalobrama amblycephala | N | 10 | Medium | 10 | Medium | 0 | 3.4 | 3.4 | 3.3 | 0.84 | 0.84 | 0.83 |
| Micropterus salmoides | Y | 35 | High | 43 | High | 8 | 3.1 | 3.2 | 2.5 | 0.79 | 0.81 | 0.63 |
| Mylopharyngodon piceus | Y | 29 | High | 35 | High | 6 | 3.3 | 3.3 | 3.0 | 0.82 | 0.83 | 0.75 |
| Neosalanx taihuensis | N | 24.5 | High | 22.5 | High | −2 | 3.4 | 3.4 | 3.0 | 0.85 | 0.86 | 0.75 |
| Oncorhynchus mykiss | Y | 29 | High | 37 | High | 8 | 3.0 | 3.0 | 2.8 | 0.75 | 0.75 | 0.71 |
| Oreochromis aureus | Y | 49 | High | 61 | High | 12 | 3.1 | 3.1 | 2.7 | 0.77 | 0.78 | 0.67 |
| Oreochromis mossambicus | Y | 44.5 | High | 56.5 | High | 12 | 2.9 | 3.0 | 2.8 | 0.75 | 0.75 | 0.71 |
| Oreochromis niloticus | Y | 47 | High | 59 | High | 12 | 2.9 | 3.0 | 2.5 | 0.74 | 0.75 | 0.63 |
| Parabramis pekinensis | N | 5.5 | Medium | 3.5 | Medium | −2 | 3.3 | 3.3 | 3.0 | 0.81 | 0.82 | 0.75 |
| Paramisgurnus dabryanus | N | 13.5 | Medium | 17.5 | High | 4 | 3.2 | 3.2 | 3.0 | 0.80 | 0.80 | 0.75 |
| Piaractus brachypomus | Y | 8 | Medium | 12 | Medium | 4 | 3.1 | 3.1 | 3.0 | 0.77 | 0.77 | 0.75 |
| Prochilodus lineatus | N | 11 | Medium | 17 | Medium | 6 | 3.1 | 3.1 | 3.0 | 0.76 | 0.77 | 0.75 |
| Protosalanx hyalocranius | N | 14.5 | Medium | 12.5 | Medium | −2 | 3.1 | 3.1 | 2.8 | 0.76 | 0.77 | 0.71 |
| Rhinogobius cliffordpopei | Y | 37 | High | 43 | High | 6 | 3.1 | 3.1 | 2.8 | 0.76 | 0.77 | 0.71 |
| Salmo trutta | Y | 18 | High | 12 | Medium | −6 | 2.9 | 2.9 | 3.0 | 0.73 | 0.72 | 0.75 |
| Sarcocheilichthys nigripinnis | N | 3 | Medium | 3 | Medium | 0 | 3.5 | 3.5 | 3.2 | 0.86 | 0.87 | 0.79 |
| Siniperca chuatsi | N | 14.5 | Medium | 18.5 | High | 4 | 3.0 | 3.0 | 2.8 | 0.74 | 0.74 | 0.71 |
| Tinca tinca | Y | 21 | High | 27 | High | 6 | 3.1 | 3.1 | 3.0 | 0.77 | 0.77 | 0.75 |
| Toxabramis swinhonis | N | 16.5 | Medium | 16.5 | Medium | 0 | 3.3 | 3.4 | 3.2 | 0.84 | 0.84 | 0.79 |
| A priori categorisation (N: non-invasive; Y: invasive); Screening component (BRA: Basic Risk Assessment, BRA+CCA: BRA+ Climate Change Assessment, Delta: BRA+CCA score minus BRA score); Confidence (CL: confidence level, CF: confidence factor); Outcome (Low: score <1, Medium: 1 ≤ score <17.25, High: score ≥ 17.25) |
Notes
Published as part of Ge, You, Gu, Xiaohong, Zeng, Qingfei, Mao, Zhigang, Chen, Huihui & Yang, Huiting, 2024, Risk screening of non-native freshwater fishes in Yunnan Province, China, pp. 80 in Management of Biological Invasions 15 (1) on page 80, DOI: 10.3391/mbi.2024.15.1.05, http://zenodo.org/record/11976883
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- Journal article: 10.3391/mbi.2024.15.1.05 (DOI)
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