Abstract
To inform regional managers of potentially invasive non-native (NN) freshwater fishes in the principal hydrosystem that drains the West Siberian Plain, the River Ob basin, 31 extant and potential future NN fish species were screened using the Aquatic Species Invasiveness Screening Kit (AS-ISK) with respect to current and projected future climate conditions. Calibration of the AS-ISK scores, using receiver operating characteristic curve analysis, identified ‘basic risk assessment’ and ‘climate change assessment’ threshold scores of 27.5 and 34.75, respectively, with which to distinguish species that pose a high risk of being invasive in the Ob basin and those that pose a low-to-medium risk. Of the species screened, 12 ranked as high risk (black bullhead Ameiurus melas, brown bullhead Ameiurus nebulosus, grass carp Ctenopharyngodon idella, common carp Cyprinus carpio, eastern mosquitofish Gambusia holbrooki, silver carp Hypophthalmichthys molitrix, oriental weatherfish Misgurnus anguillicaudatus, rainbow trout Oncorhynchus mykiss, Chinese (Amur) sleeper Perccottus glenii, topmouth gudgeon Pseudorasbora parva, brown trout Salmo trutta, pikeperch Sander lucioperca and rudd Scardinius erythrophthalmus). The remaining species ranked as medium or low risk. Although the risk scores increased in 68% of species under climate change conditions, this affected the risk rankings of only two species: Salmo trutta decreased in rank from high to medium and Sander lucioperca increased in rank from medium to high. The outcomes of the present study, which identified 12 species for which full risk assessments are recommended, serves to inform the development of NN species policy and management in Russia.
Highlights
The West Siberian Plain is a region characterised by high native biodiversity (Solomeshch 2005) and aboriginal culture conservation value (Klubnikin et al 2000), but threatened by indirect and direct human impacts, including climate change, habitat destruction and non-native (NN) species introductions
The receiver operating characteristic (ROC) curve for the Basic Risk Assessment (BRA) scores resulted in an area under the curve (AUC) of 0.8614 (0.7350–0.9877 95% CI) and that for the BRA + Climate Change Assessment (CCA) scores in an AUC of 0.8273 (0.6839–0.9706 95% CI) (Fig. 1a, b)
Youden’s J provided thresholds of 27.5 for the BRA and 34.75 for the BRA + CCA, which were used for calibration of risk outcomes
Summary
The West Siberian Plain is a region characterised by high native biodiversity (Solomeshch 2005) and aboriginal culture conservation value (Klubnikin et al 2000), but threatened by indirect and direct human impacts, including climate change, habitat destruction and non-native (NN) species introductions. This is due to a lack of, or inadequately implemented, regional environmental management (Khitun and Rebristaya 2002). Of the 22 NN species of fish listed for Siberia, 17 have established self-sustaining populations in the Ob basin, which represents ≈ 32% of all fish species
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