Invasive Plant Species Distribution slide image

Invasive Plant Species Distribution

Diversity 2022, 14, 167 12 of 16 correlations between the invasion intensity of local invasive species and plant height, a positive correlation between the invasion intensity of general invasive species and plant cover, and a negative correlation between the invasion intensity of species requiring further observation and plant cover and biomass (Table 4). Table 4. Pearson's correlation coefficients between invasion intensity and plant community character- istics. * indicates significant correlation at the level of 0.05. Number of Invasive Species Biomass of Invasive Species Invasion Level Number of Species Height Plant Cover Biomass 1234512345 -0.09 0.08 -0.13* -0.15* 0.33 * -0.46 * 0.09 -0.05 0.06 -0.10* -0.02 -0.07 -0.01 -0.07 0.07 -0.04 -0.01 -0.06 -0.14* -0.11* -0.07 0.05 -0.13* -0.10 0.10* -0.32 * 0.08 -0.05 -0.01 -0.06 -0.01 -0.02 -0.06 -0.06 0.13* 0.07 0.00 -0.08 -0.12* -0.10 4. Discussion 4.1. Grasslands in Guizhou Province Are Severely Invaded by Non-Native Species Southwest China is an important route for invasive species [30,33,34]. Guizhou Province, located in Southwest China, is an important part of the invasion route and has one of the highest invasion risks [36]. Although previous studies have found that the number of alien invasive plant species in Guizhou Province is lower than that in the southwestern neighboring provinces of Yunnan and Guangxi, the number is close to that of other inland neighboring provinces such as Hunan and Chongqing and exceeds that of inland provinces such as Gansu and Shanxi [30]. This paper provides a catalogue of invasive plants in the grasslands of Guizhou Province of China and quantifies their spatial distribution patterns. Invasive plants (15 families, 41 genera, 49 species) in the grasslands of Guizhou Province accounted for about 30% of the grassland plants in China (41 families, 123 genera, 183 species) [32] and were more numerous than those within the grasslands of three northeastern provinces in China (12 families, 35 genera, 38 species) [60]. However, their number was much lower than that of the invasive plants found within the Serengeti- Mara ecosystem in East Africa (245 species) [61], the Chilean Mediterranean grasslands (66 species) [62], and the Leigong Mountain National Nature Reserve (38 families, 88 genera, 112 species) [44] and close to that of Hongfeng Lake, Baihua Lake, and the Aha Reservoir of Guiyang City in central Guizhou (52 invasive plants from 20 families) [39]. However, it was greater than that of the invasive plants found in other nature reserves of Guizhou Province [40-43]. Fifteen invasive plant species, namely Chromolaena odorata, Erigeron sumatrensis, Bidens pilosa, Ageratum conyzoides, Praxelis clematidea, Ambrosia trifida, Ambrosia artemisiifolia, Solidago canadensis, Parthenium hysterophorus, Ageratina adenophora, Dysphania ambrosioides, Alternanthera philoxeroides, Amaranthus spinosus, Ipomoea cairica, and Ipomoea purpurea, were classified as malignant invasive plants. They all originate from America (including Brazil, Mexico, South America, Tropical America, Central America, and North America), which is in agreement with previous studies reporting that Southern and Northern America were the first and second source areas, respectively, for invasive plant species in China [30]. Species originating from America account for more than 50% of the grassland invasive plants [32], suggesting that species from America should be the focus of invasive plant management policies and practices in the future in Guizhou Province.
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