Soil salinization and/or alkalization is a major constraint to crop production worldwide.Approximately 60% of the cultivated land is affected by salt,over half of which is alkalized.Alkaline soils are characterized by...Soil salinization and/or alkalization is a major constraint to crop production worldwide.Approximately 60% of the cultivated land is affected by salt,over half of which is alkalized.Alkaline soils are characterized by high alkalinity and typically high salinity,which creates a complex saline-alkaline(SA) stress that affects plant growth.Rice cultivation has been accepted as an important strategy for effective utilization of SA land if water is available for irrigation.Nevertheless,as a salt-sensitive plant,rice plants suffer severe SA-induced damage,which results in poor plant growth and grain yield.Various approaches have been employed to improve rice productivity in SA land.Among them,the priming technique has emerged as a powerful method for enhancing SA tolerance in rice plants.In this review,we summarized how SA stress damages rice plants,and then presented how priming treatment can mitigate such damage.展开更多
Soil seed banks can act as a potential seed source for natural revegetation and restoration. However, in a saline-alkaline grassland, it remains unclear how the stages of vegetation succession affect the characteristi...Soil seed banks can act as a potential seed source for natural revegetation and restoration. However, in a saline-alkaline grassland, it remains unclear how the stages of vegetation succession affect the characteristics of soil seed banks and the potential of soil seed banks of different successional stages for vegetation restoration. In this study, seasonal changes of the soil seed bank, and seed production and dispersal dynamics along degradation successional gradients were investigated in a saline-alkaline grassland in Northeast China, where the dominant grass during the 1960 s, Leymus chinensis was replaced with the secondary successional order of Puccinellia chinampoensis, Chloris virgata, and Suaeda salsa, together with bare patches. It was found that the soil seed bank composition varied according to the changing vegetation and had the highest species richness(7–16) in the climax successional stage, but had a low S?rensen similarity(0.22–0.37) with the aboveground vegetation. There was a high seed density of the soil seed bank(21 062–62 166/m2 in August and December) and also high S?rensen similarity index values(0.47–0.60) in the secondary successional stages of P. chinampoensis, C. virgata, and S. salsa. In bare patches, there were many seeds in the soil seed bank and some seedlings also appeared in the aboveground vegetation, indicating the existence of a persistent soil seed bank. Seed density and species richness differed substantially among the different successional stages, which was related to the reproductive characteristics of the standing plants in vegetation communities. Due to the lack of propagules of perennial species, especially the climax species of L. chinensis, in the soil, the successful restoration of the degraded saline-alkaline grassland was not possible. The study proved that in a degraded saline-alkaline grassland dominated by biennial or annual species, the soil seed bank was important for the revegetation of the current dominant plants, but not for the restoration of the original target species. Therefore, it is necessary to induce seeds or other propagules of the target perennial species.展开更多
基金supported by the Science and Technology Innovation Project of Shandong Academy of Agricultural Sciences, China(Grant No.CXGC2022F02)the Agricultural Variety Improvement Project of Shandong Province, China(Grant No.2019LZGC003)。
文摘Soil salinization and/or alkalization is a major constraint to crop production worldwide.Approximately 60% of the cultivated land is affected by salt,over half of which is alkalized.Alkaline soils are characterized by high alkalinity and typically high salinity,which creates a complex saline-alkaline(SA) stress that affects plant growth.Rice cultivation has been accepted as an important strategy for effective utilization of SA land if water is available for irrigation.Nevertheless,as a salt-sensitive plant,rice plants suffer severe SA-induced damage,which results in poor plant growth and grain yield.Various approaches have been employed to improve rice productivity in SA land.Among them,the priming technique has emerged as a powerful method for enhancing SA tolerance in rice plants.In this review,we summarized how SA stress damages rice plants,and then presented how priming treatment can mitigate such damage.
基金Under the auspices of National Basic Research Program of China(No.2015CB150802)National Natural Science Foundation of China(No.41371260,41771058)+1 种基金National Key Research&Development Program of China(No.2016YFC0501200)National Key Basic Survey of Resources(No.2015FY110500)
文摘Soil seed banks can act as a potential seed source for natural revegetation and restoration. However, in a saline-alkaline grassland, it remains unclear how the stages of vegetation succession affect the characteristics of soil seed banks and the potential of soil seed banks of different successional stages for vegetation restoration. In this study, seasonal changes of the soil seed bank, and seed production and dispersal dynamics along degradation successional gradients were investigated in a saline-alkaline grassland in Northeast China, where the dominant grass during the 1960 s, Leymus chinensis was replaced with the secondary successional order of Puccinellia chinampoensis, Chloris virgata, and Suaeda salsa, together with bare patches. It was found that the soil seed bank composition varied according to the changing vegetation and had the highest species richness(7–16) in the climax successional stage, but had a low S?rensen similarity(0.22–0.37) with the aboveground vegetation. There was a high seed density of the soil seed bank(21 062–62 166/m2 in August and December) and also high S?rensen similarity index values(0.47–0.60) in the secondary successional stages of P. chinampoensis, C. virgata, and S. salsa. In bare patches, there were many seeds in the soil seed bank and some seedlings also appeared in the aboveground vegetation, indicating the existence of a persistent soil seed bank. Seed density and species richness differed substantially among the different successional stages, which was related to the reproductive characteristics of the standing plants in vegetation communities. Due to the lack of propagules of perennial species, especially the climax species of L. chinensis, in the soil, the successful restoration of the degraded saline-alkaline grassland was not possible. The study proved that in a degraded saline-alkaline grassland dominated by biennial or annual species, the soil seed bank was important for the revegetation of the current dominant plants, but not for the restoration of the original target species. Therefore, it is necessary to induce seeds or other propagules of the target perennial species.
