Arid and semiarid regions account for ~ 40% of the world’s land area. Rivers and lakes in these regions provide sparse, but valuable, water resources for the fragile environments; and play a vital role in the development and sustainability of local societies. During the late 1980s, the climate of arid and semiarid northwest China dramatically changed from “warm-dry” to “warm-wet”. Understanding how these environmental changes and anthropogenic activities affect water quantity and quality is critically important for protecting the aquatic ecosystem and determining the best use of freshwater resources. Lake Bosten is the largest inland freshwater lake in NW China and has experienced inter-conversion processes between freshwater and brackish status. Herein, we explored the long-term water level and salinity trends in Lake Bosten from 1958 to 2019. During the past 62 years, Lake Bosten’s water level and salinity exhibited “W” and “M” patterns. Partial least squares path modeling (PLS-PM) suggested that the decreasing water level and salinization during 1958–1986 were mainly caused by anthropogenic activities, while the variations in water level and salinity during 1987–2019 were mainly affected by climate change. The transformation of anthropogenic activities and climate change is beneficial for sustainable freshwater management in Lake Bosten Catchment. Our findings highlight the benefit of monitoring aquatic environmental changes in arid and semi-arid regions over the long-term for the purpose of fostering a balance between socioeconomic development and ecological protection of the lake environment.

The diversity of phytoplankton is fundamental to the health of aquatic ecosystems. Those commonly used diversity indices (e.g., Shannon-weiner diversity index, etc.) were assumed that a uniform distribution was the optimal status of phytoplankton taxa in aquatic system during the assessment of these indices. We discovered that the relative abundance of phytoplankton within an aquatic ecosystem can be fitted with exponential distribution, suggesting that the exponential distribution was the intrinsic and inherent distribution of phytoplankton communities. Through mathematical derivation, taxa capacity (N), competition coefficient (k), critical relative abundance of extinction (a), degree of monopoly, and the residual sum of squares of the phytoplankton community can be obtained to provide a greater insight into phytoplankton diversity. Our results highlight a new methodology based on the above indices has been developed to provide a better insight into the phytoplankton community diversity. It will also help to evaluate the aquatic system ecological health.