Lakes provide critical resources for humankind, such as drinking water, food, biodiversity, and transportation. The dual effects of climate change (e.g., shifts in temperature and precipitation regimes) and human activities significantly alter lake environments (Adrian et al., 2009;Bennett et al., 2001). Widespread increases in lake temperature (O'Reilly et al., 2015), cyanobacterial blooms (Huisman et al., 2018), and deoxygenation (Jane et al., 2021) have been reported in lakes throughout the world. In China, rapid economic development and major land-use changes have influenced lakes. In 2007, a drinking water crisis in Wuxi city resulted from the cyanobacterial blooms in Lake Taihu (Guo, 2007). Zhang et al. (2020) have shown that lakes in China had degraded optical conditions. Recently, water quality is improving (Ma et al., 2020) and some lakes are becoming more transparent (Liu et al., 2020), with large investments in the restoration of lakes and their watersheds. However, Song et al. ( 2021) reported intensified cyanobacterial blooms in China lakes. Though several studies monitored individual water quality indicators (Liu et al., 2020;Song et al., 2021), a comprehensive assessment of the prevalence of shifts in lake conditions and relevant drivers needs further investigation.Lakes range widely in apparent color owing to interactions among suspended and dissolved materials and sunlight (Plass et al., 1978). Lake color is related to productivity, water quality, and ecological state (Topp et al., 2021). For example, high suspended solids can be related to brown/yellow colors (Leech et al., 2018), more phytoplankton results in greener water (Wilkinson et al., 2022), and increased colored dissolved organic matter (CDOM) has led