چكيده لاتين
Water is one of the most vital elements for life, and without it, healthy living is impossible; therefore, it must be consumed in sufficient quantities. In the past year, climate changes and global warming have restricted access to water resources, creating broad challenges for the environment and human health. Given these challenges, quality management of water for the optimal use of these vital resources has become an undeniable necessity. Adopting approaches for qualitative monitoring, reducing water losses, and developing data-driven qualitative management policies can help mitigate the effects of climate change and support sustainable living. Zayandeh Roud Dam is one of the critical and strategic dams in Iran, located in Isfahan Province, and holds significant importance.
The main objective of this study is to monitor and model water quality in order to track pollution and changes in the qualitative parameters of water in the Zayandeh Roud Dam reservoir. In this research, using surface earth observation imagery captured by the Sentinel-2 satellite at two time points, a numerical model was developed using an artificial neural network under supervised learning on a machine learning platform. This modeling is based on finding the relationship between the energy reflectance behavior from the lake surface of the reservoir and the physical changes of the lake surface, where satellite data captured in 13 different bands are considered as model inputs and the qualitative parameter as the output. In the next stage, in addition to satellite data, environmental air temperature and reservoir water level parameters under four different scenarios were treated as inputs to determine the impact of these two parameters on the modeling. The collected data are observations taken at three points at a depth of one meter. These data were collected non-uniformly across 33 sampling events from the year 2018 to 2023 and include seven qualitative parameters: Chlorophyll-a, Dissolved and Suspended Disks, Organic and Inorganic Colloids, Electrical Conductivity, Nitrate, and a Acid-Base Index. The modeling was conducted in two modes: in the first series, all satellite data were used, and in the second series, six best bands that show higher correlation with the target qualitative parameter were used. In this study, missing data and outliers were removed due to non-regular sampling.
Assessments in the modeling show that when all data are entered, the performance metrics R², RMSE, and NSE for Chlorophyll-a are, on average, 0.920, 0.391 micrograms per liter, and 0.959 for training data, and 0.893, 0.275 micrograms per liter, and 0.959 for testing data, respectively. Similarly, for DS, training results are 0.951, 0.424 meters, and 0.975, and testing results are 0.934, 0.472 meters, and 0.967. For Turbidity, training results are 0.923, 2.442 NTU, and 0.961, and testing results are 0.911, 3.754 NTU, and 0.955. For TDS, training results are 0.908, 8.317 mg/L, and 0.953, and testing results are 0.889, 8.116 mg/L, and 0.943. For EC, training results are 0.881, 17.905 μS/cm, and 0.939, and testing results are 0.854, 20.915 μS/cm, and 0.924. For Nitrate, training results are 0.877, 18.538 mg/L, and 0.936, and testing results are 0.854, 19.594 mg/L, and 0.924. For the PH, training results are 0.912, 0.799, and 0.954, and testing results are 0.864, 0.811, and 0.929. Furthermore, in modeling with optimized input data, the parameters Chlorophyll-a, Turbidity, Nitrate, and EC, on average, better results, while DS, TDS, and PH relatively weaker results on average.
Following this, the effects of temperature and `r level in the modeling were examined under four different scenarios, but no meaningful results were obtained to identify the influence of these two parameters in the modeling.