First Author: Zhang Huazhan PhD student (Nanjing Agricultural University, College of Resources and Environmental Sciences)
Corresponding Author: Gao Xiang Associate Professor (Nanjing Agricultural University, College of Resources and Environmental Sciences)
Paper DOI: 10.1016/j.watres.2024.122663





System Design
Fig. 1. WG-IoT-MS: (a) system circuit connection diagram, (b) system internal diagram, (c) the monitoring showcase of pond. Copyright 2024, Elsevier Inc.
WG-IoT-MS system integrates various low-cost sensors including pH, water temperature, air temperature, water depth, flow rate, nitrate nitrogen, CO2 sensors. The system uses Arduino Mega2560 as the microcontroller, communicates with OneNET via a GPRS module, and stores data in a cloud database. Additionally, the monitoring system is powered alternately by a 12V battery and an 18W solar panel, ensuring reliable operation in remote areas.。
Optimal Model Selection
Fig. 2. Comparison of the observed and modeled dissolved N2O concentration on different model test sets: (a) RFR, (b) ETR, (c) GBR, (d) SVR-rbf, (e) KNN, (f) BPNN. The blue line shows the linear regression through the data, and the gray line indicates a 1:1 fit. Copyright 2024, Elsevier Inc.
Missing Value Tolerance
Fig. 3. The influence of missing input parameters of ETR and SVR-rbf on prediction accuracy: coefficient of determination (R2). Copyright 2024, Elsevier Inc.
To explore the impact of missing model input parameters on the prediction accuracy of dissolved N2O concentration, this study further compared the performance of ETR and SVR-rbf under six different missing scenarios and four missing proportions (MP = 25%, 50%, 75%, 100%). As the number of missing variables and the missing proportion (MP) increased, differences in prediction accuracy were observed. Although the SVR-rbf showed slightly lower prediction accuracy than ETR on the overall data, its accuracy decreased at a relatively slower rate. Overall, the SVR-rbf outperformed ETR in overall performance, demonstrating stronger prediction stability and robustness against disturbances. Therefore, this study selected SVR-rbf as the optimal algorithm for dissolved N2O concentration.
Applicability of Scenarios

Fig. 4. Prediction of dissolved N2O concentration in different application scenarios based on SVR-rbf: (a) Paddy field, (b) Pond, (c) Lake. Copyright 2024, Elsevier Inc.
When the test data came from lakes ( Fig. 4c), the model performed well (R2 = 0.82, MAPE = 13%). When the test data came from paddy fields (Fig. 4a), R2 slightly decreased, but the prediction performance remained acceptable (R2 = 0.80, MAPE = 13%). However, when the test data came from pond scenarios (Fig. 4b), the prediction performance was relatively poor (R2 = 0.62, MAPE = 15%). This difference may stem from the different aquatic species cultivated in the aquaculture ponds, leading to specific water temperature and pH values.。
Validation of Emission Flux

Fig. 5. Comparison of observed and simulated value of CO2 and N2O emissions: a case study at paddy field sites (B1 and B2) in the study area. Copyright 2024, Elsevier Inc.
Based on WG-IoT-MS, using the dissolved N2O concentration model and the air-water gas exchange model to monitor/simulate CO2 and N2O emissions in the study area and comparing with floating box method results. The results show that the emission flux measurement results of both methods are relatively consistent (R2> 0.7). At different time points, the average absolute errors (MAE) of the simulated values of CO2 and N2O emission flux from the two paddy field monitoring sites were 7.16 mg C/(m2·h) and 2.01 g N/(m2·h). This study successfully achieved low-cost, portable monitoring of CO2 and N2O emission flux, demonstrating acceptable performance.。

This work reports the development and application of an innovative synchronous monitoring system for water quality and greenhouse gas emissions. The research integrates low-cost IoT sensing technology and intelligent algorithms, providing a new approach and technology to overcome the cost and portability issues of traditional monitoring equipment/methods for water quality and greenhouse gases. With the continuous accumulation, updating, and optimization of real measurement data in the later stage, the monitoring accuracy and applicability of this system will continue to improve.
Acknowledgments: PhD student Zhang Huazhan is the first author of the paper, and Associate Professor Gao Xiang is the corresponding author. Professors Zou Jianwen, Ding Yanfeng, Jiang Xiaosan, Xiong Zhengqin, Wang Songhan, Wang Jinyang, Researcher Wang Xuelai from the Remote Sensing Application Center of the Ministry of Ecology and Environment, and Associate Professor Li Wentao from Nanjing University also participated in this research. This research was funded by the National Natural Science Foundation, Jiangsu Province Carbon Peak Carbon Neutrality Technology Innovation Project, Jiangsu Province Agricultural Science and Technology Independent Innovation Project, Nanjing Agricultural University High-Level Talent Introduction Start-up Fund, and Jiangsu Province Graduate Scientific Research Practice Innovation Program.
Zhao Weihua’s Research Directions:
(1) Statistical analysis, modeling, and machine learning (AI) in the fields of environment and dual carbon;
(2) Processes and microorganisms in wastewater treatment
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