Document Type : Research Paper

Author

Assistant Professor, Desert Research Division, Research Institute of Forests and Rangelands, Agricultural Research, Education and Extension Organization (AREEO), Terhran, Iran

10.22092/ijrdr.2026.135837

Abstract

Abstract
 
Background and Objectives
Lakes and wetlands in arid and semi-arid regions play a crucial role in sustaining ecosystems, regulating local climate, controlling dust storms, and preserving biodiversity. Lake Namak, as one of the major evaporitic–saline basins of the Central Iranian Plateau, has experienced a noticeable decline in surface area and increasing instability in its water coverage over recent decades. Reduced hydrological persistence in this lake can intensify dust emissions and weaken regional ecological functions. Despite its importance, long-term analyses based on continuous satellite time series remain limited. Therefore, the objective of this study is to monitor and analyze the spatiotemporal changes in the inundated area of Lake Namak during 1995–2024 using Landsat imagery and the Google Earth Engine platform.
Materials and Methods
In this study, Landsat satellite imagery from Landsat 5, Landsat 7, and Landsat 8 acquired between 1995 and 2024 was used. To harmonize data from different sensors and minimize inconsistencies, surface reflectance products were employed, and cloud and cloud-shadow pixels were masked using standard algorithms. All processing and analyses were conducted within Google Earth Engine, enabling access to a long-term satellite archive and efficient data processing. To extract water bodies, the Normalized Difference Water Index (NDWI) was calculated for each image using the green and near-infrared bands. A threshold value was then determined empirically based on comparisons with false-color composites and visual interpretation, and binary water/non-water maps were generated. Water-covered areas were subsequently calculated at monthly, seasonal, annual, and decadal scales. Trend analysis was performed using time-series assessment and linear regression to determine the direction and magnitude of changes over time. Additionally, the non-parametric Sen’s Slope estimator was applied to obtain a more robust estimate of change rates and to reduce the influence of outliers. To evaluate the stability of the lake’s inundation regime, the Transition and Seasonality layers from the JRC Global Surface Water dataset were analyzed within Google Earth Engine.
Results
Time-series analysis of Landsat imagery revealed a decreasing and unstable trend in the extent of Lake Namak’s inundated area over the past three decades. The mean inundated area in the first decade (1995–2004) was about 154.4 km², decreasing to 48.1 km² in the second decade (2005–2014) and to approximately 41.1 km² in the third decade (2015–2024). Annually, the maximum water extent occurred in 2001 (about 383.6 km²), while the minimum was recorded in 2014 (about 1 km²), indicating strong interannual variability. Trend analysis using linear regression confirmed a significant negative trend, and the negative slope highlighted continuous decline in inundation. Similarly, Sen’s Slope analysis yielded negative annual change rates, indicating a persistent long-term reduction with higher robustness. Seasonal patterns showed that spring exhibited the highest inundation, with about 10% of the lake’s surface containing water, followed by winter with about 5.4%, while summer and autumn displayed minimal inundation. Monthly analysis showed maximum inundation in March, April, and May. The Transition layer indicated that approximately 70.4% of the lake area remained unchanged, while about 15.9% fell into the “new seasonal” class and around 13% into the “seasonal” class, reflecting the expansion of temporary water bodies. Seasonality results showed that more than 71.1% of the lake surface lacked persistent inundation, with most water-covered areas present only one to three months per year.
Conclusion
The findings indicate that Lake Namak has undergone a substantial reduction in surface area and hydrological persistence over the past three decades, with both linear regression and Sen’s Slope confirming the declining trend. The dominance of short-term and seasonal inundation reflects increasing hydrological instability. Continuation of this trend may lead to major environmental consequences, including increased salinity, intensified evaporation, and expansion of dust-source areas. The use of satellite imagery and Google Earth Engine provides an effective framework for long-term monitoring of such dynamic environments.

Keywords

  1. Box, G. (2013). Box and Jenkins: time series analysis, forecasting and control. In A Very British Affair: Six Britons and the Development of Time Series Analysis During the 20th Century(pp. 161-215). London: Palgrave Macmillan UK. 1057/9781137291264
  2. Cao, H., Han, L., & Li, L. (2022). Long-Term Land Surface Water Monitoring in the Yellow River Basin of China Based on Landsat Imagery on the Google Earth Engine. ISPRS Annals of the Photogrammetry, Remote Sensing and Spatial Information Sciences3, 9-16. https://doi.org/10.5194/isprs-annals-V-3-2022-9-2022
  3. Fayzollahpour, M., 2023. Detection of changes in the water extent of Meyghan Wetland using spectral indices (NDWI, MNDWI, and AWEI) and supervised SVM models during the period 1994–2022. Geographical Studies of Arid Regions, 14, 104–119. (In Persian) https://doi.org/10.22034/JARGS.2023.404501.1045
  4. Gorelick, N., Hancher, M., Dixon, M., Ilyushchenko, S., Thau, D., & Moore, R. (2017). Google Earth Engine: Planetary‑scale geospatial analysis for everyone. Remote Sensing of Environment, 202, 18–27. https://doi.org/10.1016/j.rse.2017.06.031
  5. Hassanzadeh, E., Zarghami, M., & Hassanzadeh, Y. (2012). Determining the main factors in declining the Urmia Lake level by using system dynamics modeling. Water resources management, 26(1), 129-145. https://doi.org/10.1007/s11269-011-9909-8
  6. Helsel, D. R., & Hirsch, R. M. (1993). Statistical methods in water resources (Vol. 49). Elsevier.
  7. Hirsch, R. M., Slack, J. R., & Smith, R. A. (1982). Techniques of trend analysis for monthly water quality data. Water resources research18(1), 107-121. https://doi.org/10.1029/WR018i001p00107
  8. (2021). Climate Change 2021: The Physical Science Basis. Cambridge University Press. doi:10.1017/9781009157896.
  9. Jain, S.K., 2001. Development of integrated sediment rating curves using ANNs. Journal of Hydraulic Engineering, 127, 30–37. https://doi.org/10.1061/(ASCE)0733‑9429(2001)127:1(30)
  10. Karami, H. & Sayyadi, Z. 2024. Monitoring the dynamic changes of Miangaran wetland sub-basin using Google Earth Engine system, Journal of of Geographical Data (SEPEHR), 33(130), 161-178.(In Persian) 10.22131/sepehr.2023.1988493.2950
  11. Khoshravesh, M., Abedi-Koupai, J. & Nikzad-Taheri, E., 2016. Detection of trends in hydro-climatological variables using parametric and non-parametric tests in Neka Basin. Journal of Water and Soil Science, 19(74), 1–14. (In Persian)
  12. Li, L., Skidmore, A., Vrieling, A. & Wang, T., 2019. A new dense 18-year time series of surface water fraction estimates from MODIS for the Mediterranean region. Hydrology and Earth System Sciences, 23(7), 3037–3056.https://doi.org/10.5194/hess-23-3037-2019
  13. Madani, K. (2014). Water management in Iran: what is causing the looming crisis?. Journal of environmental studies and sciences, 4(4), 315-328.  https://doi.org/10.1007/s13412-014-0182-z
  14. Khosrobeigi Bozchaloei, S., & Vafakhah, M. (2017). Regional analysis of flow duration curve in Namak Lake basin, Iran. Journal of Watershed Management Research, 7(14), 228–236.https://doi.org/10.29252/jwmr.7.14.236 
  15. McFeeters, S. K. (1996). The use of the normalized difference water index (NDWI) in the delineation of open water features. International Journal of Remote Sensing, 17(7), 1425–1432. https://doi.org/10.1080/01431169608948714
  16. Montaseri, H., Mardani, R. & Reza Khalili. 2025.Evaluation of changes in the water level of Droudzan dam lake using the Normalized Difference Water Index (NDWI), Journal of Environmental Science Studies, 9(4), 9637-9644.(In Persian).  https://doi.org/10.22034/jess.2023.423153.2161
  17. Montgomery, D. C., Peck, E. A., & Vining, G. G. (2021). Introduction to linear regression analysis. John Wiley & Sons.
  18. Mousavi, S. M., Babazadeh, H., Sarai-Tabrizi, M., & Khosrojerdi, A. (2024). Assessment of rehabilitation strategies for lakes affected by anthropogenic and climatic changes: A case study of the Urmia Lake, Iran. Journal of Arid Land. 16(6), 752–767. https://doi.org/10.1007/s40333-024-0019-x
  19. Özvan, H., 2021. Determining the change on the water surface of Lake Namak by using remote sensing methods by water indices (NDWI, MNDWI, AWEI and WRI). Ecological Perspective, 1(1), 37–45.https://doi.org/10.53463/ecopers.20210073
  20. Pekel, J.‑F., Cottam, A., Gorelick, N., & Belward, A. S. (2016). High‑resolution mapping of global surface water and its long‑term changes. Nature, 540(7633), 418–422. https://doi.org/10.1038/nature20584
  21. Hadi, F. H. F., Ebadi, H., & Farhadi, H. (2024). Spatiotemporal Monitoring of Saline Water Body Changes Using Remote Sensing Data with a Focus on Comparing Spectral Indices (Case Study: Lake Urmia).
  22. Rohani, N., Rajaei, T., Mojarradi, B., Jabbari, A., Shafiei-Darabi, S.A. & Heydari-Bani, M., 2021. Climatic analysis of changes in major water resources in Qom Province using satellite data and remote sensing technologies. Quarterly Journal of Environmental Sciences, 19(1): 239–258. (In Persian) https://doi.org/10.52547/envs.33643
  23. Sen, P. K. (1968). Estimates of the regression coefficient based on Kendall’s tau. Journal of the American Statistical Association, 63(324), 1379–1389. 1080/01621459.1968.10480934
  24. Sheikh‑Assadi, A., Khademi, M., & Ahmadi, R. 2019. Monitoring the Lut Desert lake using Landsat and Sentinel‑2 imagery and hydrological pattern analysis. Geography and Environment Journal, 23(4), 70–88. (In Persian) 10.22034/RSGI.2025.66297.1127
  25. Sheikh, Z., Yazdani, M. R., & Moghaddam Nia, A. (2020). Spatiotemporal changes of 7-day low flow in Iran’s Namak Lake Basin: impacts of climatic and human factors. Theoretical and Applied Climatology, *139*(1), 57–73. https://doi.org/10.1007/s00704-019-02946-3
  26. Shumway, R. H., & Stoffer, D. S. (2006). Time series analysis and its applications: with R examples. New York, NY: Springer New York. 1007/0-387-36276-2
  27. Solaimani, K. , Darvishi, S. and Shokrian, F. 2022. Accuracy assessment of remote sensing methods for extraction and monitoring of Zrebar Lake, Iran.Journal of Ecohydrology9(3), 505-516. (In Persian) doi: 10.22059/ije.2023.342056.1632
  28. Taheri Dehkordi, A., Valadan Zoej, M.J., Ghasemi, H., Jafari, M. & Mehran, A., 2022. Monitoring long-term spatiotemporal changes in Iran surface waters using Landsat imagery. Remote Sensing, 14(18), 4491. https://doi.org/10.3390/rs14184491
  29. United Nations Environment Programme. (2019). Global environment outlook—GEO-6: Healthy planet, healthy people. United Nations Environment Programme. 1017/978110862714
  30. Vahabi, J., 2016. Flood risk zoning using remote sensing and GIS techniques in the Taleghan watershed, Master’s thesis, Tarbiat Modares University. (In Persian)
  31. Vermote, E., Justice, C., Claverie, M., & Franch, B. (2016). Preliminary analysis of the performance of the Landsat 8/OLI land surface reflectance product. Remote Sensing of Environment, 185, 46–56. https://doi.org/10.1016/j.rse.2016.04.008
  32. Voss, K. A., Famiglietti, J. S., Lo, M., De Linage, C., Rodell, M., & Swenson, S. C. (2013). Groundwater depletion in the Middle East from GRACE with implications for transboundary water management in the Tigris‐Euphrates‐Western Iran region. Water resources research, 49(2), 904-914. 1002/wrcr.20078
  33. Woolway, R. I., Kraemer, B. M., Lenters, J. D., Merchant, C. J., O’Reilly, C. M., & Sharma, S. (2020). Global lake responses to climate change. Nature reviews earth & environment, 1(8), 388-403. 1038/s43017-020-0067-5
  34. Xu, H. (2006). Modification of normalized difference water index (NDWI) to enhance open water features in remotely sensed imagery. International Journal of Remote Sensing, 27(14), 3025–3033. https://doi.org/10.1080/01431160600589179 1080/0143116060058917
  35. Yao, A.W. & Chi, S.C., 2004. Analysis and design of a Taguchi–Grey based electricity demand predictor for energy management systems. Energy Conversion and Management, 45(7), 1205–1217. https://doi.org/10.1016/S0196‑8904(03)00221‑1
  36. Yao, F., Livneh, B., Rajagopalan, B., Wang, J., Crétaux, J. F., Wada, Y., & Berge-Nguyen, M. (2023). Satellites reveal widespread decline in global lake water storage. Science, 380(6646), 743-749.1126/science.abo2812
  37. Abtahi, M., Saif, A., & Khosroshahi, M. (2012). Investigation of the last Quaternary climate from the geomorphic evidence in Namak Lake basin, Central Iran. Journal of Geography and Regional Planning, 5(3), 93–107. https://doi.org/10.5897/JGRP11.124
  38. Yousefi, H., Torabi Podeh, H., Haghizadeh, A., Samadi, A., Arshiya, A. & Yarahmadi, Y.2022. Monitoring the Changes of Zaribar Lake in Kurdistan Using Spectral Indicators and Landsat Images in Google Earth Engine System, Journal of Hydrogeology, 6(2), 30-41. magiran.com/p2425741 (In Persian) 10.22034/HYDRO.2022.12845
  39. Zhu, Z. & Woodcock, C.E., 2014. Continuous change detection and classification of land cover using all available Landsat data. Remote Sensing of Environment, 144, 152–171. https://doi.org/10.1016/j.rse.2014.01.011
  40. Nodefarahani, M., Aradpour, S., Noori, R., & others. (2020). Metal pollution assessment in surface sediments of Namak Lake, Iran. Environmental Science and Pollution Research , 27, 45639–45649. https://doi.org/10.1007/s11356-020-10298-1
  41. Rahimi, M., & Khosravi, M. (2025). Analysis of Wind Regime and Sand Transport Potential in the Marginal Ergs of the Namak Lake, Central Iran. Arid Regions Geographic Studies , 16(60), 1–20. https://doi.org/10.30495/jargs.2025.191973