Abstract
One of the most significant applications of remote sensing data is to prepare land use and land cover (LULC) maps. LULC maps are always affected by seasonality and a single LULC map of a particular month is prepared to represent a year in most of the research, especially in change detection research. This does not represent the real view of the landscape because the seasonal variation of different LULC types is always overlooked. Considering the issue, the current method aims to solve the problem by incorporating seasonal LULC using the raster overlay method to remove the seasonality effect on LULC classification. To apply this method, a minimum of two seasonal LULC maps is required for a single study year. The map needs to overlay and then reclassify according to the stable and rotational LULC pattern of the study area. This method will replicate the actual LULC pattern of a study area from satellite images. Summary of the method is as follows:
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LULC of each season was classified using image classification technique.
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LULC of each seasons are coded and combined using overlay technique.
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Combined map is reclassified to prepare the actual LULC map.
Keywords: Geographic information systems, Land use and land cover classification, Seasonality, Overlay, Actual LULC
Method name: Actual LULC modelling by incorporating seasonality effect
Graphical abstract
Specifications Table
Subject area: | Environmental Science |
More specific subject area: | GIS and Remote Sensing Application |
Name of your method: | Actual LULC modelling by incorporating seasonality effect |
Name and reference of original method: | NA |
Resource availability: | Equipment: Seasonal satellite images and image classification toolset Data: Open source Landsat images are available at USGS earth explorer (https://earthexplorer.usgs.gov/) Processed Data will be made available on request. Software: AcrMap 10.5 Hardware requirement for software: CPU Speed 2.2 GHz minimum; Hyper-threading (HHT) or Multi-core recommended; Memory/RAM minimum 4 GB, recommended 8 GB; Disk space minimum: 4 GB recommended: 6 GB or higher; Display properties 24-bit colour depth |
Method details
Seasonality significantly affects the accuracy of LULC maps extracted from satellite imageries. The effect of seasonality on LULC maps has been studied and emphasis was given to comparing and improving the accuracy of the classified maps [1], [2], [3]. Spectral-temporal mixing of cloud-free satellite images was also been applied to reduce the seasonality effect and to improve map accuracy [[4], [5]]. Another emphasis has been given to selecting the best season to delineate LULC of a particular environmental condition or extracting a particular feature [[5], [6]].
LULC has significant application in several scientific studies [7,8] such as LULC change analysis [9], LST analysis and its impact analysis [10], hazard assessment [11,12], climate change and impact analysis [13,14], large-scale environmental monitoring [15,16] and environmental degradation assessment [17,18] etc. Besides, LULC and LULC change maps are the major input variables of many models such as climate change models [19], [20], [21], hazard assessment models [22] and hydrological models [23], [24], [25]. The accurate LULC helps take proper action for sustainable environmental management, hazard mitigation and climate change policy development [7,8]. LULC plays a key role in the sustainable management and development of urban and rural areas, agricultural land, watersheds or wetlands, river banks, forests etc. [2].
However, preparing an accurate LULC always depends on the quality of the satellite image. Cloud-free satellite image provides more accurate LULC of a region. Researchers always emphasized taking a cloud-free image and mapped LULC of a single season which is considered as the representative of a single year [6,9,26,27]. This type of classified map, though it has higher accuracy, is not appropriate for field application as some of the seasonally affected features (vegetation, water and bare land) are ignored in this type of classification. Due to the cloud effect, cloud-free satellite data may be available for two or three seasons for LULC classification. The seasonal change affects the extent of the water body and alters the pattern of vegetation cover which ultimately affects the extent of built-up areas and bare land. To get an accurate LULC map of a single year it needs to consider the seasonally varied landscape features such as seasonally altering water body, vegetation type and bare land characteristics. Change in the built-up areas within this short time is negligible and it can be considered a fixed amount.
In this method, seasonal variation of LULC is considered and from the combination of LULC of three seasons a final LULC map is prepared using ArcMap 10.5 software. This type of classification will produce an accurate LULC of a given year and will be very useful for scientific application. The method is discussed below.
Data acquisition and source
Landsat 8 OLI data was acquired for three seasons of post-monsoon, winter and summer for the study area. In Bangladesh, cloud-free Landsat images are available from November to March. During April and May, though they are the months of the summer season, sometimes cloud affects the Landsat images. So, images of the three seasons are collected following the months and seasons shown in Table 1.
Table 1.
Description of the acquired satellite image.
Seasons and Corresponding Months | Acquisition Date | Path and Row |
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Post-monsoon (October to November) | 2021/11/19 | 136 and 45 |
Winter (December to February) | 2022/01/08 | 136 and 45 |
Summer (March to May) | 2022/03/21 | 136 and 45 |
The LULC is prepared in two steps: in the first step, LULC of three seasons are prepared and the LULCs are coded according to category. In the second step, the three maps are combined and reclassified according to the combination of the code.
LULC classification for single season
A common, widely accepted and intensively used LULC classification method is the Maximum Likelihood classification method [28,29]. LULC of the three seasons are classified using the Maximum Likelihood classification technique. To classify the LULC maps, training samples are taken for individual images of each season.
The classified maps are shown in Fig. 1 and the obtained accuracy of the maps is shown in Table 2. The graphical distribution of LULC maps shows that types of LULC vary according to the variation of the season (Fig. 1). The accuracy of the classified maps are measured using commonly used statistical indices of user accuracy, producer accuracy overall accuracy and kappa coefficient [30], [31], [32]. The accuracy (Overall Accuracy and Kappa Coefficient) of the LULC maps and the accuracy of the LULC types (User Accuracy and Producer Accuracy) of the LULC maps also vary according to the variation of the seasons (Table 2).
Fig. 1.
Seasonal land use and land cover map of the study area.
Table 2.
Accuracy of the classified maps (PA = Producer Accuracy; UA = User Accuracy; OA = Overall Accuracy; Kc = Kappa Coefficient).
Season | Code | LULC Type | PA | UA | OA | Kc |
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Post-monsoon | 1 | Water body | 1.00 | 0.92 | 0.96 | 0.95 |
2 | Vegetation | 0.97 | 1.00 | |||
3 | Built up | 1.00 | 0.93 | |||
4 | Bare land | 0.89 | 1.00 | |||
Winter | 1 | Water body | 1.00 | 0.82 | 0.92 | 0.89 |
2 | Vegetation | 0.88 | 0.87 | |||
3 | Built up | 1.00 | 1.00 | |||
4 | Bare land | 0.83 | 1.00 | |||
Summer | 1 | Water body | 1.00 | 0.92 | 0.94 | 0.92 |
2 | Vegetation | 0.94 | 0.87 | |||
3 | Built up | 0.97 | 1.00 | |||
4 | Bare land | 0.86 | 0.98 |
Combining the LULC maps by simple overlay method
The LULC types of maps are coded to identify the changes or rotation of the LULC types around the seasons. Codes of the LULC categories are given in Table 1. Using a simple overlay technique of ArcMap 10.5 software the maps are combined into a single map. This type of technique also can be applied to detect the change in LULC between two years. In this case, three years are combined to observe the rotational LULC to demarcate and reclassify them (Fig. 2.a and b).
Fig. 2.
a) Overlay of the LULC maps of the three seasons, and b) pixel value of the final map derived from seasonal map overlay (Figure legend: 1=water, 2=vegetation, 3= built up and 4= bare land).
Reclassification of combined map
After the combining the three maps, the combined map got three codes from the three seasons as shown in Table 3 and Fig. 2.a and b. The combined map is now reclassified following rotations of the codes. Such as when the code is 111 this means the area was water body in the three consecutive seasons. So this is considered as stable water body. When the code is 121 it is considered as seasonal water body. In this type of classification, maximum number of similar rotation is considered as final LULC class such as water rotated two times. Again, the code 212 is considered seasonal vegetation as in one season it drowned under water but most of the times dominated by Vegetation cover. When three different categories aroused, it is carefully interpreted visually from the three consecutive images and final decision was made (Fig. 3). The code 324 is considered as mixed urban as this feature is dominant in the urban areas and the spectral signature changes during summer identified it as bare land. The common assumption followed during visual interpretation was the association, proximity, colour depth and the mixture pattern of the class. A manual and the assumptions for visual interpretation are added in the Appendix. The visualization of the different codes and corresponding false colour combinations can also be found there.
Table 3.
Reclassification of the combined map (1= Water body, 2= Vegetation, 3= Built up and 4= Bare land).
Post-Monsoon | Winter | Summer | Combined | Final LULC Type |
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1 | 1 | 1 | 111 | Water (Stable) |
2 | 2 | 2 | 222 | Vegetation (Stable) |
1 | 1 | 2 | 112 | Seasonal Water Body |
1 | 2 | 1 | 121 | Seasonal Water Body |
2 | 1 | 1 | 211 | Seasonal Water Body |
1 | 1 | 3 | 113 | Seasonal Water Body |
3 | 1 | 1 | 311 | Seasonal Water Body |
1 | 1 | 4 | 114 | Seasonal Water Body |
1 | 2 | 4 | 124 | Seasonal Water Body |
1 | 3 | 4 | 134 | Seasonal Water Body |
1 | 4 | 1 | 141 | Seasonal Water Body |
4 | 1 | 1 | 411 | Seasonal Water Body |
3 | 1 | 2 | 312 | Seasonal Water Body |
3 | 2 | 1 | 321 | Seasonal Water Body |
2 | 1 | 2 | 212 | Seasonal Vegetation |
2 | 2 | 1 | 221 | Seasonal Vegetation |
2 | 2 | 3 | 223 | Seasonal Vegetation |
2 | 3 | 2 | 232 | Seasonal Vegetation |
3 | 2 | 2 | 322 | Seasonal Vegetation |
1 | 2 | 2 | 122 | Seasonal Vegetation |
2 | 2 | 4 | 224 | Seasonal Vegetation |
2 | 3 | 4 | 234 | Seasonal Vegetation |
2 | 4 | 2 | 242 | Seasonal Vegetation |
4 | 2 | 2 | 422 | Seasonal Vegetation |
3 | 1 | 3 | 313 | Seasonal Built Up |
3 | 3 | 1 | 331 | Seasonal Built Up |
2 | 3 | 3 | 233 | Seasonal Built Up |
3 | 2 | 3 | 323 | Seasonal Built Up |
3 | 3 | 2 | 332 | Seasonal Built Up |
3 | 3 | 4 | 334 | Seasonal Built Up |
3 | 4 | 3 | 343 | Seasonal Built Up |
4 | 3 | 3 | 433 | Seasonal Built Up |
1 | 4 | 4 | 144 | Seasonal Bare Land |
4 | 1 | 4 | 414 | Seasonal Bare Land |
4 | 4 | 1 | 441 | Seasonal Bare Land |
2 | 4 | 4 | 244 | Seasonal Bare Land |
4 | 2 | 4 | 424 | Seasonal Bare Land |
4 | 4 | 2 | 442 | Seasonal Bare Land |
3 | 4 | 4 | 344 | Seasonal Bare Land |
4 | 3 | 4 | 434 | Seasonal Bare Land |
4 | 4 | 3 | 443 | Seasonal Bare Land |
2 | 1 | 4 | 214 | Seasonal Water Body |
3 | 4 | 1 | 341 | Seasonal Water Body |
4 | 1 | 2 | 412 | Mixed Water |
1 | 4 | 2 | 142 | Mixed Water |
2 | 4 | 1 | 241 | Mixed Water |
1 | 4 | 3 | 143 | Mixed Water |
4 | 1 | 3 | 413 | Mixed Water |
2 | 4 | 3 | 243 | Mixed Vegetation |
3 | 2 | 4 | 324 | Mixed Urban |
3 | 4 | 2 | 342 | Mixed Urban |
4 | 2 | 3 | 423 | Mixed Urban |
4 | 3 | 2 | 432 | Mixed Urban |
3 | 1 | 4 | 314 | Coastal Sand |
3 | 3 | 3 | 333 | Built up (Stable) |
4 | 4 | 4 | 444 | Bare land (Stable) |
Fig. 3.
Reclassification of Mixed Urban and Seasonal Vegetation by visual interpretation.
Prepared actual LULC map
The final map has twelve types of LULC namely Water (Stable), Seasonal Water, Seasonal Vegetation, Mixed Water, Seasonal Bare land, Vegetation (Stable), Seasonal Built-up, Mixed Vegetation, Coastal Sand, Mixed Urban, Built-up (Stable) and Bare land (Stable) (Fig. 4). The characteristics of LULC classes and the measured area are shown in Table 4.
Fig. 4.
The final LULC map of the study area reclassified from the combined map.
Table 4.
Characteristics of the final LULC types and the measured area of the LULC types.
LULC | Area | Characteristics |
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Water (Stable) | 1.7 | Perennial Water remains same types in all seasons |
Seasonal Water | 0.8 | Changes in two seasons and finally returns to the previous class |
Seasonal Vegetation | 19.6 | Changes in two seasons and finally returns to the previous class. |
Mixed Water | 0.14 | Converts into three category around the seasons. |
Seasonal Bare land | 21.8 | Changes in two seasons and finally returns to the previous class. |
Vegetation (Stable) | 50.0 | Actual Vegetation Cover remains in all seasons |
Seasonal Mixed Built up | 13.9 | Vegetation Cover exposed during another season. Bare land detected as built up in another season. |
Mixed Vegetation | 0.09 | Converts into three category around the seasons but mostly vegetation dominant or located along vegetation cover. |
Coastal Sand | 0.5 | Sands in the coast or in river bank, sometimes classified as built up areas |
Mixed Urban | 4.5 | Converts into three categories around the seasons located in urban areas or along built up areas. |
Built up (Stable) | 40.0 | Actual Built up area remains in all seasons |
Bare land (Stable) | 16.6 | Actual Bare land remains in all seasons |
Merits of the proposed classification
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This type of classification provides pixel-based LULC maps.
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This classification process can be done in any GIS software which supports the raster overlay method or has a raster calculator.
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The method is simple to handle and no difficult mathematical expertise is required. Anyone who knows the LULC change detection method can easily understand and apply this method.
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Reduces the complexity of spectral-mixing of seasonal images or mixing of multi-sensor data
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Reduces classification time and cost.
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Produces actual LULC of a given year considering the dynamics of LULC
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The method will be very helpful for actual LULC change detection of a given area
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Provides actual LULC information on the study area which will be very helpful for policy or decision-making
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In agricultural areas, this classification will help to demarcate rotational agricultural land
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In forestry, it will help to demarcate the seasonal vegetation and its changing pattern over the season
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The phenology of LULC in any environmental condition can be detected using this method.
Demerits/Limitations of the proposed classification
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Complexity is aroused during the reclassification of the mixed pixels and it requires visual interpretation using all the raw satellite images
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Sometimes it becomes tough to categorize the mixed pixels due to the similarity in the spectral signature of the neighbouring pixels.
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A clear knowledge of the study area is required
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Need to depend on the accuracy of each season's map.
Further replication of the proposed classification
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Other LULC classification algorithms can be used to prepare a more accurate LULC map of each season such as random forest, KNN, ANN etc. this type of classification algorithm will produce better accuracy of the primary LULC maps which will ultimately increase the actual representation of the LULC pattern.
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At least two seasons should be considered to get the real LULC of the study area. The inclusion of more seasons will increase the reliability of the map. The inclusion of more seasons will provide more LULC classes which will be more representative of reality.
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The method can be used in other types of satellite data such as Landsat 7 EMT+, Landsat 4/5, sentinel, MODIS, ASTER etc. Similar satellite images of different seasons will produce better results. If a different satellite sensor is used, rescaling and re-sampling, and geo-referencing of the image should be done to make the pixels comparable.
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Application of machine or deep learning algorithm during preparation of each season's LULC map will subsequently increase the reliability and acceptability of the final map.
Limitation of the current research
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Only one classification method of Maximum Likelihood is used for LULC preparation of a season.
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Some areas containing sand cover along the coast produce complexity in reclassification. They are classified as built-up in the summer season water bodies during the post-monsoon season and bare land during the winter season. This type of mixing also occurs in dense urban areas. Demarcation of this type of category produces errors.
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Only one urban area is classified considering the seasonal rotation of LULC but other environmental settings are not tested.
Remarks
A simple and easy-to-handle method of actual LULC preparation from seasonal satellite data is presented. The classification method incorporates seasonal LULCs to prepare a final LULC map of a given study area where the seasonal rotational land cover of seasonal phenology of land cover is considered. Removing the seasonality effect, the method properly classifies the LULC of a given area. The method will be very helpful for scientific research of LULC mapping and change detection and other scientific research where the true representation of LULC is of significant importance. Though there are some limitations in the current research the method can be replicated for other environmental conditions. Any GIS software that supports raster overlay or raster calculator can be used to replicate the method. Satellite data from other sensors can also be engaged to classify actual LULC maps.
Ethics statements
Not Applicable
CRediT authorship contribution statement
Md. Sharafat Chowdhury: Conceptualization, Methodology, Software, Visualization, Writing – original draft, Writing – review & editing.
Declaration of Competing Interest
The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.
Acknowledgments
No funding received for this research.
Footnotes
Supplementary material associated with this article can be found, in the online version, at doi:10.1016/j.mex.2023.102472.
Appendix. Supplementary materials
Data availability
Data will be made available on request.
References
- 1.Sharma D.P., Bren L. Effect of seasonal spectral variations on land cover classification. J. Indian Soc. Remote Sens. 2005;33:203–209. doi: 10.1007/BF02990036. [DOI] [Google Scholar]
- 2.Sinha P., Kumar L., Reid N. Seasonal variation in land-cover classification accuracy in a diverse region. Photogrammetr. Eng. Remote Sens. 2012;78(3):271–280. [Google Scholar]
- 3.Yimer A.K., Haile A.T., Hatiye S.D., Azeref A.G. Seasonal effect on the accuracy of Land use/Land cover classification in the Bilate Sub-basin, Abaya-Chamo Basin, Rift valley Lakes Basin of Ethiopia. Ethiopian J. Water Sci. Technol. 2020;3:23–50. doi: 10.59122/134C842. [DOI] [Google Scholar]
- 4.Nasiri V., Deljouei A., Moradi F., Sadeghi S.M.M., Borz S.A. Land use and land cover mapping using Sentinel-2, Landsat-8 Satellite Images, and Google Earth Engine: a comparison of two composition methods. Remote Sens. (Basel) 2022;14(9):1977. doi: 10.3390/rs14091977. [DOI] [Google Scholar]
- 5.Dawelbait M., Dal Ferro N., Morari F. Using landsat images and spectral mixture analysis to assess drivers of 21-Year LULC changes in Sudan. Land Degradat. Dev. 2017;28(1):116–127. [Google Scholar]
- 6.Karila K., Matikainen L., Litkey P., Hyyppä J., Puttonen E. The effect of seasonal variation on automated land cover mapping from multispectral airborne laser scanning data. Int. J. Remote Sens. 2019;40(9):3289–3307. doi: 10.1080/01431161.2018.1528023. [DOI] [Google Scholar]
- 7.Zhu Z., Woodcock C.E. Continuous change detection and classification of land cover using all available Landsat data. Remote Sens. Environ. 2014;144:152–171. [Google Scholar]
- 8.Zhang C., Li X. Land use and land cover mapping in the era of big data. Land (Basel) 2022;11(10):1692. doi: 10.3390/land11101692. [DOI] [Google Scholar]
- 9.Seyam M.M.H., Haque M.R., Rahman M.M. Identifying the land use land cover (LULC) changes using remote sensing and GIS approach: a case study at Bhaluka in Mymensingh, Bangladesh. Case Stud. Chem. Environ. Eng. 2023;7 doi: 10.1016/j.cscee.2022.100293. [DOI] [Google Scholar]
- 10.Jiang J., Tian G. Analysis of the impact of land use/land cover change on land surface temperature with remote sensing. Procedia Environ. Sci. 2010;2:571–575. doi: 10.1016/j.proenv.2010.10.062. [DOI] [Google Scholar]
- 11.Vu V.T., Nguyen H.D., Vu P.L., Ha M.C., Bui V.D., Nguyen T.O., Hoang V.H., Nguyen T.K.H. Predicting land use effects on flood susceptibility using machine learning and remote sensing in coastal Vietnam. Water Pract. Technol. 2023 doi: 10.2166/wpt.2023.088. [DOI] [Google Scholar]
- 12.Viet Du Q.V., Nguyen H.D., Pham V.T., Nguyen C.H., Nguyen Q.H., Bui Q.T., Doan T.T., Tran A.T., Petrisor A.I. Deep learning to assess the effects of land use/land cover and climate change on landslide susceptibility in the Tra Khuc river basin of Vietnam. Geocarto Int. 2023 doi: 10.1080/10106049.2023.2172218. [DOI] [Google Scholar]
- 13.Dias F.T., Mazon G., Cembranel P., Birch R., de Andrade Guerra J.B.S.O. Land use and global environmental change: an analytical proposal based on a systematic review. Land (Basel) 2022;12(1):115. doi: 10.3390/land12010115. [DOI] [Google Scholar]
- 14.Jia S., Yang C., Wang M., Failler P. Heterogeneous impact of land-use on climate change: study from a spatial perspective. Front. Environ. Sci. 2022;10:510. doi: 10.3389/fenvs.2022.840603. [DOI] [Google Scholar]
- 15.Yourek M., Liu M., Scarpare F.V., Rajagopalan K., Malek K., Boll J., Huang M., Chen M., Adam J.C. Downscaling global land-use/cover change scenarios for regional analysis of food, energy, and water subsystems. Front. Environ. Sci. 2023;11 doi: 10.3389/fenvs.2023.1055771. [DOI] [Google Scholar]
- 16.Kilic S., Evrendilek F., Berberoglu S.Ü.H.A., Demirkesen A.C. Environmental monitoring of land-use and land-cover changes in a Mediterranean region of Turkey. Environ. Monit. Assess. 2006;114:157–168. doi: 10.1007/s10661-006-2525-z. [DOI] [PubMed] [Google Scholar]
- 17.Rahman M.M., Szabó G. Impact of land use and land cover changes on urban ecosystem service value in Dhaka. Bangladesh. Land. 2021;10(8):793. doi: 10.3390/land10080793. [DOI] [Google Scholar]
- 18.Kgaphola M.J., Ramoelo A., Odindi J., Mwenge Kahinda J.M., Seetal A.R., Musvoto C. Impact of land use and land cover change on land degradation in rural semi-arid South Africa: case of the greater Sekhukhune district municipality. Environ. Monit. Assess. 2023;195(6):710. doi: 10.1007/s10661-023-11104-0. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 19.Barati A.A., Zhoolideh M., Azadi H., Lee J.H., Scheffran J. Interactions of land-use cover and climate change at global level: how to mitigate the environmental risks and warming effects. Ecol. Indic. 2023;146 doi: 10.1016/j.ecolind.2022.109829. [DOI] [Google Scholar]
- 20.Pongratz J., Schwingshackl C., Bultan S., Obermeier W., Havermann F., Guo S. Land use effects on climate: current state, recent progress, and emerging topics. Curr. Clim. Change Rep. 2021:1–22. doi: 10.1007/s40641-021-00178-y. [DOI] [Google Scholar]
- 21.Pielke R.A., Sr, Pitman A., Niyogi D., Mahmood R., McAlpine C., Hossain F., Goldewijk K.K., Nair U., Betts R., Fall S., Reichstein M. Land use/land cover changes and climate: modeling analysis and observational evidence. Wiley Interdiscip. Rev. Clim. Change. 2011;2(6):828–850. doi: 10.1002/wcc.144. [DOI] [Google Scholar]
- 22.Houet T., Gremont M., Vacquié L., Forget Y., Marriotti A., Puissant A., Bernardie S., Thiery Y., Vandromme R., Grandjean G. Downscaling scenarios of future land use and land cover changes using a participatory approach: an application to mountain risk assessment in the Pyrenees (France) Reg. Environ. Change. 2017;17:2293–2307. [Google Scholar]
- 23.Hosseini M., Ashraf M.A. Application of the SWAT Model for Water Components Separation in Iran. Springer Hydrogeology. Springer; Tokyo: 2015. Application of hydrological models related to land use land cover change. [DOI] [Google Scholar]
- 24.Bal M., Dandpat A.K., Naik B. Hydrological modeling with respect to impact of land-use and land-cover change on the runoff dynamics in Budhabalanga river basing using ArcGIS and SWAT model. Remote Sens. Appl.: Soc. Environ. 2021;23 doi: 10.1016/j.rsase.2021.100527. [DOI] [Google Scholar]
- 25.Alawi S.A., Özkul S. Evaluation of land use/land cover datasets in hydrological modelling using the SWAT model. H2Open J. 2023;6(1):63–74. doi: 10.2166/h2oj.2023.062. [DOI] [Google Scholar]
- 26.Zhou T., Zhao M., Sun C., Pan J. Exploring the impact of seasonality on urban land-cover mapping using multi-season sentinel-1a and gf-1 wfv images in a subtropical monsoon-climate region. ISPRS Int. J. Geoinf. 2017;7(1):3. [Google Scholar]
- 27.Corbane C., Politis P., Kempeneers P., Simonetti D., Soille P., Burger A., Pesaresi M., Sabo F., Syrris V., Kemper T. A global cloud free pixel-based image composite from Sentinel-2 data. Data Brief. 2020;31 doi: 10.1016/j.dib.2020.105737. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 28.Erbek F.S., Özkan C., Taberner M. Comparison of maximum likelihood classification method with supervised artificial neural network algorithms for land use activities. Int. J. Remote Sens. 2004;25(9):1733–1748. doi: 10.1080/0143116031000150077. [DOI] [Google Scholar]
- 29.Shivakumar B.R., Rajashekararadhya S.V. Investigation on land cover mapping capability of maximum likelihood classifier: a case study on North Canara, India. Procedia Comput. Sci. 2018;143:579–586. doi: 10.1016/j.procs.2018.10.434. [DOI] [Google Scholar]
- 30.Das N., Mondal P., Sutradhar S., Ghosh R. Assessment of variation of land use/land cover and its impact on land surface temperature of Asansol subdivision. Egypt. J. Remote Sens. Space Sci. 2021;24(1):131–149. doi: 10.1016/j.ejrs.2020.05.001. [DOI] [Google Scholar]
- 31.Hay A.M. The derivation of global estimates from a confusion matrix. Int. J. Remote Sens. 1988;9(8):1395–1398. doi: 10.1080/01431168808954945. [DOI] [Google Scholar]
- 32.Jupp D.L. The stability of global estimates from confusion matrices. Int. J. Remote Sens. 1989;10(9):1563–1569. doi: 10.1080/01431168908903990. [DOI] [Google Scholar]
Associated Data
This section collects any data citations, data availability statements, or supplementary materials included in this article.
Supplementary Materials
Data Availability Statement
Data will be made available on request.