The Joshimath area has an inclination angle ranging from 17 to 47 degrees, according to the slope analysis (Fig. 2) which indicate a topography that is particularly prone to landslides and soil instability. The region's weak soil composition makes slope failures and soil sinking even more dangerous. The region's unstable soil nature makes landslides and subsidence more likely to occur. The gravitational forces acting on soil and rock formations are increased on steep slopes, which increases their susceptibility to sliding and downward movement. This is especially true when combined with other destabilizing variables like intense rainfall or seismic activity. Joshimath's steep terrain makes landslides and other related risks like land subsidence extremely dangerous. A number of basins or catchment areas within the research region are delineated in Joshimath (Fig. 3). The regions from which water flows into a shared outlet or stream are represented by these basins. Different colours are used to delineate the basins, signifying different drainage systems. The topography and elevation data most likely define the basin boundaries, with ridgelines and high points serving as divisions between neighbouring basins. A dendritic drainage pattern is shown by the streams in Joshimath (Fig. 4), where numerous smaller streams and tributaries merge to form larger streams or rivers. Larger rivers or streams are shown by longer lines in the blue depiction of the streams. This dendritic pattern, which is typical of the Joshimath region, is prevalent in regions with generally uniform geology. A watershed is a section of land that empties into a common outlet, like a lake, river, or stream, all of the water that flows over or under it. The topography and drainage patterns serve as the basis for defining the watershed boundaries, which divide the areas that supply water to various outlets or streams (Band et al. 1989). A more thorough view of the stream network, including the hierarchy or stream order, can be found in Streams and Watershed (Fig. 4). The primary rivers or streams are shown by the thickest blue lines, whereas lesser tributaries and streams of lower order are shown by the thinner lines. It is possible to see where these streams converge, where smaller one’s merge with larger ones to form a larger river system. Considering that the studied area includes many watersheds, it is likely that the area's drainage system is complex, with different streams and rivers coming from different catchment areas. Hydrological analysis, water resource management, and evaluating the possible effects of land use changes or development on the drainage network and water flow patterns all depend on an understanding of the basin, stream, and watershed characteristics. The Joshimath region has a dendritic drainage pattern, as shown by the hydrology mapping (Figs. 3 and 4), with numerous streams and tributaries joining to form bigger rivers. Although carefully designed drainage systems can reduce erosion and landslides, any disruption or change to the natural drainage patterns can cause water to build up, flooding, and compaction of the soil, which raises the danger of subsidence.
The Normalized Difference Vegetation Index (NDVI) analysis for the years 2000, 2011, and 2022 (Fig. 5, 6, and 7) demonstrated a declining trend in vegetation cover over time. The decreasing vegetation orientation suggests deforestation, leading to a reduction in soil-binding capacity due to the absence of tree and plant roots acting anchors for the soil. The decreasing vegetation orientation suggests deforestation, which reduces soil binding capacity due to the absence of tree and plant roots acting as anchor. Vegetation cover plays a crucial role in stabilizing soil and preventing erosion. The loss of vegetation due to deforestation reduces the soil's ability to bind and resist erosion forces, making it more susceptible to subsidence (Zhang et al. 2021). The declining NDVI values indicate a diminishing capacity of the soil to withstand subsidence, especially in the presence of other destabilizing factors like heavy rainfall or seismic activities. A declining pattern in vegetation cover over time was shown by the Normalized Difference Vegetation Index (NDVI) analysis for the years 2000, 2011, and 2022 (Fig. 5, 6, and 7). The presence of vegetation cover is essential for maintaining soil stability and halting erosion. Deforestation causes the soil to lose its ability to bind and withstand erosion forces, which increases the soil's susceptibility to subsidence. The NDVI values are showing a decline in the soil's ability to resist subsidence, particularly when other destabilizing variables such as intense rainfall or seismic activity are present.
The 35.8% of the area is designated as rangeland on the Land Use Land Cover (LULC) map for 2022 (Fig. 10). This indicates a lack of vegetation cover that binds soil, which increases the area's susceptibility to soil subsidence. According to the LULC map for 2022 (Fig. 10), rangeland makes up a sizeable share (35.8%) of the research region. According to the NDVI analysis, the high proportion of rangelands suggests a lack of plant cover that binds soil, making the region more vulnerable to processes that cause soil erosion and subsidence (Table 1). Deep-rooted plants and thick vegetation—both necessary for stable soil—are rare in rangelands. This deficiency in soil-binding components makes soil erosion and sinking more likely, particularly after periods of intense rainfall or other disturbances. Heavy precipitation occurrences are on the rise, especially during the monsoon months of June through September, according to the rainfall data study (Figs. 8 and 9). Instability and soil erosion are caused in part by the increased frequency and intensity of these intense downpours. The stability of the soil and subsidence are significantly impacted by heavy rainfall occurrences. Heavy rainfall occurrences are on the rise, especially during the monsoon months of June through September, according to the rainfall data study (Figs. 8 and 9).
Table 1
Showing the total area and its percentage for different land use characterisation
Area Characterisation | Sum of Area | % Area |
Built up | 1.43 | 0.03 |
Cloud Cover | 1099.10 | 24.10 |
Rangeland | 1633.78 | 35.80 |
snow | 0.22 | 0.05 |
trees | 310.38 | 6.80 |
valley | 1507.98 | 33.04 |
water body | 7.73 | 0.17 |
The rainfall data analysis (Figs. 8 and 9) demonstrates an increasing trend in heavy precipitation events, particularly during the monsoon months (June-September). The frequency and intensity of these heavy downpours have been on the rise, contributing to soil erosion and instability (Table 2). Heavy rainfall events have a significant impact on soil stability and subsidence. The rainfall data analysis (Figs. 8 and 9) demonstrates an increasing trend in heavy rainfall events, particularly during the monsoon months (June-September). The frequency and intensity of these heavy downpours have been on the rise, contributing to soil erosion and instability. Intense precipitation leads to water accumulation, soil saturation, and erosion, reducing the soil's bearing capacity and increasing the risk of subsidence. The observed increasing trend in heavy rainfall events, coupled with the effects of climate change, poses an additional threat to the already vulnerable Joshimath region, potentially exacerbating the land subsidence problem.
Table 2
Monthly Averaged data of rainfall (IMD)
Months
|
2011
|
2012
|
2013
|
2014
|
2015
|
2016
|
2017
|
2018
|
2019
|
2020
|
2021
|
2022
|
Jan
|
0.81
|
2.27
|
2.47
|
0.32
|
1.90
|
0.24
|
1.43
|
0.78
|
3.72
|
4.69
|
0.98
|
1.88
|
Feb
|
3.25
|
0.84
|
7.23
|
3.13
|
2.85
|
0.72
|
0.40
|
0.44
|
5.02
|
0.66
|
0.74
|
2.35
|
March
|
0.47
|
2.71
|
1.07
|
2.25
|
3.09
|
1.80
|
2.95
|
1.13
|
1.19
|
4.91
|
0.91
|
1.14
|
April
|
1.56
|
1.07
|
0.68
|
1.84
|
1.20
|
0.43
|
3.36
|
3.20
|
3.56
|
1.75
|
2.79
|
1.23
|
May
|
2.11
|
0.23
|
0.48
|
2.37
|
0.98
|
4.04
|
6.29
|
3.14
|
0.96
|
4.67
|
7.57
|
2.22
|
June
|
7.49
|
1.01
|
17.27
|
1.90
|
6.69
|
11.85
|
10.79
|
8.97
|
2.46
|
5.02
|
14.74
|
5.26
|
July
|
8.94
|
8.48
|
18.33
|
13.98
|
13.39
|
22.95
|
19.30
|
17.83
|
9.01
|
14.53
|
12.89
|
13.66
|
Aug
|
12.97
|
18.18
|
15.20
|
11.03
|
9.45
|
20.96
|
16.49
|
21.91
|
17.45
|
21.72
|
10.88
|
12.36
|
Sept
|
3.20
|
3.61
|
4.82
|
2.68
|
1.40
|
7.49
|
9.38
|
8.13
|
11.85
|
3.06
|
10.16
|
3.55
|
Oct
|
0.12
|
0.01
|
1.10
|
1.25
|
0.66
|
1.06
|
0.02
|
0.00
|
0.63
|
0.00
|
4.73
|
1.32
|
Nov
|
0.02
|
0.00
|
0.04
|
0.00
|
0.03
|
0.00
|
0.02
|
0.51
|
1.39
|
0.55
|
0.02
|
0.01
|
Dec
|
0.16
|
0.38
|
0.00
|
2.20
|
0.09
|
0.05
|
1.04
|
0.02
|
2.70
|
0.28
|
0.61
|
1.23
|
The combination of steep slopes, loose soil composition, deforestation, and heavy rainfall events makes the Joshimath region highly susceptible to landslides and soil subsidence. The declining vegetation cover, as indicated by the NDVI analysis, reduces the soil's ability to bind and resist erosion, further exacerbating the subsidence risk (Jiang et al. 2022). The significant proportion of rangeland in the LULC map suggests a lack of soil-binding vegetation, which can contribute to soil instability and subsidence, especially during heavy downpour events or seismic activities. The increasing frequency and intensity of heavy rainfall, particularly during the monsoon season, can lead to soil erosion, water accumulation, and a reduction in soil bearing capacity, ultimately resulting in subsidence. The dendritic drainage pattern, while generally efficient in draining water, can be disrupted by human activities or natural events, leading to water pooling and soil compaction. Temperature fluctuations can also contribute to soil subsidence through thermal expansion and contraction of soil particles, changes in soil moisture content, and increased susceptibility to erosion and landslides. Additionally, groundwater extraction and aquifer puncturing can lower the water table, reducing soil support and leading to compaction and subsidence. Anthropogenic factors like groundwater overexploitation, can further exacerbate the soil subsidence problem in the Joshimath region. The Joshimath Aquifer Occurrence in 2009 and the Bone Chilling Lake Surge (GLOF) in 2021 exemplify the potential consequences of such events, causing significant damage to infrastructure, disrupting water supplies, and posing socio-economic challenges. To mitigate the risk of soil subsidence and ensure the long-term stability of the Joshimath region, a comprehensive approach is required, involving sustainable land management practices, afforestation efforts, responsible urban planning, groundwater regulation, and disaster preparedness measures. The findings of this study align with and complement previous research on land subsidence in the Himalayan region, particularly in the Joshimath area. The observed declining trend in vegetation cover, as indicated by the NDVI analysis, is consistent with the findings of Bhandari et al. (2021), who reported deforestation and vegetation loss in the Garhwal Himalayas, including Joshimath. This deforestation has led to a reduction in soil-binding capacity, increasing the susceptibility to soil erosion and subsequent subsidence, as also noted by Rautela and Lakhera (2000). The increasing trend in heavy precipitation events, particularly during the monsoon months, is consistent with the broader regional and global patterns of climate change-induced changes in precipitation patterns (Shrestha et al., 2015; IPCC, 2021). This trend has been observed in several studies conducted in the Himalayan region, including the work of Srivastava et al. (2013), who reported an increase in the frequency and intensity of extreme rainfall events. These heavy downpours can lead to soil erosion, water accumulation, and a reduction in soil stability, ultimately contributing to land subsidence, as documented in the present study and supported by the findings of Bru et al. (2013).