Aire de conservation du Parc national du Grand Himalaya
Country
India
Inscribed in
2014
Criterion
(x)
The conservation outlook for this site has been assessed as "good with some concerns" in the latest assessment cycle. Explore the Conservation Outlook Assessment for the site below. You have the option to access the summary, or the detailed assessment.
Ce parc national se trouve dans le secteur occidental de l’Himalaya, dans l’État indien septentrional de l’Himachal Pradesh. Il se caractérise par de hauts sommets alpins, des prairies alpines et des forêts riveraines. Les 90 540 ha du bien englobent les sources, nées des hautes montagnes glacées et de la fonte des neiges, de plusieurs fleuves et les bassins-versants des eaux qui alimentent de façon vitale des millions de personnes vivant en aval. Le site protège les forêts touchées par la mousson et les prairies alpines des chaînes frontales de l’Himalaya. Le bien, qui protège aussi une partie du « haut lieu de biodiversité » de l’Himalaya, comprend 25 types de forêts et un riche assemblage associé d’espèces de la faune, dont plusieurs sont menacées. Cela lui confère une importance exceptionnelle pour la conservation de la biodiversité. © UNESCO
Summary
2025 Conservation Outlook
Finalised on
11 oct 2025
Good with some concerns
Current state and trend of VALUES
Low Concern
Overall THREATS
Overall PROTECTION and MANAGEMENT
Full assessment
Description of values
Globally significant habitat
Criterion
(x)
The Great Himalayan National Park Conservation Area (GHNPCA) is located in the Kullu district of Himachal Pradesh, India and is spread across 90,540 hectares. It consists of the Great Himalayan National Park (GHNP) (75,440 hectares), and two adjacent wildlife sanctuaries-Sainj Wildlife Sanctuary (9,000 hectares) and Tirthan Wildlife Sanctuary (6,100 hectares). It also encompasses a 5 km buffer zone along the national park’s western boundary, covering 26,560 hectares. Though the Ecozone is not a part of the inscribed property, it is managed under the same administration as the national park and sanctuaries.
The GHNPCA includes the upper Mountain glacial and snow melt water source origins of the westerly flowing Jiwa Nal, Sainj and Tirthan Rivers and the north-westerly flowing Parvati River. The rivers are headwater tributaries to the River Beas and subsequently, the Indus River (World Heritage Committee, 2014).
Geographically, the GHNPCA lies at the junction of two major faunal realms, i.e., the Indomalayan to the south and Palearctic to the north, supporting biotic elements from both the realms. The elevation ranges from 1900 m to 6000 m, and the property protects a variety of habitats across the steep side valley landscapes: sub-tropical forests at lower elevations; mid-level temperate deciduous forests; flowering alpine meadows and the high glaciers and peaks (State Party of India, 2013; IUCN, 2013). GHNPCA is a part of the Conservation International’s Himalaya Biodiversity hotspot and is home to several plants and animals endemic to the Western Himalayan Region (World Heritage Committee, 2014). It includes 25 forest types including the unmodified low altitude (60 m in height) (State Party of India, 2013; IUCN, 2013). GHNP also harbours natural populations of 11 out of 14 conifer species found in Himachal Pradesh (WII, 2023).
Recent studies reaffirm its role as a critical refuge for endemic and endangered species such as the Western Tragopan (Tragopan melanocephalus) and Snow Leopard (Panthera uncia) (Bhatnagar et al., 2021). The park spans elevations from 1,500 to over 6,000 meters, encompassing a wide range of habitats from subtropical forests to alpine meadows, which contribute to its high species richness (UNESCO, 2024). Research by Sharma et al. (2022) underscores GHNPCA’s importance in maintaining ecological connectivity in the western Himalayas, while climate modeling studies predict a contraction in suitable habitats for several plant and animal species due to rising temperatures (Thakur et al., 2023).
The GHNPCA includes the upper Mountain glacial and snow melt water source origins of the westerly flowing Jiwa Nal, Sainj and Tirthan Rivers and the north-westerly flowing Parvati River. The rivers are headwater tributaries to the River Beas and subsequently, the Indus River (World Heritage Committee, 2014).
Geographically, the GHNPCA lies at the junction of two major faunal realms, i.e., the Indomalayan to the south and Palearctic to the north, supporting biotic elements from both the realms. The elevation ranges from 1900 m to 6000 m, and the property protects a variety of habitats across the steep side valley landscapes: sub-tropical forests at lower elevations; mid-level temperate deciduous forests; flowering alpine meadows and the high glaciers and peaks (State Party of India, 2013; IUCN, 2013). GHNPCA is a part of the Conservation International’s Himalaya Biodiversity hotspot and is home to several plants and animals endemic to the Western Himalayan Region (World Heritage Committee, 2014). It includes 25 forest types including the unmodified low altitude (60 m in height) (State Party of India, 2013; IUCN, 2013). GHNP also harbours natural populations of 11 out of 14 conifer species found in Himachal Pradesh (WII, 2023).
Recent studies reaffirm its role as a critical refuge for endemic and endangered species such as the Western Tragopan (Tragopan melanocephalus) and Snow Leopard (Panthera uncia) (Bhatnagar et al., 2021). The park spans elevations from 1,500 to over 6,000 meters, encompassing a wide range of habitats from subtropical forests to alpine meadows, which contribute to its high species richness (UNESCO, 2024). Research by Sharma et al. (2022) underscores GHNPCA’s importance in maintaining ecological connectivity in the western Himalayas, while climate modeling studies predict a contraction in suitable habitats for several plant and animal species due to rising temperatures (Thakur et al., 2023).
Rich assemblage of faunal species
Criterion
(x)
GHNPCA supports around 31 mammalian species, including the globally threatened species, i.e., Himalayan Musk Deer (Moschus leucogaster, Endangered), Asian Black Bear (Ursus thibetanus, Vulnerable), Common Leopard (Panthera pardus, Vulnerable), Snow Leopard (Panthera uncia, Vulnerable) and Cheer Pheasant (Catreus wallichii, Vulnerable) (State Party of India, 2010; 2013; World Heritage Committee, 2014). The GHNP is also a part of the Project Snow Leopard, a Government of India Project to conserve Snow Leopards and their habitats in the Himalayan and Trans Himalayan region. The latest Snow Leopard population estimation in India confirms the presence of the species within the national park area suggesting a habitat overlap with the common leopard (MoEF, 2008; Wildlife Wing - Himachal Pradesh Forest Department, 2021). Research also suggests that GHNP is an important protected habitat for the Snow Leopard, in the context of climate change and future vulnerability. The national park area is also a year round habitat to the Himalayan Tahr (Hemitragus jemlahicus, Near Threatened) which is endemic to Western Himalayas (State Party of India, 2020; Ale, et al., 2020).
Moreover, the contiguity of the GHNNPCA with other protected areas, i.e., Pin Valley NP, Rupi Bhabha WLS, Khirganga NP and proximity to to Kanawar WLS enhances ecological connectivity in the region. The continuity provides extensive land areas for movement of animals through their ranges and supports plant dispersal (State Party of India, 2010).
The Great Himalayan National Park Conservation Area (GHNPCA) have documented over 375 faunal species, including 31 mammals, 209 birds, 12 reptiles, and 9 amphibians (UNESCO, 2024). Long-term monitoring efforts indicate stable or increasing trends in several key species, a result attributed to stringent protection measures and low anthropogenic pressure (Thakur et al., 2023). Furthermore, the park’s intact vertical zoning from subtropical to alpine zones ensures year-round habitat for migratory and resident species (Bhatnagar et al., 2022).
Moreover, the contiguity of the GHNNPCA with other protected areas, i.e., Pin Valley NP, Rupi Bhabha WLS, Khirganga NP and proximity to to Kanawar WLS enhances ecological connectivity in the region. The continuity provides extensive land areas for movement of animals through their ranges and supports plant dispersal (State Party of India, 2010).
The Great Himalayan National Park Conservation Area (GHNPCA) have documented over 375 faunal species, including 31 mammals, 209 birds, 12 reptiles, and 9 amphibians (UNESCO, 2024). Long-term monitoring efforts indicate stable or increasing trends in several key species, a result attributed to stringent protection measures and low anthropogenic pressure (Thakur et al., 2023). Furthermore, the park’s intact vertical zoning from subtropical to alpine zones ensures year-round habitat for migratory and resident species (Bhatnagar et al., 2022).
Rich assemblage of floral species
Criterion
(x)
The property is floristically one of the richest sites in the Western Himalayan region supporting 805 vascular (high order) plant species, 192 lichen species, 12 species of liverworts and 25 species of ferns. 58% of the angiosperm species recorded from the GHNPCA are endemic to Western Himalayas (World Heritage Committee, 2014). The property also provides refuge to Himalayan Mulberry (Morus serrata), a tree species confined to the Indo-Pakistan subcontinent and now existing as one of the last remaining wild populations (State Party of India, 2013; WII, 2023).
The Great Himalayan National Park Conservation Area (GHNPCA) has documented over 1,000 plant species within the park, including a significant number of endemic and medicinal plants (UNESCO, 2024). Notably, the park is home to various orchid species, which are indicators of ecological health and biodiversity. Advancements in deep learning have facilitated the mapping of conservation statuses of orchid assemblages globally, highlighting regions like GHNPCA as critical for orchid conservation (Estopinan et al., 2024). Furthermore, innovative approaches using Convolutional Neural Networks (CNNs) have been developed to classify and monitor herb species in the region, enhancing our understanding of plant diversity and aiding in conservation efforts (Thapa et al., 2025).
The Great Himalayan National Park Conservation Area (GHNPCA) has documented over 1,000 plant species within the park, including a significant number of endemic and medicinal plants (UNESCO, 2024). Notably, the park is home to various orchid species, which are indicators of ecological health and biodiversity. Advancements in deep learning have facilitated the mapping of conservation statuses of orchid assemblages globally, highlighting regions like GHNPCA as critical for orchid conservation (Estopinan et al., 2024). Furthermore, innovative approaches using Convolutional Neural Networks (CNNs) have been developed to classify and monitor herb species in the region, enhancing our understanding of plant diversity and aiding in conservation efforts (Thapa et al., 2025).
Significant biodiversity values - birds
The GHNPCA plays a crucial role in preserving the biodiversity of the Western Himalayas, particularly as an important habitat for threatened species. A total of 209 species of birds have been recorded from the GHNPCA at least being 50 summer visitors (State Party of India, 2013; World Heritage Committee, 2014). The Western Himalayan region has been categorized as an Endemic Bird Area (EBA) by BirdLife International, and GHNPCA provides significant habitat for restricted bird range species like the Western Tragopan (Tragopan melanocephalus) and Cheer Pheasant (Catreus wallichii). Both species are categorized as ‘Vulnerable’ as per the IUCN Red List of Threatened Species and protected under Schedule-I of India’s Wildlife Protection Act, 1972 (highest degree of legal protection) (State Party of India, 2013; IUCN, 2013.
The GHNP is one of the two national parks in the world that supports substantial populations of Western Tragopan, alongside Palas Valley in Northern Pakistan (Naithani, et al., 2018).
The GHNP is one of the two national parks in the world that supports substantial populations of Western Tragopan, alongside Palas Valley in Northern Pakistan (Naithani, et al., 2018).
High medicinal plant biodiversity
The property has the greatest concentration of medicinal plants known for all of the Himalayas and more than 250 species of medicinal plants native to the Himalayan region are recorded within the GHNPCA (IUCN, 2013).
Important cultural heritage
The GHNPCA holds spiritual and cultural significance for its local inhabitants, with particular sites such as water bodies and forest patches regarded as divine and revered in their traditions. These sacred sites are protected through rituals, taboos, and cultural practices. Many of these sites are within the national park area and its ecozone. The Rakti Sar glacier at 4,000 meters is the origin of river Sainj in the GHNP and is considered the battle ground between mythological demon Raktbeej and Goddess Mahakali. Higher up at around 4,088 meters, the Hanskund Tirath is a sacred bathing site. The Maantalai lake is revered as the birthplace of goddess Parvati and her marriage to Lord Shiva. The region is home to sacred groves, pilgrimage sites, and seasonal festivals that play a vital role in conserving biodiversity through traditional ecological knowledge (Rana et al., 2021). The Devta worship system, reinforce sustainable land-use practices and foster a spiritual connection with nature (Mehta & Negi, 2022). Bathing in its waters is considered therapeutic, and local people perform worship ceremonies here during cultural festivals. These visits to the national park are accompanied by a forest guard (Sood & Dhyani, 2024; State Party of India, 2013).
For the residents of the Kullu district, Shrikhand Mahadev located on the southern boundary of the GHNPCA is a significant pilgrimage site. It is dedicated to Lord Shiva, and the Parvati Baagicha (garden), named after Lord Shiva’s wife is located on the trek route to site. This area is the habitat of Saussurea obvallata (Brahmakamal), an endangered species that blooms profusely in the region and is of high conservation priority in local conservation programs (Semwal, et al., 2020; Sood & Dhyani, 2024).
Sacred groves or Devbans present within the GHNPCA represent areas of forestlands historically preserved in the honour of the regional deities. The Ringoo Van near Sharan village, Nagini near Baghi Kashari and Lapah in the ecozone area represent some of the finest examples of community conservation where local traditions ensure that these sites remain undisturbed and pristine (Pandey, 2019; Sood & Dhyani, 2024). community-based ecotourism initiatives have helped maintain cultural identity while supporting conservation goals, as documented in participatory development studies (Singh & Sharma, 2023).
For the residents of the Kullu district, Shrikhand Mahadev located on the southern boundary of the GHNPCA is a significant pilgrimage site. It is dedicated to Lord Shiva, and the Parvati Baagicha (garden), named after Lord Shiva’s wife is located on the trek route to site. This area is the habitat of Saussurea obvallata (Brahmakamal), an endangered species that blooms profusely in the region and is of high conservation priority in local conservation programs (Semwal, et al., 2020; Sood & Dhyani, 2024).
Sacred groves or Devbans present within the GHNPCA represent areas of forestlands historically preserved in the honour of the regional deities. The Ringoo Van near Sharan village, Nagini near Baghi Kashari and Lapah in the ecozone area represent some of the finest examples of community conservation where local traditions ensure that these sites remain undisturbed and pristine (Pandey, 2019; Sood & Dhyani, 2024). community-based ecotourism initiatives have helped maintain cultural identity while supporting conservation goals, as documented in participatory development studies (Singh & Sharma, 2023).
Assessment information
Cumulative anthropogenic pressures, including unsustainable grazing, illegal hunting, and overexploitation of medicinal plants, have precipitated biodiversity declines, with endemic species like the Western Tragopan (Tragopan melanocephalus) and Himalayan musk deer (Moschus leucogaster) facing habitat fragmentation and population drops exceeding 30% in critical zones. Climate change amplifies risks, driving intensified forest fires, glacial retreat, and erratic rainfall, which destabilize slopes and elevate landslide frequency by 40%, degrading soil health and aquatic ecosystems. Infrastructure expansion, notably power lines in Sainj Sanctuary and tourism-related construction, fragments wildlife corridors, disrupts avian migration, and introduces invasive species like Parthenium hysterophorus, which colonize 45% of degraded areas, outcompeting native flora. Agricultural encroachment and horticultural practices further erode forest cover, exacerbate human-wildlife conflict, and contaminate freshwater systems vital for endemic fish (Schizothorax richardsonii).
Terrestrial Animal Farming, Ranching & Herding
(High grazing pressure on the meadows )
Inside site
, Scattered(5-15%)
Outside site
Many local inhabitants in the GHNPCA and its ecozone area are transhumant pastoralists relying on seasonal migration, with livestock and dependent graziers spending winter months in the village pastures (and their surrounds) and migrating to alpine and sub-alpine pastures during summer and rainy months. The alpine and sub-alpine grasslands serve as important grazing sites not only for locals but also migratory graziers from Suket region of Mandi district and Ani and Nirmand areas of Outer Kullu (Irfan, et al., 2023).
When the GHNP was notified in 1999, traditional rights to collect medicinal plants, timber, and non-timber forest produce (NTFP) and to graze livestock within the national park area were ceased. While cash compensation was provided to the right holders of medicinal plant collection, no monetary benefits were provided to villagers who grazed their sheep and goats in the park. Graziers were redirected to alternate pasturelands in Sainj and Tirthan sanctuaries and the ecozone. The Sainj sanctuary was notified in 1994 around three villages of Shagwar, Shakti and Marore and Tirthan sanctuary was notified in 1999. Their notification retained the traditional rights of local communities, including grazing and herb collection. Presently, 120 village residents in Sainj exercise these rights, and while Tirthan sanctuary does not have human settlements, it is still subject to traditional seasonal grazing by surrounding villages (State Party of India, 2010; 2018; 2020). Reduced vegetation cover, soil compaction, and biodiversity loss, particularly impacts endemic alpine flora such as Meconopsis aculeata and Rheum australe (Sharma et al., 2022), while soil degradation, noting a 40% decline in organic carbon in intensively grazed zones, exacerbates erosion risks. Livestock-mediated dispersal of invasive species (e.g., Lantana camara) further disrupts native ecosystems, as evidenced by remote sensing analyses (Singh et al., 2024).
The Management Effectiveness Evaluation (MEE) conducted for GHNPCA (2006-2009 and 2018-2019) identified biotic and human interference, including livestock grazing as a management weakness to be addressed (WII, 2015; Mohan, et al., 2020). Concerns about the likely impact of local resource use, including grazing, on the OUV of the GHNPCA were highlighted in the 43rd and 44th World Heritage Committee meetings. The committee requested State Party updates on the current state of livestock grazing in Sainj and Tirthan sanctuary (World Heritage Committee, 2019 & 2021). A recent study conducted by the Wildlife Institute of India (WII) assed grazing impacts in the two sanctuaries. The study recorded that sanctuaries are visited by six Gaddi and two Gujjar groups with total livestock of 3,508 sheep and goats, and 160 buffalos and 82 oxen. Forage yields in meadows were found to range from 1.5 to 3.8 tonnes per hectare, with carrying capacity varying from 3.4–4.98 Animal Carrying Units, indicating very high grazing pressure. This has resulted in soil compaction, erosion, and lower species richness in grazed areas (WII, 2024).
The restrictions on access to GHNP area, has also increased pressure on the village pastures in the ecozone area. There are 160 villages within the ecozone, many with historical dependencies on GHNP resources. Village pastures, especially those at higher elevations are important grazing grounds for cattle and livestock population. Increased pressures over pasture lands has turned them into one of the most intensively used land use categories, occasionally leading to conflicts among locals (Irfan, et al., 2023).
Graziers also engage in collection of medicinal herbs and lopping and girdling of trees for fuelwood which may affect certain flora species. The rare Rhododendron campanulatum occurs in sub-alpine zones in the GHNPCA and dense patches of this shrub is a prime habitat of Himalayan Musk deer. However, the shrub faces threats from its collection by graziers (and herb collectors) and tourists for fuelwood. Juniperus communis is another rare shrub found in alpine and sub-alpine areas. The species is harvested by graziers during their camping in alpine areas and has sharply declined in the recent past. Further, the trees of Himalayan Brown Oak (Quercus floribunda) constitute an important upper temperate and sub-alpine forests harbouring a rich diversity of plants and animals. These trees are commonly lopped by locals and migratory pastoralists for fuel (State Party of India, 2010). Current grazing practices should be monitored to minimize any possible threats to local flora.
When the GHNP was notified in 1999, traditional rights to collect medicinal plants, timber, and non-timber forest produce (NTFP) and to graze livestock within the national park area were ceased. While cash compensation was provided to the right holders of medicinal plant collection, no monetary benefits were provided to villagers who grazed their sheep and goats in the park. Graziers were redirected to alternate pasturelands in Sainj and Tirthan sanctuaries and the ecozone. The Sainj sanctuary was notified in 1994 around three villages of Shagwar, Shakti and Marore and Tirthan sanctuary was notified in 1999. Their notification retained the traditional rights of local communities, including grazing and herb collection. Presently, 120 village residents in Sainj exercise these rights, and while Tirthan sanctuary does not have human settlements, it is still subject to traditional seasonal grazing by surrounding villages (State Party of India, 2010; 2018; 2020). Reduced vegetation cover, soil compaction, and biodiversity loss, particularly impacts endemic alpine flora such as Meconopsis aculeata and Rheum australe (Sharma et al., 2022), while soil degradation, noting a 40% decline in organic carbon in intensively grazed zones, exacerbates erosion risks. Livestock-mediated dispersal of invasive species (e.g., Lantana camara) further disrupts native ecosystems, as evidenced by remote sensing analyses (Singh et al., 2024).
The Management Effectiveness Evaluation (MEE) conducted for GHNPCA (2006-2009 and 2018-2019) identified biotic and human interference, including livestock grazing as a management weakness to be addressed (WII, 2015; Mohan, et al., 2020). Concerns about the likely impact of local resource use, including grazing, on the OUV of the GHNPCA were highlighted in the 43rd and 44th World Heritage Committee meetings. The committee requested State Party updates on the current state of livestock grazing in Sainj and Tirthan sanctuary (World Heritage Committee, 2019 & 2021). A recent study conducted by the Wildlife Institute of India (WII) assed grazing impacts in the two sanctuaries. The study recorded that sanctuaries are visited by six Gaddi and two Gujjar groups with total livestock of 3,508 sheep and goats, and 160 buffalos and 82 oxen. Forage yields in meadows were found to range from 1.5 to 3.8 tonnes per hectare, with carrying capacity varying from 3.4–4.98 Animal Carrying Units, indicating very high grazing pressure. This has resulted in soil compaction, erosion, and lower species richness in grazed areas (WII, 2024).
The restrictions on access to GHNP area, has also increased pressure on the village pastures in the ecozone area. There are 160 villages within the ecozone, many with historical dependencies on GHNP resources. Village pastures, especially those at higher elevations are important grazing grounds for cattle and livestock population. Increased pressures over pasture lands has turned them into one of the most intensively used land use categories, occasionally leading to conflicts among locals (Irfan, et al., 2023).
Graziers also engage in collection of medicinal herbs and lopping and girdling of trees for fuelwood which may affect certain flora species. The rare Rhododendron campanulatum occurs in sub-alpine zones in the GHNPCA and dense patches of this shrub is a prime habitat of Himalayan Musk deer. However, the shrub faces threats from its collection by graziers (and herb collectors) and tourists for fuelwood. Juniperus communis is another rare shrub found in alpine and sub-alpine areas. The species is harvested by graziers during their camping in alpine areas and has sharply declined in the recent past. Further, the trees of Himalayan Brown Oak (Quercus floribunda) constitute an important upper temperate and sub-alpine forests harbouring a rich diversity of plants and animals. These trees are commonly lopped by locals and migratory pastoralists for fuel (State Party of India, 2010). Current grazing practices should be monitored to minimize any possible threats to local flora.
Gathering, Harvesting & Controlling Terrestrial Plants & Fungi
(Overexploitation of medicinal plants)
Other targeted species names
Fritillaria cirrhosa Trillium govanianum Wall Nardostachys jatamansi Arnebia benthamii Dactylorhiza hatagirea Dioscorea deltoidea Taxus wallichiana
Inside site
, Scattered(5-15%)
Outside site
The Indian Himalayas are home to over 1,700 medicinal plant species, which are used as a raw material for the commercial herbal industry (Chauhan, et al., 2018). The GHNPCA is reported as one the most important sites for medicinal plant conservation in the Western Himalayas, both in terms of species diversity and population. Collection of medicinal herbs poses biotic pressures on the GHNPCA and its ecozone. Historically, village elders followed sustainable harvesting practices, such as extracting herbs only after Bees Bhadon (around October), when plants had completed their annual cycles and seeds had naturally dispersed. These practices were accompanied by sacred ceremonies to select a time and particular plant to extract it for medicinal purposes. However, with the growth of the pharmaceutical industry and the onset of commercialization, such sacred practices have gradually phased out (Pandey, 2019). The high commercial value of various medicinal species has led to the overexploitation of their roots, tubers, seeds, fruits, flowers, and leaves. Field surveys reveal significant declines in the occurrence of species such as Fritillaria cirrhosa and Trillium govanianum Wall, attributed to unsustainable harvesting by locals. Other valuable medicinal plants, including Nardostachys jatamansi, Arnebia benthamii, Dactylorhiza hatagirea, and Dioscorea deltoidea, are also vanishing from the area (Kumar et al., 2021).
The endangered tree Taxus wallichiana, native to the Sainj and Tirthan valleys, has also experienced population declines. Its bark and leaves are heavily lopped as they contain Taxol, a potent anticancer drug used to treat ovarian and breast cancer. The leaves are also utilized in Ayurvedic medicine for asthma and bronchitis (State Party of India, 2010). Large-scale collection of medicinal herbs may also involve nest predation and cause habitat disturbance to Himalayan Monal and Koklass. Prominent pollinators, such as Common blue Apollo (Parnassius hardwicki virdicans, Endangered) and rare Yellow swallowtail (Papilio Machaon) are also vulnerable to changes in native vegetation caused during herb collection (State Party of India, 2010).
Unsustainable harvesting practices targeting high-value species like Aconitum heterophyllum and Dactylorhiza hatagirea, have led to population declines of over 60% in key habitats, disrupting ecological balance and regeneration cycles (Thakur et al., 2021). Habitat fragmentation and biodiversity loss, with invasive species encroachment (e.g., Polygonum polystachyum) is evident in overharvested zones. Socio-ecological impacts are showing heightened conflicts between local livelihoods and conservation goals, as dwindling medicinal resources drive illegal trade networks (Negi et al., 2025). Climate change synergies exacerbate these threats, with warming temperatures (Rana & Pandey, 2022).
The endangered tree Taxus wallichiana, native to the Sainj and Tirthan valleys, has also experienced population declines. Its bark and leaves are heavily lopped as they contain Taxol, a potent anticancer drug used to treat ovarian and breast cancer. The leaves are also utilized in Ayurvedic medicine for asthma and bronchitis (State Party of India, 2010). Large-scale collection of medicinal herbs may also involve nest predation and cause habitat disturbance to Himalayan Monal and Koklass. Prominent pollinators, such as Common blue Apollo (Parnassius hardwicki virdicans, Endangered) and rare Yellow swallowtail (Papilio Machaon) are also vulnerable to changes in native vegetation caused during herb collection (State Party of India, 2010).
Unsustainable harvesting practices targeting high-value species like Aconitum heterophyllum and Dactylorhiza hatagirea, have led to population declines of over 60% in key habitats, disrupting ecological balance and regeneration cycles (Thakur et al., 2021). Habitat fragmentation and biodiversity loss, with invasive species encroachment (e.g., Polygonum polystachyum) is evident in overharvested zones. Socio-ecological impacts are showing heightened conflicts between local livelihoods and conservation goals, as dwindling medicinal resources drive illegal trade networks (Negi et al., 2025). Climate change synergies exacerbate these threats, with warming temperatures (Rana & Pandey, 2022).
Hunting, Collecting & Controlling Terrestrial Animals
(Illegal opportunistic hunting and retaliatory killings of wildlife)
Other targeted species names
Himalayan Monal, Western Tragopan, Koklass, of Musk Deer and Himalayan Tahr
Inside site
, Scattered(5-15%)
Outside site
Hunting in the area was officially banned in 1984 following the notification for the creation of the GHNP and wildlife sanctuary. However, illegal opportunistic hunting and snaring may be a threat, particularly in the Sainj sanctuary and its adjoining areas. Instances of poaching of mammals and birds by locals have been reported. Additionally, villagers within the Sainj area and those residing around the GHNP boundaries also resort to retaliatory killings of wildlife in response to human injury, crop damage, or livestock depredation (State Party of India, 2013). The management plan has identified poaching for crest feathers as one of the threats to the Himalayan Monal, Western Tragopan, and Koklass. Poaching may also be a factor contributing to the declining population of Musk Deer and Himalayan Tahr (State Party of India, 2010).
There has been a surge in poaching of high-value species like musk deer (Moschus chrysogaster) and Himalayan monal (Lophophorus impejanus), driven by illegal wildlife trade networks, with population declines exceeding 30% in vulnerable zones (Verma et al., 2022). Retaliatory killings of carnivores, particularly snow leopards (Panthera uncia) and Himalayan brown bears (Ursus arctos isabellinus), have intensified due to livestock depredation, as noted in community surveys (Rawat & Joshi, 2023), destabilizing apex predator roles and trophic cascades. Pathak et al. (2024) link these killings to reduced genetic diversity in small, isolated populations, heightening extinction risks. Camera-trap data (Thapa et al., 2025) reveal altered wildlife behaviour, including nocturnal shifts and habitat abandonment, exacerbating human-wildlife conflict cycles. Socioeconomic drivers, such as limited alternative livelihoods and weak enforcement, perpetuate these practices (Negi & Bhatt, 2021).
There has been a surge in poaching of high-value species like musk deer (Moschus chrysogaster) and Himalayan monal (Lophophorus impejanus), driven by illegal wildlife trade networks, with population declines exceeding 30% in vulnerable zones (Verma et al., 2022). Retaliatory killings of carnivores, particularly snow leopards (Panthera uncia) and Himalayan brown bears (Ursus arctos isabellinus), have intensified due to livestock depredation, as noted in community surveys (Rawat & Joshi, 2023), destabilizing apex predator roles and trophic cascades. Pathak et al. (2024) link these killings to reduced genetic diversity in small, isolated populations, heightening extinction risks. Camera-trap data (Thapa et al., 2025) reveal altered wildlife behaviour, including nocturnal shifts and habitat abandonment, exacerbating human-wildlife conflict cycles. Socioeconomic drivers, such as limited alternative livelihoods and weak enforcement, perpetuate these practices (Negi & Bhatt, 2021).
Fire & Fire Management
(Forest fires)
Inside site
, Scattered(5-15%)
Outside site
The forests of the GHNPCA face pressure from local communities due to their traditional rights to use forest resources. One major threat arises from fires set by graziers and NTFP collectors (State Party of India, 2010). Village pastures, locally known as ghasnies, are burned annually by locals, based on the belief that it enhances pasture yield for the following season. However, these practices often lead to forest fires, damaging huge forest patches and adversely affecting land use and land cover (Irfan et al., 2023). The risk of forest fires is further exacerbated by higher temperatures during April and May, which create favorable conditions for ignition. In some cases, fires are deliberately kindled by local residents as an act of retaliation against enforcement measures taken by the GHNPCA management (Jacob et al., 2019).
Fire incidences in particular localities is detrimental to the flora and fauna of the area. They affect several herbaceous plant species, microflora, and micro fauna, reducing overall biodiversity and degrading habitats. These fires may also pose threat to the pheasant species-Himalayan Monal, Western Tragopan, and Koklass. Important pollinators such as dung beetles and longhorn beetles, which are indicator species and help in maintaining soil fertility, are also highly vulnerable to forest fires (State Party of India, 2010).
There has been a rising fire frequency due to climate-driven temperature increases and prolonged dry spells, with a 50% surge in fire-prone zones (Kumar et al., 2021). Human activities, such as slash-and-burn agriculture and unchecked tourism, to 70% of ignition sources, exacerbate habitat fragmentation in critical oak (Quercus semecarpifolia) and deodar (Cedrus deodara) forests (Joshi and Thakur, 2022) while causing a 35% decline in nutrient retention, impairing regeneration of endemic flora like Rhododendron campanulatum (Bhattacharya et al., 2023). Invasive species (e.g., Ageratina adenophora) colonise burnt areas, outcompeting native vegetation, as shown in remote sensing analyses (Meena et al., 2024).
Fire incidences in particular localities is detrimental to the flora and fauna of the area. They affect several herbaceous plant species, microflora, and micro fauna, reducing overall biodiversity and degrading habitats. These fires may also pose threat to the pheasant species-Himalayan Monal, Western Tragopan, and Koklass. Important pollinators such as dung beetles and longhorn beetles, which are indicator species and help in maintaining soil fertility, are also highly vulnerable to forest fires (State Party of India, 2010).
There has been a rising fire frequency due to climate-driven temperature increases and prolonged dry spells, with a 50% surge in fire-prone zones (Kumar et al., 2021). Human activities, such as slash-and-burn agriculture and unchecked tourism, to 70% of ignition sources, exacerbate habitat fragmentation in critical oak (Quercus semecarpifolia) and deodar (Cedrus deodara) forests (Joshi and Thakur, 2022) while causing a 35% decline in nutrient retention, impairing regeneration of endemic flora like Rhododendron campanulatum (Bhattacharya et al., 2023). Invasive species (e.g., Ageratina adenophora) colonise burnt areas, outcompeting native vegetation, as shown in remote sensing analyses (Meena et al., 2024).
Annual & Perennial Non-Timber Crops, Wood & Pulp Plantations
(Expansion of agricultural and horticultural practices in the ecozone)
Outside site
The three villages within the Sainj Wildlife Sanctuary—Shagwar, Shakti, and Marore—are located on its southern boundary, contiguous with the boundary of the GHNP. These villages are situated in highly remote areas, lacking basic amenities such as electricity, roads, healthcare, and schools. Agriculture is the primary occupation for residents, but its productivity is limited due to the area's inaccessibility and the absence of modern agricultural facilities. Collectively, the agricultural land across these three villages totals just 12.80 hectares (State Party of India, 2010).
On the western boundary of the GHNPCA, 160 villages with a population of approximately 18,000 people live in 1,200 households. Traditionally, agricultural activities in the ecozone were largely subsistence-based, focusing on growing traditional crops well-suited to local conditions. However, supportive government policies for agriculture and horticulture, along with improvements in road networks, have significantly altered farming practices in the region. Improved connectivity and exposure to market economies have led the replacement of traditional crops with horticultural trees and cash crops. The booming of horticulture sector, driven by better road access in areas with challenging terrain, has increased the demand for agricultural land. Over time, this expansion of agriculture and horticulture has occurred at the expense of surrounding forest cover, leading to environmental impacts such as deforestation and habitat loss (Irfan et al., 2023). Encroachment into buffer zones has led to the fragmentation of critical habitats for endangered species like the Western Tragopan (Tragopan melanocephalus) and Himalayan musk deer (Moschus leucogaster), with a 25% reduction in forest cover in peripheral areas (Sharma et al., 2021). Intensive horticulture, particularly apple orchards, has driven soil erosion and agrochemical runoff, contaminating freshwater systems vital for endemic fish species (Schizothorax richardsonii) (Mehta and Joshi, 2023). Rising human-wildlife conflicts, fueled by crop-raiding by species such as Himalayan black bears (Ursus thibetanus), exacerbate retaliatory killings and habitat stress (Rawat & Negi, 2022). Climate synergies, including erratic rainfall and glacial retreat, further strain traditional farming systems, pushing communities to expand into protected zones (Pandey et al., 2025).
On the western boundary of the GHNPCA, 160 villages with a population of approximately 18,000 people live in 1,200 households. Traditionally, agricultural activities in the ecozone were largely subsistence-based, focusing on growing traditional crops well-suited to local conditions. However, supportive government policies for agriculture and horticulture, along with improvements in road networks, have significantly altered farming practices in the region. Improved connectivity and exposure to market economies have led the replacement of traditional crops with horticultural trees and cash crops. The booming of horticulture sector, driven by better road access in areas with challenging terrain, has increased the demand for agricultural land. Over time, this expansion of agriculture and horticulture has occurred at the expense of surrounding forest cover, leading to environmental impacts such as deforestation and habitat loss (Irfan et al., 2023). Encroachment into buffer zones has led to the fragmentation of critical habitats for endangered species like the Western Tragopan (Tragopan melanocephalus) and Himalayan musk deer (Moschus leucogaster), with a 25% reduction in forest cover in peripheral areas (Sharma et al., 2021). Intensive horticulture, particularly apple orchards, has driven soil erosion and agrochemical runoff, contaminating freshwater systems vital for endemic fish species (Schizothorax richardsonii) (Mehta and Joshi, 2023). Rising human-wildlife conflicts, fueled by crop-raiding by species such as Himalayan black bears (Ursus thibetanus), exacerbate retaliatory killings and habitat stress (Rawat & Negi, 2022). Climate synergies, including erratic rainfall and glacial retreat, further strain traditional farming systems, pushing communities to expand into protected zones (Pandey et al., 2025).
Residential Areas, Recreation & Tourism Areas
(Growth in settlement infrastructure and tourism in the ecozone area)
Outside site
The four valleys of the GHNPCA remain untouched by road connectivity. In the Tirthan Valley, a traveller has to walk over seven kms to reach the park boundary; in the Sainj Valley, it requires a 14-km trek to Shakti village across the boundary. Reaching the Jiwa Nal Valley park boundary involves trekking more than 20 kms, while accessing the Parvati Valley entails a two-day journey covering approximately 40 kms through Khirganga National Park. Due to its remote accessibility, fewer than 1,000 trekkers visit the GHNPCA annually. However, the western boundary of the park is fringed by 160 villages with a population of around 18,000 people living in approximately 120 households (Pandey, 2019).
The Tirthan valley is the most populated area in the ecozone, followed by Jiwanal and Sainj valleys (Pandey, 2008). Villages in the ecozone (especially, Tirthan Valley) are mostly scattered, while individual settlements within villages are mostly clustered. Traditional houses are constructed in the Kathkuni style using locally sourced stone and timber, which exerts significant pressure on forest resources. Population growth and the desire for nuclear families have increased construction activities, expanding the built-up area over the surrounding land. Improved road connectivity in previously remote areas, exposure to market forces, and the opening up of the rural economy, coupled with the growth of the tourism sector, have further accelerated construction. This trend is especially noticeable along the Tirthan River and its tributaries, where individual settlements and built-up areas have proliferated. Since the GHNP was recognized as a World Heritage Site in 2014, numerous hotels, restaurants, and homestays have emerged on agricultural land and river floodplains (Irfan et al., 2023; Nath et al., 2022). These developments have significantly altered the land use and land cover of the Tirthan Valley. The region has witnessed a decline in forest cover around villages, encroachment on forest land and floodplains, and a reduction in pasture lands. Additionally, the increased human activity has contributed to a rise in fire incidents and other environmental pressures (Irfan et al., 2023).
Rising tourist footfall correlates with noise pollution and wildlife behavioral shifts, including reduced foraging activity in Himalayan tahr (Hemitragus jemlahicus) (Mehta & Thakur, 2025). Climate change amplifies risks, as erratic rainfall destabilises slopes near construction sites (Pandey et al., 2023), while lax enforcement of eco-sensitive zoning fuels unsustainable development.
The Tirthan valley is the most populated area in the ecozone, followed by Jiwanal and Sainj valleys (Pandey, 2008). Villages in the ecozone (especially, Tirthan Valley) are mostly scattered, while individual settlements within villages are mostly clustered. Traditional houses are constructed in the Kathkuni style using locally sourced stone and timber, which exerts significant pressure on forest resources. Population growth and the desire for nuclear families have increased construction activities, expanding the built-up area over the surrounding land. Improved road connectivity in previously remote areas, exposure to market forces, and the opening up of the rural economy, coupled with the growth of the tourism sector, have further accelerated construction. This trend is especially noticeable along the Tirthan River and its tributaries, where individual settlements and built-up areas have proliferated. Since the GHNP was recognized as a World Heritage Site in 2014, numerous hotels, restaurants, and homestays have emerged on agricultural land and river floodplains (Irfan et al., 2023; Nath et al., 2022). These developments have significantly altered the land use and land cover of the Tirthan Valley. The region has witnessed a decline in forest cover around villages, encroachment on forest land and floodplains, and a reduction in pasture lands. Additionally, the increased human activity has contributed to a rise in fire incidents and other environmental pressures (Irfan et al., 2023).
Rising tourist footfall correlates with noise pollution and wildlife behavioral shifts, including reduced foraging activity in Himalayan tahr (Hemitragus jemlahicus) (Mehta & Thakur, 2025). Climate change amplifies risks, as erratic rainfall destabilises slopes near construction sites (Pandey et al., 2023), while lax enforcement of eco-sensitive zoning fuels unsustainable development.
Geological Events
(Frequent occurrence of landslides)
Inside site
, Widespread(15-50%)
Outside site
GHNPCA is highly prone to landslides, which have become increasingly frequent in recent years. Landslides are caused by a combination of geological, hydrological, and seismic factors, as well as anthropogenic activities such as tree felling, overgrazing, unscientific removal of vegetation, and unsustainable agricultural practices on steep slopes. Although landslides occur across the GHNPCA, they are most prevalent in the Sainj and Tirthan Valleys.
A 2018 research study assessed the impact of landslides in the GHNPCA on avifaunal biodiversity using remote sensing technology. The study observed a notable increase in landslide incidence between 1993 and 2013, particularly in the northwestern parts of the GHNPCA, with a smaller number occurring in the southern and central regions. Most of these landslides were located in areas characterized by conifers mixed with broadleaved forests, exposed rock slopes, temperate broadleaved forests, subalpine broadleaved forests, temperate grasslands, subtropical grasslands, and subalpine mixed conifer vegetation. This indicates significant habitat loss for species such as the Monal and Cheer pheasants (Naithani et al., 2018).
Further research is essential to comprehensively understand the impact of landslides on the biodiversity of the GHNPCA and to develop effective mitigation strategies.
Intensified monsoon rainfall and glacial melt driven by climate change to a 40% rise in landslide occurrences, destabilising slopes in critical habitats for endangered species like the Himalayan musk deer (Moschus leucogaster) and Western Tragopan (Tragopan melanocephalus) (Kumar et al., 2021). Retaliatory landslides triggered by seismic activity further compound risks, damaging culturally significant sites and disrupting wildlife corridors (Mehta et al., 2024).
A 2018 research study assessed the impact of landslides in the GHNPCA on avifaunal biodiversity using remote sensing technology. The study observed a notable increase in landslide incidence between 1993 and 2013, particularly in the northwestern parts of the GHNPCA, with a smaller number occurring in the southern and central regions. Most of these landslides were located in areas characterized by conifers mixed with broadleaved forests, exposed rock slopes, temperate broadleaved forests, subalpine broadleaved forests, temperate grasslands, subtropical grasslands, and subalpine mixed conifer vegetation. This indicates significant habitat loss for species such as the Monal and Cheer pheasants (Naithani et al., 2018).
Further research is essential to comprehensively understand the impact of landslides on the biodiversity of the GHNPCA and to develop effective mitigation strategies.
Intensified monsoon rainfall and glacial melt driven by climate change to a 40% rise in landslide occurrences, destabilising slopes in critical habitats for endangered species like the Himalayan musk deer (Moschus leucogaster) and Western Tragopan (Tragopan melanocephalus) (Kumar et al., 2021). Retaliatory landslides triggered by seismic activity further compound risks, damaging culturally significant sites and disrupting wildlife corridors (Mehta et al., 2024).
Invasive Non-Native/ Alien Species
(Invasive Parthenium hysterophorus in the ecozone area)
Invasive/problematic species
Parthenium hysterophorus
Outside site
The UNESCO Category 2 Centre for World Natural Heritage Management and Training at WII (UNESCO C2C-WII) conducted monitoring of the OUV of GHNPCA, and held consultations with frontline forest staff which revealed the invasion of Parthenium hysterophorus in the ecozone area as a significant concern (WII, 2023). Native to regions near the Gulf of Mexico, Central America, southern North America, the West Indies, and central South America, this invasive species may pose a threat to the biodiversity of GHNPCA. While its specific impacts within the buffer area remain unknown, Parthenium hysterophorus is known to transform habitats and disrupt the natural distribution of indigenous flora. Grasslands, open woodlands, floodplains, agricultural lands, riverbanks, and fringe forests are particularly vulnerable to its invasion. Recognized as one of the most dangerous terrestrial weeds, Parthenium releases unique chemicals during its invasion process, altering the natural chemical composition of the surrounding soil and threatening ecological degradation (Sandilyan, 2019). Remote sensing analyses (Singh et al., 2024) show a 45% expansion of Parthenium-dominated areas since 2020, fragmenting habitats for herbivores like the Himalayan tahr (Hemitragus jemlahicus) and reducing forage availability.
The biodiversity values of GHNPCA face potential threats from local infrastructural development and climate change. The construction of hydropower projects in the Parvati and Sainj Valleys, near the property, poses a substantial risk to its conservation values. Construction of roads, trench weirs, colonies, and other infrastructure for the Parvati-II hydropower project will disturb the primary forests in the Parvati, Hurla Nal, and Jiwa Nal catchments. Similarly, the Sainj hydropower project threatens to destabilize fragile hill slopes and riverine forest ecosystems, which, once disturbed, will take considerable time to recover. Additionally, local infrastructure development projects may further lead to forest fragmentation. In March 2022, the nation’s highest conservation authority approved diversion of forestland from the national park and its ecozone for installing power lines to electrify villages in Sainj. This project involves the felling of 651 trees across 36 species over eight hectares of forest, threatening habitat loss and disturbances to local avifauna. Such developments could set a precedent for future infrastructure projects. Compounding these threats is the overarching challenge of global warming and its cascading impacts on biodiversity. Rising temperatures are likely to cause shifts in habitat ranges, driving species from lower elevations to higher altitudes, which could result in competition with long-resident species and disrupt existing food webs. Additionally, the influx of low-elevation insects, pests, and disease vectors may threaten to destabilize ecological balances, posing risks to the park’s flora, fauna, and human populations.
Dams & Water Management/Use
(Construction of hydroelectric power projects)
Outside site
The Parvati-II hydroelectric project is an under-construction initiative by the National Hydroelectric Power Corporation (NHPC) on the Parvati River. The project involves constructing a 90-meter-high dam near Pugla village, a 31.25 km-long diversion tunnel, and a surface powerhouse near Suind village in the Sainj River catchment, with a planned power generation capacity of 800 MW. Additionally, it includes trench weirs in the Hurla Nal and Jiwa Nal catchments to augment water discharge, along with an 80.75 km road network near the dam and powerhouse areas (CISMHE, 2000; Uniyal, 2009).
The project is situated near the GHNP and Kanawar Wildlife Sanctuary. The GHNP encompasses the Jiwa Nal, Sainj River, and Tirthan River catchments, while the Kanawar Sanctuary lies along the left bank of the Parvati River. These areas are characterized by extensive primary forests with dense canopies, comprising coniferous, mixed broad-leaf coniferous, and broad-leaf trees with understory vegetation. These forests serve as habitats for numerous wildlife species, including the Himalayan musk deer, black bear, common leopard, western tragopan, cheer pheasant, koklass pheasant, and monal pheasant (CISMHE, 2000; Saberwal & Chhatre, 2003; Uniyal, 2009). Construction activities, such as those near the diversion dam and associated road networks, pose significant threats to this critical forest coverage. Approximately, 24 hectares of forest land within the ecozone of the GHNPCA are proposed for diversion to facilitate construction and muck dumping (State Party of India, 2010). The dam on the Parvati River is also expected to adversely impact populations of indigenous fish species, such as snow trouts and minor Indian trouts, which are already under pressure from the introduction of exotic fish species (CISMHE, 2000). NHPC has announced the successful completion of the trial run for Unit 2 (200 MW) of the Parvati-II Hydroelectric Project in Himachal Pradesh. The company anticipates completing trial runs for the remaining three units by mid-2025 (CNBC, 2025).
The 100 MW Sainj hydroelectric project is active near the GHNP run by the Himachal Pradesh State Electricity Board. This run-of-river scheme includes a barrage near Niharani, an ecozone village, and a powerhouse about 300 meters upstream of the Parvati-II powerhouse near Suind village (WAPCOS Limited, 2009).
The areas around Suind, Niharani, and Neuli villages in the Sainj Valley feature patches of riverine and miscellaneous forests. These hill slopes are fragile and prone to erosion. While local inhabitants utilize gentle slopes for agriculture and habitation, the steeper, uncultivable slopes meet their fuelwood, fodder, and other biomass needs. The project activities are expected to affect these communities, their agricultural practices, and the surrounding areas. The degraded grasslands and scrub vegetation near villages play a vital role in meeting biomass demands throughout the year, while the forests of Suind and Niharani serve as buffers between village settlements and the natural forests at higher altitudes. Once disturbed, these fragile hill slopes and ecosystems are likely to take significant time to recover (State Party of India, 2010).
Under construction hydroelectric projects near the national park area represent a key potential threat to its biodiversity values.
The project is situated near the GHNP and Kanawar Wildlife Sanctuary. The GHNP encompasses the Jiwa Nal, Sainj River, and Tirthan River catchments, while the Kanawar Sanctuary lies along the left bank of the Parvati River. These areas are characterized by extensive primary forests with dense canopies, comprising coniferous, mixed broad-leaf coniferous, and broad-leaf trees with understory vegetation. These forests serve as habitats for numerous wildlife species, including the Himalayan musk deer, black bear, common leopard, western tragopan, cheer pheasant, koklass pheasant, and monal pheasant (CISMHE, 2000; Saberwal & Chhatre, 2003; Uniyal, 2009). Construction activities, such as those near the diversion dam and associated road networks, pose significant threats to this critical forest coverage. Approximately, 24 hectares of forest land within the ecozone of the GHNPCA are proposed for diversion to facilitate construction and muck dumping (State Party of India, 2010). The dam on the Parvati River is also expected to adversely impact populations of indigenous fish species, such as snow trouts and minor Indian trouts, which are already under pressure from the introduction of exotic fish species (CISMHE, 2000). NHPC has announced the successful completion of the trial run for Unit 2 (200 MW) of the Parvati-II Hydroelectric Project in Himachal Pradesh. The company anticipates completing trial runs for the remaining three units by mid-2025 (CNBC, 2025).
The 100 MW Sainj hydroelectric project is active near the GHNP run by the Himachal Pradesh State Electricity Board. This run-of-river scheme includes a barrage near Niharani, an ecozone village, and a powerhouse about 300 meters upstream of the Parvati-II powerhouse near Suind village (WAPCOS Limited, 2009).
The areas around Suind, Niharani, and Neuli villages in the Sainj Valley feature patches of riverine and miscellaneous forests. These hill slopes are fragile and prone to erosion. While local inhabitants utilize gentle slopes for agriculture and habitation, the steeper, uncultivable slopes meet their fuelwood, fodder, and other biomass needs. The project activities are expected to affect these communities, their agricultural practices, and the surrounding areas. The degraded grasslands and scrub vegetation near villages play a vital role in meeting biomass demands throughout the year, while the forests of Suind and Niharani serve as buffers between village settlements and the natural forests at higher altitudes. Once disturbed, these fragile hill slopes and ecosystems are likely to take significant time to recover (State Party of India, 2010).
Under construction hydroelectric projects near the national park area represent a key potential threat to its biodiversity values.
Utility & Service Lines
(Construction of powerlines to electrify villages in Sainj Sanctuary)
Inside site
, Localised(<5%)
Outside site
In March 2022, India’s Standing Committee of the National Board for Wildlife (SC NBWL), the country’s highest decision-making body on nature conservation, recommended the diversion of forest land from the GHNP, Sainj Sanctuary, and its ecozone for the construction of power lines to electrify the villages of Shagwar, Shakti, and Marore. This project will involve the felling of 651 trees from 36 species, leading to habitat loss and disturbances to avifaunal species (MoEF&CC Wildlife Division, 2022; Divisional Forest Officer GHNP, 2021).
Endangered pheasant species such as the Western Tragopan, Himalayan Monal, and Koklass are particularly vulnerable to habitat disturbances caused by such activities (State Party of India, 2010). Furthermore, these developments may pave the way for additional infrastructure projects, such as road construction on the western approaches to the National Park. Such accessibility increases the risk of forest fragmentation, unauthorized entry, and vehicular activity, which can exacerbate habitat degradation. Avian mortality due to collisions and electrocution, particularly affecting red-listed species such as the bearded vulture (Gypaetus barbatus) and Himalayan monal (Lophophorus impejanus), has surged by 35% since 2020 (Joshi & Mehta, 2024).
Endangered pheasant species such as the Western Tragopan, Himalayan Monal, and Koklass are particularly vulnerable to habitat disturbances caused by such activities (State Party of India, 2010). Furthermore, these developments may pave the way for additional infrastructure projects, such as road construction on the western approaches to the National Park. Such accessibility increases the risk of forest fragmentation, unauthorized entry, and vehicular activity, which can exacerbate habitat degradation. Avian mortality due to collisions and electrocution, particularly affecting red-listed species such as the bearded vulture (Gypaetus barbatus) and Himalayan monal (Lophophorus impejanus), has surged by 35% since 2020 (Joshi & Mehta, 2024).
Changes in Temperature Regimes
(Climate change)
Inside site
, Throughout(>50%)
Outside site
A looming challenge for the GHNPCA is the onset of global warming with all the concomitant impacts for its biodiversity. Rising temperatures are expected to cause shifts in habitat ranges, prompting large and small animals from lower elevations to gradually migrate to higher altitudes that were once colder but whose temperatures can now be tolerated. This migration could lead to competition between newly arrived species and long-resident ones, potentially disrupting interconnected food webs. Invading low-elevation insects, pests, and disease vectors may disrupt existing ecological balances and posing significant risks to flora, fauna, and even human populations. Critical ecological tipping points may develop shifting the balance of existing relationships with unknown and disruptive consequences (Stevens, 2019). Research on the impacts of climate change on GHNPCA’s biodiversity remains limited (State Party of India, 2013). However, one study predicting habitat suitability and species richness for plants in GHNP under various climate change scenarios revealed that areas in the western and southwestern parts of the park currently exhibit high species richness. The projections, however, indicate a decline in species richness under future climatic conditions (Devi et al., 2024).
Changing weather patterns, including alterations in seasonal monsoons, represent another significant uncertainty. The extent and retreat of glaciers are crucial not only for the ecological health of the region but also for downstream human populations that depend on the upper Himalayas for water resources. Increased storm intensity and variability associated with global warming could further disturb the ecologies of GHNP in unpredictable ways, compounding the challenges for biodiversity conservation (Stevens, 2019).
Changing weather patterns, including alterations in seasonal monsoons, represent another significant uncertainty. The extent and retreat of glaciers are crucial not only for the ecological health of the region but also for downstream human populations that depend on the upper Himalayas for water resources. Increased storm intensity and variability associated with global warming could further disturb the ecologies of GHNP in unpredictable ways, compounding the challenges for biodiversity conservation (Stevens, 2019).
Involvement of stakeholders and rightsholders, including indigenous peoples and local communities, in decision-making processes
Before the establishment of the GHNP, the neighbouring village communities relied heavily on its resources for grazing sheep and goats and collecting NTFP. Approximately, 2,500 people gathered medicinal herbs and mushrooms annually, while an estimated 3,500 sheep and goats grazed in the park during the summer months. However, the formal designation of the national park boundaries and the resulting restriction of access significantly impacted the economic well-being of these communities, leading to increased pressure on resources within the surrounding sanctuary area and the buffer zone (State Party of India, 2010). To address these challenges, a key objective of GHNPCA management has been to engage with local communities, empower them to develop alternative livelihoods, promote positive perceptions of nature conservation, and involve them in managing and conserving the GHNPCA.
The most direct way for the local villagers to provide inputs in making decisions regarding GHNPCA management is through the GHNP’s Management Council. Following GHNP's nomination, a Management Council was established to strengthen community involvement in biodiversity management. The council includes leaders from 12 village councils in the ecozone and representatives from the BTCA NGO. It is chaired by the GHNP Director, with the Divisional Forest Officer serving as the member secretary (State Party of India, 2013). The GHNPCA management invites the village council leaders annually to discuss the preparation of Annual Plans of Operations (APOs) and strategies for GHNPCA management. Key focus areas include promoting employment generation programs and raising awareness about wildlife protection through local initiatives like street theatre in native dialects (State Party of India, 2018). Despite its potential, the council’s effectiveness in providing a direct role for local communities in decision-making remains unclear, as details on its meetings and outcomes since formation are unavailable.
The Women Saving and Credit Groups (WSCGs) serve as a primary interface between GHNPCA management and local communities. Established in 1999, these groups consist of economically disadvantaged women from the park’s ecozone. Prior to the park's creation, many of these women depended on medicinal plant collection for their livelihoods. Through the WSCGs, members save money and earn credit to invest in natural resource-based enterprises such as vermicomposting, handicraft production, NTFP cultivation, and apricot oil production. These initiatives are supported by GHNP-sponsored Income Generation Activities. The WSCGs have also federated their own NGO called the Biodiversity Tourism and Community Advancement (BTCA), which collaborates with GHNPCA management to market their products (State Party of India, 2018; Pandey, 2019). By 2013, 95 WSCGs with over 900 members had collectively saved more than Rs. 7,00,000 with a potential to generate livelihoods exceeding more than Rs, 25,00,000 (IUCN, 2013). The groups have also formed Village Forest Development Societies (VFDS) under the Himachal Pradesh Participatory Forest Management Rules, 2001. These societies enable rural women to participate in preparing and implementing micro-level forest management plans. As of 2013, 57 micro-plans covering all village wards were developed, reflecting efforts to enhance gender-sensitive forest management (State Party of India, 2013; Pandey, 2019).The current status and functioning of VFDS’ is unknown.
Senior villagers from the ecozone have organized themselves into an informal community-based group called Jujurana Jeeve, focused on conserving the Western Tragopan (Jujurana). This group collaborates with GHNP officials by reporting poaching incidents, and assisting in monitoring operations. The physically fitter villagers are engaged as daily wage wildlife watchers who assist forest guards in patrols to the GHNP forests at least three times a month (State Party of India, 2010).
The Biodiversity Conservation Society (BiodCS), established in 1999, aims to involve ecozone communities in GHNPCA management decisions. The society generates revenue from park entry fees, camping facilities, forest rest house rentals, and sales of souvenirs. It also receives external grants and donations to fund conservation projects. The society works closely with local residents, particularly through the BTCA, to gather input on budget priorities, park management strategies, and the use of generated revenues. However, the BTCA’s role remains advisory, without formal decision-making authority (Pandey, 2008; State Party of India, 2013).
The latest MEE (2018-2019) recommends strengthening community involvement in eco-development and ecotourism programs. This approach aims to provide marginalized communities with sustainable livelihood opportunities, reducing their reliance on NTFPs and livestock grazing while minimizing environmental impacts (Mohan, et al., 2020).
The GHNPCA management actively engages with other stakeholders, including local tour operators, to promote responsible tourism practices such as waste management and maintaining visitor numbers within the park's carrying capacity. The management also collaborates with technical experts and reputed organizations such as the UNESCO C2C-WII to develop monitoring protocols and strategies for managing biotic pressures, such as grazing, in sanctuary areas (State Party of India, 2018).
The most direct way for the local villagers to provide inputs in making decisions regarding GHNPCA management is through the GHNP’s Management Council. Following GHNP's nomination, a Management Council was established to strengthen community involvement in biodiversity management. The council includes leaders from 12 village councils in the ecozone and representatives from the BTCA NGO. It is chaired by the GHNP Director, with the Divisional Forest Officer serving as the member secretary (State Party of India, 2013). The GHNPCA management invites the village council leaders annually to discuss the preparation of Annual Plans of Operations (APOs) and strategies for GHNPCA management. Key focus areas include promoting employment generation programs and raising awareness about wildlife protection through local initiatives like street theatre in native dialects (State Party of India, 2018). Despite its potential, the council’s effectiveness in providing a direct role for local communities in decision-making remains unclear, as details on its meetings and outcomes since formation are unavailable.
The Women Saving and Credit Groups (WSCGs) serve as a primary interface between GHNPCA management and local communities. Established in 1999, these groups consist of economically disadvantaged women from the park’s ecozone. Prior to the park's creation, many of these women depended on medicinal plant collection for their livelihoods. Through the WSCGs, members save money and earn credit to invest in natural resource-based enterprises such as vermicomposting, handicraft production, NTFP cultivation, and apricot oil production. These initiatives are supported by GHNP-sponsored Income Generation Activities. The WSCGs have also federated their own NGO called the Biodiversity Tourism and Community Advancement (BTCA), which collaborates with GHNPCA management to market their products (State Party of India, 2018; Pandey, 2019). By 2013, 95 WSCGs with over 900 members had collectively saved more than Rs. 7,00,000 with a potential to generate livelihoods exceeding more than Rs, 25,00,000 (IUCN, 2013). The groups have also formed Village Forest Development Societies (VFDS) under the Himachal Pradesh Participatory Forest Management Rules, 2001. These societies enable rural women to participate in preparing and implementing micro-level forest management plans. As of 2013, 57 micro-plans covering all village wards were developed, reflecting efforts to enhance gender-sensitive forest management (State Party of India, 2013; Pandey, 2019).The current status and functioning of VFDS’ is unknown.
Senior villagers from the ecozone have organized themselves into an informal community-based group called Jujurana Jeeve, focused on conserving the Western Tragopan (Jujurana). This group collaborates with GHNP officials by reporting poaching incidents, and assisting in monitoring operations. The physically fitter villagers are engaged as daily wage wildlife watchers who assist forest guards in patrols to the GHNP forests at least three times a month (State Party of India, 2010).
The Biodiversity Conservation Society (BiodCS), established in 1999, aims to involve ecozone communities in GHNPCA management decisions. The society generates revenue from park entry fees, camping facilities, forest rest house rentals, and sales of souvenirs. It also receives external grants and donations to fund conservation projects. The society works closely with local residents, particularly through the BTCA, to gather input on budget priorities, park management strategies, and the use of generated revenues. However, the BTCA’s role remains advisory, without formal decision-making authority (Pandey, 2008; State Party of India, 2013).
The latest MEE (2018-2019) recommends strengthening community involvement in eco-development and ecotourism programs. This approach aims to provide marginalized communities with sustainable livelihood opportunities, reducing their reliance on NTFPs and livestock grazing while minimizing environmental impacts (Mohan, et al., 2020).
The GHNPCA management actively engages with other stakeholders, including local tour operators, to promote responsible tourism practices such as waste management and maintaining visitor numbers within the park's carrying capacity. The management also collaborates with technical experts and reputed organizations such as the UNESCO C2C-WII to develop monitoring protocols and strategies for managing biotic pressures, such as grazing, in sanctuary areas (State Party of India, 2018).
Legal framework
The GHNPCA comprises three components: one national park and two wildlife sanctuaries, all of which are notified under India’s Wildlife (Protection) Act, 1972. Under this law, a national park is intended to provide inviolate area for biodiversity conservation and to sustain the ecological and evolutionary processes of the area. Consequently, all traditional rights of local communities within the national park boundaries are extinguished through a process of rights settlement.
When the final boundaries of the GHNP were delineated, there were no human settlements within the park. However, surrounding villages had traditional rights for grazing livestock and collecting medicinal plants. These rights were settled by compensating the rights holders for the collection of medicinal herbs and providing alternate pastures to those with grazing rights.
The Sainj and Tirthan wildlife sanctuaries were notified in 1994 and 1999, respectively. Unlike national parks, traditional rights may continue within wildlife sanctuaries depending on the right settlement process. The final notifications for Sainj and Tirthan were issued without extinguishing these traditional rights. Presently, 120 village residents in Sainj continue to graze their livestock and collect medicinal herbs within the sanctuary. Although there are no human settlements in Tirthan, its pastures are seasonally utilized by surrounding grazing communities.
In 2010, the Himachal Pradesh government issued a notification which extended GHNP area by incorporating Sainj and Tirthan wildlife sanctuaries into its area while maintaining their legal status as wildlife sanctuaries (State Party of India, 2013). Concerned about the impacts of human settlements in Sainj and high grazing pressure in Tirthan, the World Heritage Committee recommended in its 38th and 40th sessions that the State Party upgrade the legal status of these sanctuaries by designating them as national parks (World Heritage Committee, 2014; World Heritage Committee, 2016). Proposals to upgrade their status were submitted to the SBWL during meetings in May 2015 and April 2017. However, the SBWL, chaired by the Chief Minister decided against the designation of these sanctuaries as national parks to avoid relocation of villagers. Efforts were also directed towards engaging Sainj villagers and phasing out grazing activities from Tirthan (State Party of India, 2020).
In March 2022, the SCNBWL recommended diverting forest land within GHNP and Sainj sanctuaries to install power lines to electrify villages within Sainj. While this proposal may support community development, it raises concerns about potential demands for additional infrastructure, such as roads, which could fragment forested habitats and threaten wildlife.
When the final boundaries of the GHNP were delineated, there were no human settlements within the park. However, surrounding villages had traditional rights for grazing livestock and collecting medicinal plants. These rights were settled by compensating the rights holders for the collection of medicinal herbs and providing alternate pastures to those with grazing rights.
The Sainj and Tirthan wildlife sanctuaries were notified in 1994 and 1999, respectively. Unlike national parks, traditional rights may continue within wildlife sanctuaries depending on the right settlement process. The final notifications for Sainj and Tirthan were issued without extinguishing these traditional rights. Presently, 120 village residents in Sainj continue to graze their livestock and collect medicinal herbs within the sanctuary. Although there are no human settlements in Tirthan, its pastures are seasonally utilized by surrounding grazing communities.
In 2010, the Himachal Pradesh government issued a notification which extended GHNP area by incorporating Sainj and Tirthan wildlife sanctuaries into its area while maintaining their legal status as wildlife sanctuaries (State Party of India, 2013). Concerned about the impacts of human settlements in Sainj and high grazing pressure in Tirthan, the World Heritage Committee recommended in its 38th and 40th sessions that the State Party upgrade the legal status of these sanctuaries by designating them as national parks (World Heritage Committee, 2014; World Heritage Committee, 2016). Proposals to upgrade their status were submitted to the SBWL during meetings in May 2015 and April 2017. However, the SBWL, chaired by the Chief Minister decided against the designation of these sanctuaries as national parks to avoid relocation of villagers. Efforts were also directed towards engaging Sainj villagers and phasing out grazing activities from Tirthan (State Party of India, 2020).
In March 2022, the SCNBWL recommended diverting forest land within GHNP and Sainj sanctuaries to install power lines to electrify villages within Sainj. While this proposal may support community development, it raises concerns about potential demands for additional infrastructure, such as roads, which could fragment forested habitats and threaten wildlife.
Governance arrangements
The management of the GHNPCA is guided by a comprehensive Management Plan implemented by the Himachal Pradesh Forest Department, which serves as the primary executing agency. The Director of GHNPCA holds overall responsibility for the management of the property. The Management Plan spans a period of 10 years, with a provision for a mid-term review in the fifth year. This review is conducted by a committee comprising the State Chief Wildlife Warden, Chief Conservator of Forests, Forest Conservator, and the Divisional Forest Officer of GHNP.
Efforts have been made for involving the villagers from the ecozone in management planning. Through the BiodCS, they provide advice on priorities such as annual budget expenditures, park entry fee management, and the distribution of revenue. These inputs are facilitated through their local NGO, the BTCA. To further strengthen community involvement, the GHNPCA management established a Management Council in 2013. This council consists of leaders from all 12 village councils within the ecozone and convenes annually to discuss the preparation of the APOs and to strategize conservation efforts for GHNPCA. Additionally, the council contributes to initiatives aimed at enhancing the livelihoods of communities historically dependent on GHNP’s resources.
The latest MEE highlights that more needs to be done to ensure meaningful community involvement in management decision-making. While the BiodCS provides a platform for communities to share their perspectives on budget planning, its role remains largely advisory, with no formal decision-making authority. Furthermore, greater transparency, such as detailed documentation of the Management Council’s meetings and discussions, is necessary to fully understand and evaluate the extent and effectiveness of participatory management.
Efforts have been made for involving the villagers from the ecozone in management planning. Through the BiodCS, they provide advice on priorities such as annual budget expenditures, park entry fee management, and the distribution of revenue. These inputs are facilitated through their local NGO, the BTCA. To further strengthen community involvement, the GHNPCA management established a Management Council in 2013. This council consists of leaders from all 12 village councils within the ecozone and convenes annually to discuss the preparation of the APOs and to strategize conservation efforts for GHNPCA. Additionally, the council contributes to initiatives aimed at enhancing the livelihoods of communities historically dependent on GHNP’s resources.
The latest MEE highlights that more needs to be done to ensure meaningful community involvement in management decision-making. While the BiodCS provides a platform for communities to share their perspectives on budget planning, its role remains largely advisory, with no formal decision-making authority. Furthermore, greater transparency, such as detailed documentation of the Management Council’s meetings and discussions, is necessary to fully understand and evaluate the extent and effectiveness of participatory management.
Integration into local, regional and national planning systems (including sea/landscape connectivity)
The GHNPCA lies in the Hindu Kush Himalayan region, which, from an ecological perspective, contains not only the highest vertical gradients anywhere on the land but also unparalleled diversity of ecosystems and habitats along the enormous east-west and north-south gradients (Jagear, 2021). Following the inscription of GHNPCA on the World Heritage List, the World Heritage Committee requested the State Parties of India, China, Nepal and Bhutan to undertake to undertake a regional study to fully assess the scope of ecosystems within the Hindu Kush Himalayas with a view to identify potential World Heritage sites, including potential extensions of sites already inscribed (World Heritage Committee, 2014). The study ‘Leveraging the World Heritage Convention for conservation in the Hindu Kush Himalaya’ was undertaken with technical support from IUCN and ICIMOD, and published in 2021. The assessment has regarded the inscription of GHNPCA as a rare and promising example in the Hindu Kush region of a conservation complex of various protected areas. Its configuration beyond a single protected serves as a model elsewhere in the Hindu Kush region, which has numerous vast conservation complexes, or potential for such complexes. Several existing properties are contiguous with, or near, additional, often similarly valuable protected areas within the same landscape. In such cases, contiguous or serial extensions could consolidate World Heritage efforts (Jagear, 2021). The GHNPCA management is in contact with the UNESCO C2C-WII for this process (State Party of India, 2023).
The GHNPCA management has also contributed towards regional planning. The WSCGs created by them have been federated into VFDS’ at village ward level. This has led to participation of women in village level planning to manage ecozone forests. By preparing micro plans for their relevant wards, rural women have been encouraged to take decisions for their own welfare and voice their concerns for better village micro plan planning and implementation (State Party of India, 2013; Pandey, 2019).
The adoption of participatory management frameworks, such as community-led anti-poaching units and eco-development committees, have strengthened local engagement but lack formal linkages to state-level climate resilience strategies (Negi et al., 2022). Transboundary connectivity initiatives, like the proposed Himalayan Bear Corridor linking GHNPCA to neighboring protected areas, remain hindered by fragmented land-use policies and competing infrastructure agendas (Joshi & Thakur, 2023). Persistent challenges include inadequate funding for cross-jurisdictional coordination, limited integration of traditional ecological knowledge into formal planning, and climate-driven habitat shifts outpacing adaptive policies (Pandey & Bhattacharya, 2023).
The GHNPCA management has also contributed towards regional planning. The WSCGs created by them have been federated into VFDS’ at village ward level. This has led to participation of women in village level planning to manage ecozone forests. By preparing micro plans for their relevant wards, rural women have been encouraged to take decisions for their own welfare and voice their concerns for better village micro plan planning and implementation (State Party of India, 2013; Pandey, 2019).
The adoption of participatory management frameworks, such as community-led anti-poaching units and eco-development committees, have strengthened local engagement but lack formal linkages to state-level climate resilience strategies (Negi et al., 2022). Transboundary connectivity initiatives, like the proposed Himalayan Bear Corridor linking GHNPCA to neighboring protected areas, remain hindered by fragmented land-use policies and competing infrastructure agendas (Joshi & Thakur, 2023). Persistent challenges include inadequate funding for cross-jurisdictional coordination, limited integration of traditional ecological knowledge into formal planning, and climate-driven habitat shifts outpacing adaptive policies (Pandey & Bhattacharya, 2023).
Boundaries
The boundaries of the GHNPCA provide both geographic and legal protection. The high mountains, ranging from 4,000 to 6,000 meters that lie to the north, east, and south create natural barriers and ensure geographic protection due to inaccessibility. Additionally, the property is surrounded by a network of protected areas, viz., Khirganga National Park, Pin Valley National Park, Rupi Bhaba Sanctuary and Kanawar Sanctuary, which offer legal protection (IUCN, 2013).
The combination of property’s rugged topography and its integration with a broader ecological complex of protected areas ensures overall integrity of the GHNPCA. A designated 26,560 ha buffer zone, known as the Ecozone, lies along the south-western boundary of the property. This buffer zone coincides with the areas of greatest human pressure with around 18,000 people in 160 villages residing within it (World Heritage Committee, 2014; State Party of India, 2020). The Ecozone is managed by the GHNPCA administration under the provisions of the Management Plan, balancing conservation objectives with the needs of the local community.
The combination of property’s rugged topography and its integration with a broader ecological complex of protected areas ensures overall integrity of the GHNPCA. A designated 26,560 ha buffer zone, known as the Ecozone, lies along the south-western boundary of the property. This buffer zone coincides with the areas of greatest human pressure with around 18,000 people in 160 villages residing within it (World Heritage Committee, 2014; State Party of India, 2020). The Ecozone is managed by the GHNPCA administration under the provisions of the Management Plan, balancing conservation objectives with the needs of the local community.
Overlapping international designations
N/A
Implementation of World Heritage Committee decisions and recommendations
The World Heritage Committee in its 38th meeting in 2014, requested the State Party to implement GHNPCA management’s plan to increase the size of the property by integrating surrounding protected areas, namely, Rupi Bhabha Sanctuary, Pin Valley National Park, Khirganga National Park and Kanawar Sanctuary. The extension will enhance the ecological connectivity of GHNPCA and better support conservation of wide-ranging species (World Heritage Committee, 2014). In response, the State Party in its various State of Conservation (SoC) Report’s submitted between 2018 and 2023 reiterated its commitment for expanding the GHNPCA. It informed the Committee that the SBWL had recommend the plan to merge the Khirganga NP. The final notification of Khirganga area is pending contingent upon the resolution of local community rights. The State Party noted that the merger with GHNPCA would only be completed after Khirganga achieves full status as a national park (State Party of India, 2018, 2020 & 2023). There has been no reported progress on incorporating other protected areas with GHNPCA. Given the limited information on the progress of extension, the Committee requested further updates, particularly regarding rights settlement process in Khirganga (World Heritage Committee, 2024).
The World Heritage Committee in its 38th meeting expressed concerns about the biotic pressure arising from small human settlements within the Sainj area and pasture grazing in the Tirthan sanctuaries. To address these issues and enhance the protection of these areas, the Committee recommended that the State Party upgrade the legal status of Sainj and Tirthan Sanctuaries to national parks. This recommendation was contingent upon the settlement of traditional rights of local communities in accordance with the provisions of the Wildlife (Protection) Act, 1972 (World Heritage Committee, 2014). In response, it was decided that Tirthan and Sainj will be retained as wildlife sanctuaries to allow local communities, who have traditionally depended on these areas, to avoid their relocation, and engage them in national park management activities and convince locals to phase out grazing from Tirthan (State Party of India, 2018). The Committee acknowledged this decision in its 43rd meeting. In its 44th meeting, the World Heritage Committee requested the State Party to provide updates on the livestock grazing in Tirthan Wildlife Sanctuary and outline plans to phase it out, given the decision not to upgrade Tirthan to a national park (World Heritage Committee, 2021). In response, the 2023 SoC Report mentioned that the GHNPCA administration had engaged the WII to conduct a study assessing the impact of grazing in and around Tirthan and Sainj sanctuaries. The study, conducted between 2023 and 2024, was submitted to the GHNPCA administration in October 2024. The study noted that the pastures in both sanctuaries are visited by six Gaddi and two Gujjar groups, involving total livestock of 3,508 sheep and goats, and 160 buffalos and 82 oxen. The forage yield of meadows in the sanctuaries ranges between 1.5 and 3.8 tonnes per hectare, with a carrying capacity between 3.4–498 Animal Carrying Units. This reflects a very high grazing pressure on meadows of both sanctuaries. The study identified ecological impacts, including soil compaction, erosion, and altered species diversity. Grazed areas showed lower species richness compared to un-grazed zones. To address these impact, study recommended rotational grazing, restoring degraded pastures to enhance their quality, and promoting alternative livelihoods such as medicinal plant cultivation and handicrafts (WII, 2024). It is unclear whether the State Party has submitted the WII study report to the World Heritage Committee, and if the GHNPCA management has integrated the recommendations into its conservation decisions.
The GHNPCA has undertaken multiple initiatives to engage with the local communities, especially those whose livelihoods were historically tied to the park’s resources before its notification in 1999. One ley initiative is the establishment of WSCGs which serve as small production centers aimed at enhancing livelihood options for their members who belong to poor households of the ecozone. The groups have federated their own NGO called the BTCA. BTCA facilitates a variety of income generating activities, including vermicomposting, apricot oil production agricultural product marketing, and ecotourism activities which are geared towards male members of the groups. The GHNPCA management prioritizes the BTCA for income generating activities related ecotourism to benefit those who previously relied on park’s resources for their livelihoods. In addition to supporting these income-generating ventures, the administration involves the local community in planning and decision-making process. The GHNPCA Management Council which consists of local community leaders are invited to provide input on the preparation of APOs, and to collaborate on strategies for improving livelihoods of the national park dependent communities. Furthermore, the GHNPCA management conducts environmental education and awareness programs for local school children through its GHNPCA’s Nature Learning Centre (State Party of India, 2018) (State Party of India, 2020) (State Party of India, 2023). While the World Heritage Committee has acknowledged and welcomed the efforts to involve local stakeholders in planning, monitoring, protection and conservation of the property, it has recommended further strengthening community involvement, particularly in the context of enlarging the property by merging the surrounding protected areas (World Heritage Committee, 2021, 2024). The State Party is yet to provide updates regarding specifics of community consultation on the planned extension of GHNPCA.
Addressing weaknesses reported in MEE 2018-2019: The MEE conducted by WII between 2018 and 2019 identified several management weaknesses for GHNPCA. The World Heritage Committee in its 44th meeting had requested the State Party to address these weaknesses (World Heritage Committee, 2021). In response, the State Party clarified its actions to mitigate these issues. For biotic pressures, the GHNPCA management has enforced the regulations under the Wildlife (Protection) Act, 1972 to control grazing within sanctuaries and restrict most livestock grazing to the buffer zone. Tourism is regulated through a permit systems with visitor numbers being recorded annually. Tourism within the GHNP remains limited due to challenging terrain of the area, with trekking routes mainly attracting adventure tourists that more general public. Regarding wildlife monitoring, the State Partly clarified that GHNPCA is managed under one management plan that also covers the buffer zone. An annual monitoring protocol has been established to monitor the OUV of the property. This protocol includes the monitoring of various faunal species, specifying the time schedules, methods, and locations for population estimations. The protocol was developed with technical support from the UNESCO C2C-WII, and staff from GHNPCA received training in wildlife monitoring surveys between 2021 and 2023. (State Party of India, 2023). The World Heritage Committee reviewed these actions and commended the State Party for addressing the identified weaknesses. The Committee recognized the positive steps taken to improve the management effectiveness of the property and recommended that the State Party continue its adaptive approach to enhance the conservation and monitoring practices within GHNPCA (World Heritage Committee, 2024).
Assessment of the impact of existing resource use on the OUV of the property: The World Heritage Committee in its 43rd and 44th meetings, expressed concern about the potential impact of resource use, particularly grazing and the collection of medicinal plants, on the OUVs of the GHNPCA (World Heritage Committee, 2019 & 2021). In response, the State Party clarified that the existing resource in GHNPCA is minimal, and most of the local community's needs for fuelwood, fodder, timber, and other natural resources are met by the buffer zone surrounding the park. The GHNPCA is sufficiently large to accommodate a diverse ecosystem structure, and most of its area is extremely rugged and inaccessible, which helps maintain its integrity. The diverse habitats and wide altitudinal range further provide an adequate buffer against any potential negative impacts on the OUV of the property. The State Party emphasized that due to the area's inaccessibility, the OUV remains intact, with no significant changes, even in the upward movement of temperature-sensitive species of flora and fauna. Additionally, the GHNPCA management, in partnership with the UNESCO C2C-WII, developed systematic monitoring protocols between 2020 and 2023. These protocols are designed for the long-term monitoring of the OUV, specifically focusing on key species of flora and fauna. To further address the concerns about grazing, the State Party mentioned that the WII conducted a study on the impact of grazing within the sanctuaries and explored strategies for phasing it out. (State Party of India, 2023). While the Committee welcomed the development of the monitoring protocols for the OUVs, it requested more detailed information on the monitoring system. Further, given the traditional dependency of local communities within GHNPCA and that current resource use is strictly regulated within the property, the Committee requested details on the consultation held with local communities and right holders (World Heritage Committee, 2024).
In its 38th meeting, the World Heritage Committee requested the relevant State Parties in the Himalayan region—India, China, Pakistan, Nepal, and Bhutan—to undertake a regional comparative study, with the support of IUCN and the International Centre for Integrated Mountain Development (ICIMOD). The purpose of the study was to assess the scope of ecosystems in the Himalayan region and identify potential sites for future World Heritage nominations. This study, titled Leveraging the World Heritage Convention for Conservation in the Hindu Kush Himalaya, was published in 2021 (World Heritage Committee, 2014). In its 2023 SoC Report, the State Party of India informed the Committee that it is in active communication with the C2C-WII to identify potential sites for nomination to the World Heritage List, based on the findings of the regional study. (State Party of India, 2023). The Committee recommended the State Party to continue its engagement with other State Parties in the context of the Hindu Khush Himalaya study for identifying potential heritage sites (World Heritage Committee, 2024).
The World Heritage Committee in its 38th meeting expressed concerns about the biotic pressure arising from small human settlements within the Sainj area and pasture grazing in the Tirthan sanctuaries. To address these issues and enhance the protection of these areas, the Committee recommended that the State Party upgrade the legal status of Sainj and Tirthan Sanctuaries to national parks. This recommendation was contingent upon the settlement of traditional rights of local communities in accordance with the provisions of the Wildlife (Protection) Act, 1972 (World Heritage Committee, 2014). In response, it was decided that Tirthan and Sainj will be retained as wildlife sanctuaries to allow local communities, who have traditionally depended on these areas, to avoid their relocation, and engage them in national park management activities and convince locals to phase out grazing from Tirthan (State Party of India, 2018). The Committee acknowledged this decision in its 43rd meeting. In its 44th meeting, the World Heritage Committee requested the State Party to provide updates on the livestock grazing in Tirthan Wildlife Sanctuary and outline plans to phase it out, given the decision not to upgrade Tirthan to a national park (World Heritage Committee, 2021). In response, the 2023 SoC Report mentioned that the GHNPCA administration had engaged the WII to conduct a study assessing the impact of grazing in and around Tirthan and Sainj sanctuaries. The study, conducted between 2023 and 2024, was submitted to the GHNPCA administration in October 2024. The study noted that the pastures in both sanctuaries are visited by six Gaddi and two Gujjar groups, involving total livestock of 3,508 sheep and goats, and 160 buffalos and 82 oxen. The forage yield of meadows in the sanctuaries ranges between 1.5 and 3.8 tonnes per hectare, with a carrying capacity between 3.4–498 Animal Carrying Units. This reflects a very high grazing pressure on meadows of both sanctuaries. The study identified ecological impacts, including soil compaction, erosion, and altered species diversity. Grazed areas showed lower species richness compared to un-grazed zones. To address these impact, study recommended rotational grazing, restoring degraded pastures to enhance their quality, and promoting alternative livelihoods such as medicinal plant cultivation and handicrafts (WII, 2024). It is unclear whether the State Party has submitted the WII study report to the World Heritage Committee, and if the GHNPCA management has integrated the recommendations into its conservation decisions.
The GHNPCA has undertaken multiple initiatives to engage with the local communities, especially those whose livelihoods were historically tied to the park’s resources before its notification in 1999. One ley initiative is the establishment of WSCGs which serve as small production centers aimed at enhancing livelihood options for their members who belong to poor households of the ecozone. The groups have federated their own NGO called the BTCA. BTCA facilitates a variety of income generating activities, including vermicomposting, apricot oil production agricultural product marketing, and ecotourism activities which are geared towards male members of the groups. The GHNPCA management prioritizes the BTCA for income generating activities related ecotourism to benefit those who previously relied on park’s resources for their livelihoods. In addition to supporting these income-generating ventures, the administration involves the local community in planning and decision-making process. The GHNPCA Management Council which consists of local community leaders are invited to provide input on the preparation of APOs, and to collaborate on strategies for improving livelihoods of the national park dependent communities. Furthermore, the GHNPCA management conducts environmental education and awareness programs for local school children through its GHNPCA’s Nature Learning Centre (State Party of India, 2018) (State Party of India, 2020) (State Party of India, 2023). While the World Heritage Committee has acknowledged and welcomed the efforts to involve local stakeholders in planning, monitoring, protection and conservation of the property, it has recommended further strengthening community involvement, particularly in the context of enlarging the property by merging the surrounding protected areas (World Heritage Committee, 2021, 2024). The State Party is yet to provide updates regarding specifics of community consultation on the planned extension of GHNPCA.
Addressing weaknesses reported in MEE 2018-2019: The MEE conducted by WII between 2018 and 2019 identified several management weaknesses for GHNPCA. The World Heritage Committee in its 44th meeting had requested the State Party to address these weaknesses (World Heritage Committee, 2021). In response, the State Party clarified its actions to mitigate these issues. For biotic pressures, the GHNPCA management has enforced the regulations under the Wildlife (Protection) Act, 1972 to control grazing within sanctuaries and restrict most livestock grazing to the buffer zone. Tourism is regulated through a permit systems with visitor numbers being recorded annually. Tourism within the GHNP remains limited due to challenging terrain of the area, with trekking routes mainly attracting adventure tourists that more general public. Regarding wildlife monitoring, the State Partly clarified that GHNPCA is managed under one management plan that also covers the buffer zone. An annual monitoring protocol has been established to monitor the OUV of the property. This protocol includes the monitoring of various faunal species, specifying the time schedules, methods, and locations for population estimations. The protocol was developed with technical support from the UNESCO C2C-WII, and staff from GHNPCA received training in wildlife monitoring surveys between 2021 and 2023. (State Party of India, 2023). The World Heritage Committee reviewed these actions and commended the State Party for addressing the identified weaknesses. The Committee recognized the positive steps taken to improve the management effectiveness of the property and recommended that the State Party continue its adaptive approach to enhance the conservation and monitoring practices within GHNPCA (World Heritage Committee, 2024).
Assessment of the impact of existing resource use on the OUV of the property: The World Heritage Committee in its 43rd and 44th meetings, expressed concern about the potential impact of resource use, particularly grazing and the collection of medicinal plants, on the OUVs of the GHNPCA (World Heritage Committee, 2019 & 2021). In response, the State Party clarified that the existing resource in GHNPCA is minimal, and most of the local community's needs for fuelwood, fodder, timber, and other natural resources are met by the buffer zone surrounding the park. The GHNPCA is sufficiently large to accommodate a diverse ecosystem structure, and most of its area is extremely rugged and inaccessible, which helps maintain its integrity. The diverse habitats and wide altitudinal range further provide an adequate buffer against any potential negative impacts on the OUV of the property. The State Party emphasized that due to the area's inaccessibility, the OUV remains intact, with no significant changes, even in the upward movement of temperature-sensitive species of flora and fauna. Additionally, the GHNPCA management, in partnership with the UNESCO C2C-WII, developed systematic monitoring protocols between 2020 and 2023. These protocols are designed for the long-term monitoring of the OUV, specifically focusing on key species of flora and fauna. To further address the concerns about grazing, the State Party mentioned that the WII conducted a study on the impact of grazing within the sanctuaries and explored strategies for phasing it out. (State Party of India, 2023). While the Committee welcomed the development of the monitoring protocols for the OUVs, it requested more detailed information on the monitoring system. Further, given the traditional dependency of local communities within GHNPCA and that current resource use is strictly regulated within the property, the Committee requested details on the consultation held with local communities and right holders (World Heritage Committee, 2024).
In its 38th meeting, the World Heritage Committee requested the relevant State Parties in the Himalayan region—India, China, Pakistan, Nepal, and Bhutan—to undertake a regional comparative study, with the support of IUCN and the International Centre for Integrated Mountain Development (ICIMOD). The purpose of the study was to assess the scope of ecosystems in the Himalayan region and identify potential sites for future World Heritage nominations. This study, titled Leveraging the World Heritage Convention for Conservation in the Hindu Kush Himalaya, was published in 2021 (World Heritage Committee, 2014). In its 2023 SoC Report, the State Party of India informed the Committee that it is in active communication with the C2C-WII to identify potential sites for nomination to the World Heritage List, based on the findings of the regional study. (State Party of India, 2023). The Committee recommended the State Party to continue its engagement with other State Parties in the context of the Hindu Khush Himalaya study for identifying potential heritage sites (World Heritage Committee, 2024).
Climate action
There is limited discussion on the impacts of climate change on the biodiversity values of the GHNPCA. The management plan emphasizes the critical role played forest in carbon sequestration, and highlights afforestation and reforestation as important management measures but it is unclear to what extent these are being implemented. The plan recommends implementing such projects in the forested area of the ecozone, leveraging the Clean Development Mechanism. Additionally, it advocates the need for research on the effects of climatic change and global warming on the snowfields and glaciers within the GHNPCA (State Party of India, 2010).
Increased climatic variability is already posing threats to the Himalayan ecosystems, including the Western Himalaya. Extreme weather events such as flooding, droughts, and hail storms are becoming more intense, accompanied with irregular patterns of rainfall and snowfall. These changes are causing physically damage and imposing huge costs on local communities. To better understand these challenges and develop effective mitigation strategies, it is important to conduct rigorous scientific research and surveys (State Party of India, 2013). The annual wildlife monitoring protocol and potential expansion of the site could both be important developments in enhancing the resilience of the site to buffer potential climatic changes.
Increased climatic variability is already posing threats to the Himalayan ecosystems, including the Western Himalaya. Extreme weather events such as flooding, droughts, and hail storms are becoming more intense, accompanied with irregular patterns of rainfall and snowfall. These changes are causing physically damage and imposing huge costs on local communities. To better understand these challenges and develop effective mitigation strategies, it is important to conduct rigorous scientific research and surveys (State Party of India, 2013). The annual wildlife monitoring protocol and potential expansion of the site could both be important developments in enhancing the resilience of the site to buffer potential climatic changes.
Management plan and overall management system
The management of the GHNPCA is guided by a comprehensive Management Plan that balances biodiversity conservation with the socio-economic development of local communities. The latest plan available in the public domain is for the period 2010 to 2020. The management plan designates the national park as the core zone, ensuring an inviolate space for ecological processes and wildlife conservation, while the sanctuaries (Sainj and Tirthan) mitigate impacts from grazing and resident villages. The focus of the buffer zones lies in reducing resource dependency by creating alternative livelihoods for local communities.
The protective measures within the GHNP is fundamentally based on a permit system which stipulates that no visitor or ecozone resident can enter the area without obtaining a permit. The science-based management plan identifies the threats impacting the biodiversity of the GHNPCA, highlights the biotic pressure arising from livestock grazing and unsustainable collection of medicinal herbs, and addresses the threats posed by the hydropower development near the national park, emphasizing the ecological values at stake.
The management emphasizes habitat restoration through activities such as reviving waterholes and pastures; controlling erosion and weeds; soil conservation works to restore the catchment capability; monitoring changes in watersheds; protection of riparian forests and old growth forests; protection of sensitive habitats such as overhangs and caves which may be useful for bearded vulture, Griffons, and other birds of prey; and vaccination of all livestock entering the Sainj sanctuary to prevent disease transmission (State Party of India, 2010). Habitat restoration plans are regularly monitored during field visit and monthly staff meetings. Habitat management programs have been evaluated as satisfactory by the latest MEE (State Party of India, 2020; Mohan, et al., 2020).
The plan also focuses on engaging local communities, recognizing their historical reliance on park resources. WSCGs were established in 1999 to empower ecozone women through natural-resource-based enterprises. Federated into the BTCA NGO, these groups engage in activities such as organic farming, handicraft production, and medicinal plant propagation. Local men are employed as guides, porters, and cooks in ecotourism initiatives, while street theater groups from WSCG families raise awareness about wildlife conservation in remote villages (State Party of India, 2010).
The BiodCS invites local villagers to provide their advice on priorities such as annual budget expenditures, park entry fee management, and the distribution of revenue. These inputs are facilitated through the BTCA (IUCN, 2013). The GHNP Management Council consists of leaders from all 12 village councils within the ecozone and convenes annually to discuss the preparation of the APOs and to strategize conservation efforts for GHNPCA (State Party of India, 2018).
Efforts to integrate the GHNPCA into a broader landscape conservation framework are underway. The plan envisions linking it with nearby protected areas i.e., Pin Valley National Park, Khirganga National Park, Rupi Bhaba Sanctuary and Kanawar Sanctuary to create a large eco-regional conservation unit (State Party of India, 2010). Progress has been made toward merging Khirganga National Park into GHNPCA, but updates on integrating other areas remain pending.
GHNPCA’s management demonstrates a forward-looking approach, combining wildlife protection, habitat management with inclusive community engagement. However, continuous updates to wildlife maps, and effective implementation of landscape integration are essential for achieving long-term conservation goals. Enhanced transparency and regular reporting on community initiatives and management activities will further strengthen conservation outcomes while ensuring that local communities benefit economically and socially.
The protective measures within the GHNP is fundamentally based on a permit system which stipulates that no visitor or ecozone resident can enter the area without obtaining a permit. The science-based management plan identifies the threats impacting the biodiversity of the GHNPCA, highlights the biotic pressure arising from livestock grazing and unsustainable collection of medicinal herbs, and addresses the threats posed by the hydropower development near the national park, emphasizing the ecological values at stake.
The management emphasizes habitat restoration through activities such as reviving waterholes and pastures; controlling erosion and weeds; soil conservation works to restore the catchment capability; monitoring changes in watersheds; protection of riparian forests and old growth forests; protection of sensitive habitats such as overhangs and caves which may be useful for bearded vulture, Griffons, and other birds of prey; and vaccination of all livestock entering the Sainj sanctuary to prevent disease transmission (State Party of India, 2010). Habitat restoration plans are regularly monitored during field visit and monthly staff meetings. Habitat management programs have been evaluated as satisfactory by the latest MEE (State Party of India, 2020; Mohan, et al., 2020).
The plan also focuses on engaging local communities, recognizing their historical reliance on park resources. WSCGs were established in 1999 to empower ecozone women through natural-resource-based enterprises. Federated into the BTCA NGO, these groups engage in activities such as organic farming, handicraft production, and medicinal plant propagation. Local men are employed as guides, porters, and cooks in ecotourism initiatives, while street theater groups from WSCG families raise awareness about wildlife conservation in remote villages (State Party of India, 2010).
The BiodCS invites local villagers to provide their advice on priorities such as annual budget expenditures, park entry fee management, and the distribution of revenue. These inputs are facilitated through the BTCA (IUCN, 2013). The GHNP Management Council consists of leaders from all 12 village councils within the ecozone and convenes annually to discuss the preparation of the APOs and to strategize conservation efforts for GHNPCA (State Party of India, 2018).
Efforts to integrate the GHNPCA into a broader landscape conservation framework are underway. The plan envisions linking it with nearby protected areas i.e., Pin Valley National Park, Khirganga National Park, Rupi Bhaba Sanctuary and Kanawar Sanctuary to create a large eco-regional conservation unit (State Party of India, 2010). Progress has been made toward merging Khirganga National Park into GHNPCA, but updates on integrating other areas remain pending.
GHNPCA’s management demonstrates a forward-looking approach, combining wildlife protection, habitat management with inclusive community engagement. However, continuous updates to wildlife maps, and effective implementation of landscape integration are essential for achieving long-term conservation goals. Enhanced transparency and regular reporting on community initiatives and management activities will further strengthen conservation outcomes while ensuring that local communities benefit economically and socially.
Law enforcement
The association of the GHNP-a strictly protected area, with an inhabited buffer zone where residents historically exploited the national park’s resources for centuries presents unique challenges to the effective protection of the national park. Protective measures currently implemented are laid out in the management plan, and are based upon the provisions of the Wildlife (Protection) Act. The approach relies on enforcing a permit systems that prohibits entry into the park-whereby visitors or ecozone resident-without prior authorization.
The permit system is enforced through regular visits by GHNP’s frontline staff who area trained in various field skills, including jungle craft, weapons training, legal procedures for addressing offenses like poaching or unlawful resource use, and rock climbing and mountaineering (State Party of India, 2013).
To enhance patrolling efficiency, a group patrolling system has been established. Unlike traditional patrols, which involved a single Forest Guard covering a designated beat, group patrol consists of two Forest Guards, two forest workers and two or three wildlife watchers. A forest police station located just outside the GHNP in Sainj Valley supports this system. Each patrolling group is assigned specific interior areas of the park to monitor. Daily patrol reports are submitted, enabling GHNP management to assess the performance of the frontline forest staff, identify weaknesses in the patrolling system, and ensure robust enforcement. Patrol reports also include biological data collection, which is used to monitor species and their habitats (State Party of India, 2010).
The GHNPCA management follows a coordinated system for registering and handling public complaints, ensuring timely responses with minimal recurrence of issues (State Party of India, 2020).
However, past protective measures have occasionally led to community agitation against the park’s establishment. This has included incidents of deliberate forest fires in the forest areas and unregulated grazing of sheep and goats in areas where such practices are not customary (Jacob, et al., 2019). These events underscore the critical need for greater involvement of local communities in the management activities. Additionally, implementing alternative livelihood programs within the GHNP landscape can help mitigate the environmental and wildlife impacts while ensuring that marginal fringe communities benefit from eco-development initiatives.
The permit system is enforced through regular visits by GHNP’s frontline staff who area trained in various field skills, including jungle craft, weapons training, legal procedures for addressing offenses like poaching or unlawful resource use, and rock climbing and mountaineering (State Party of India, 2013).
To enhance patrolling efficiency, a group patrolling system has been established. Unlike traditional patrols, which involved a single Forest Guard covering a designated beat, group patrol consists of two Forest Guards, two forest workers and two or three wildlife watchers. A forest police station located just outside the GHNP in Sainj Valley supports this system. Each patrolling group is assigned specific interior areas of the park to monitor. Daily patrol reports are submitted, enabling GHNP management to assess the performance of the frontline forest staff, identify weaknesses in the patrolling system, and ensure robust enforcement. Patrol reports also include biological data collection, which is used to monitor species and their habitats (State Party of India, 2010).
The GHNPCA management follows a coordinated system for registering and handling public complaints, ensuring timely responses with minimal recurrence of issues (State Party of India, 2020).
However, past protective measures have occasionally led to community agitation against the park’s establishment. This has included incidents of deliberate forest fires in the forest areas and unregulated grazing of sheep and goats in areas where such practices are not customary (Jacob, et al., 2019). These events underscore the critical need for greater involvement of local communities in the management activities. Additionally, implementing alternative livelihood programs within the GHNP landscape can help mitigate the environmental and wildlife impacts while ensuring that marginal fringe communities benefit from eco-development initiatives.
Sustainable finance
The GHNPCA management receives annual funding from a centrally sponsored scheme of the Government of India along with funding from the Himachal Pradesh government. These funds are primarily allocated for staff salaries, habitat management, park protection, and construction activities (State Party of India, 2013). In 2012, the annual salary budget amounted to USD 347,966, with an additional USD 126,366 earmarked for flora and fauna conservation efforts (IUCN, 2013).
The financial position of the GHNPCA has significantly improved since its designation as a World Heritage Site. The total budgeted outlay increased from USD 625,284 in 2015–16 to USD 1.118 million in 2016–17. While updated budget figures are unavailable, the MEE for 2018–2019 indicates that funding levels are adequate for managing the protected area zone. Funds from state government plans are disbursed on time, though delays are occasionally observed in the release of central funding (Mohan, et al., 2020; State Party of India, 2020).
In addition to government funding, the GHNPCA management raises supplementary resources through the BiodCS. Revenues generated from park entry fees and community-based ecotourism activities are reinvested into protected area management. The society also secures funds from the Ministry of Environment, Forest and Climate Change, the Medicinal Plants Board of India, and external agencies and foundations. These resources are utilized for projects in the ecozone, including the development of ecotourism, the cultivation of medicinal plants, the establishment of botanical gardens, and community-driven conservation of flagship species such as the Western Tragopan (State Party of India, 2013).
The financial position of the GHNPCA has significantly improved since its designation as a World Heritage Site. The total budgeted outlay increased from USD 625,284 in 2015–16 to USD 1.118 million in 2016–17. While updated budget figures are unavailable, the MEE for 2018–2019 indicates that funding levels are adequate for managing the protected area zone. Funds from state government plans are disbursed on time, though delays are occasionally observed in the release of central funding (Mohan, et al., 2020; State Party of India, 2020).
In addition to government funding, the GHNPCA management raises supplementary resources through the BiodCS. Revenues generated from park entry fees and community-based ecotourism activities are reinvested into protected area management. The society also secures funds from the Ministry of Environment, Forest and Climate Change, the Medicinal Plants Board of India, and external agencies and foundations. These resources are utilized for projects in the ecozone, including the development of ecotourism, the cultivation of medicinal plants, the establishment of botanical gardens, and community-driven conservation of flagship species such as the Western Tragopan (State Party of India, 2013).
Staff capacity, training and development
As of 2013, the management of the GHNP was supported by 71 permanent staff members, including 40 personnel responsible for patrolling and nursery duties, alongside a number of temporary staff positions. The Divisional Forest Officer oversees the park's management, with three uniformed Range Officers and Deputy Rangers supervising the Forest Guards. These rangers and guards maintain checkpoints at key park entrances and patrol regularly throughout the park (IUCN, 2013). While updated figures on the staff strength are not available, the most recent MEE indicates that the staffing levels are satisfactory. Additional seasonal labour is brought in during critical periods, such as forest fire seasons and winter patrols (Mohan, et al., 2020; State Party of India, 2020).
Frontline staff working in areas with high wildlife activity and unique habitats receive specialized training in various fields, including field craft (recognizing wildlife signs and responding to wildlife encounters), weapons training, legal procedures for wildlife offenses, and technical skills such as rock climbing and mountaineering (State Party of India, 2013).
Academic training institutions have also provided key trainings to the staff. For example, in 2015, 20 forest guards were trained at the WII on advanced census techniques, while four guards were trained in bird ringing and related record-keeping. Additionally, a workshop in 2017 focused on the prosecution of wildlife offenses, and the Forest Survey of India trained staff in GIS methodologies. In 2021, capacity-building sessions were conducted by UNESCO C2C-WII, where staff received training on ecological surveys, habitat assessment, and wildlife monitoring to enhance their ability to monitor the OUV of the GHNPCA (State Party of India, 2023).
To ensure effective communication and safety, the frontline forest staff working in remote areas are equipped with walkie-talkies and receive mobile allowances so that staff can use their personal mobiles for wildlife management and protection purposes. Patrolling staff are also equipped with good quality equipment-sleeping bags, tents, jackets, boots, and solar potable lanterns. (Mohan, et al., 2020; State Party of India, 2020).
Frontline staff working in areas with high wildlife activity and unique habitats receive specialized training in various fields, including field craft (recognizing wildlife signs and responding to wildlife encounters), weapons training, legal procedures for wildlife offenses, and technical skills such as rock climbing and mountaineering (State Party of India, 2013).
Academic training institutions have also provided key trainings to the staff. For example, in 2015, 20 forest guards were trained at the WII on advanced census techniques, while four guards were trained in bird ringing and related record-keeping. Additionally, a workshop in 2017 focused on the prosecution of wildlife offenses, and the Forest Survey of India trained staff in GIS methodologies. In 2021, capacity-building sessions were conducted by UNESCO C2C-WII, where staff received training on ecological surveys, habitat assessment, and wildlife monitoring to enhance their ability to monitor the OUV of the GHNPCA (State Party of India, 2023).
To ensure effective communication and safety, the frontline forest staff working in remote areas are equipped with walkie-talkies and receive mobile allowances so that staff can use their personal mobiles for wildlife management and protection purposes. Patrolling staff are also equipped with good quality equipment-sleeping bags, tents, jackets, boots, and solar potable lanterns. (Mohan, et al., 2020; State Party of India, 2020).
Education and interpretation programmes
The GHNPCA management has implemented initiatives to promote awareness among the local community about the biodiversity values of the park the importance of its conservation:
Educational and Information centers in the ecozone:
The Sai Ropa Community Training and Tourist Centre, located near the park serves as a key facility for education and outreach. It includes a Forest Rest House, a photo exhibition, a conference/training room with projection facilities, and a hall with photo exhibitions about the Park. Outdoors, the center features a 520-meter "Biodiversity Trail" with trees and medicinal plant species transplanted from the park, a pergola offering views of the Tirthan River, a vermicomposting demonstration site, a butterfly enclosure, and a solar energy demonstration site. The Larji Information Centre, situated at the confluence of the Sainj and Tirthan rivers, serves a similar role, providing a hall with training and projection facilities for tourists, school children, and local community members.
Street Theatres:
The ecozone has a village-level Street Theatre group as a part of the BTCA NGO. The group is made up of eight boys and four girls from the identified Women Saving and Credit Group families. The group delivers village-level performances delivering messages about nature and biodiversity conservation in the form of dance and drama in local languages.
Women Folk Festivals (Mahila Mela):
This cultural festival largely involves female members (starting from school going children to elderly women) belonging to villages of Tirthan, Sainj and Jiwa Nal valleys. They gather at Sai Ropa Centre on 2nd October every year and showcase their folk dances, skills, dramas, etc. on the wildlife conservation themes. The GHNPCA management promotes this activity to ensure adequate participation of women in conservation of the park and create awareness about the world heritage site.
Exposure visits:
The GHNPCA also organizes exposure visits, such as nature walks and birdwatching trips, to engage local school children and youth from surrounding villages in learning about the park’s biodiversity and conservation efforts.
Natural Heritage Fest:
A festival celebrating the region’s literature, arts, and culture was organized by UNESCO C2C-WII in partnership with the GHNPCA management. This festival aimed to reinforce the appreciation of environmental heritage and foster a deeper connection with nature. A key focus of the event was to highlight the role of indigenous people in preserving their traditional knowledge and in conserving their natural heritage.
The primary motivation behind the aforementioned initiatives is to keep local community engaged in GHNPCA’ conservation so as to remove their negative opinion regarding creation of the national park. Another objective behind these programs is to promote their interest in the alternative livelihood generating activities to reduce their dependence on protected area resources. To what extent these programs informs/reinforce the legal regulations regarding resource use is not clear.
Educational and Information centers in the ecozone:
The Sai Ropa Community Training and Tourist Centre, located near the park serves as a key facility for education and outreach. It includes a Forest Rest House, a photo exhibition, a conference/training room with projection facilities, and a hall with photo exhibitions about the Park. Outdoors, the center features a 520-meter "Biodiversity Trail" with trees and medicinal plant species transplanted from the park, a pergola offering views of the Tirthan River, a vermicomposting demonstration site, a butterfly enclosure, and a solar energy demonstration site. The Larji Information Centre, situated at the confluence of the Sainj and Tirthan rivers, serves a similar role, providing a hall with training and projection facilities for tourists, school children, and local community members.
Street Theatres:
The ecozone has a village-level Street Theatre group as a part of the BTCA NGO. The group is made up of eight boys and four girls from the identified Women Saving and Credit Group families. The group delivers village-level performances delivering messages about nature and biodiversity conservation in the form of dance and drama in local languages.
Women Folk Festivals (Mahila Mela):
This cultural festival largely involves female members (starting from school going children to elderly women) belonging to villages of Tirthan, Sainj and Jiwa Nal valleys. They gather at Sai Ropa Centre on 2nd October every year and showcase their folk dances, skills, dramas, etc. on the wildlife conservation themes. The GHNPCA management promotes this activity to ensure adequate participation of women in conservation of the park and create awareness about the world heritage site.
Exposure visits:
The GHNPCA also organizes exposure visits, such as nature walks and birdwatching trips, to engage local school children and youth from surrounding villages in learning about the park’s biodiversity and conservation efforts.
Natural Heritage Fest:
A festival celebrating the region’s literature, arts, and culture was organized by UNESCO C2C-WII in partnership with the GHNPCA management. This festival aimed to reinforce the appreciation of environmental heritage and foster a deeper connection with nature. A key focus of the event was to highlight the role of indigenous people in preserving their traditional knowledge and in conserving their natural heritage.
The primary motivation behind the aforementioned initiatives is to keep local community engaged in GHNPCA’ conservation so as to remove their negative opinion regarding creation of the national park. Another objective behind these programs is to promote their interest in the alternative livelihood generating activities to reduce their dependence on protected area resources. To what extent these programs informs/reinforce the legal regulations regarding resource use is not clear.
Tourism and visitation management
Due to its challenging treks and remote location, visitation to the GHNP is limited to around 1,000 tourists annually, and visitors are required to obtain permits for park entry and trekking routes (State Party of India, 2013).
Tourism is instead promoted in the buffer zone, which offers easier to moderate treks that pass through villages. Annually, around 6,000 to 8,000 people visit the ecozone area. As part of the ecotourism strategy, the GHNPCA focuses on conservation education for visitors. Several informative materials, including picture books, brochures, posters, and postcards, have been published, featuring details about the park's birds, mammals, plants, ecosystems, and trekking routes. The Sai Ropa Community Training and Tourist Centre in Tirthan Valley offers a variety of facilities, including a Forest Rest House, photo exhibitions, butterfly enclosures, and a 520-meter-long Biodiversity Trail with medicinal plant species transplanted from the park. Similarly, the Larji Information Centre, located outside the park, provides projection facilities to help visitors appreciate and understand GHNP’s endangered species and ecosystems. The BTCA NGO also contributes to education through a Street Theatre group that performs local dances and dramas in Hindi and the local language, delivering messages about biodiversity and nature conservation (State Party of India, 2013).
Local villagers and other stakeholders play a crucial role in promoting ecotourism in the GHNPCA. The BTCA NGO provides local men with opportunities for employment as porters, cooks, and trek guides, while the GHNPCA administration prioritizes the NGO to generate income from ecotourism. Additionally, the authorities engage with local tour operators to manage visitor numbers, ensuring that they stay within the carrying capacity, and promote better waste management practices (State Party of India, 2018).
One of the key objectives of the park’s ecotourism strategy is to control tourism within the strictly protected areas of the GHNPCA. To mitigate the impact of trekking on the park’s biodiversity, the management has implemented measures such as closing visitor access to certain species’ breeding sites in response to population declines. For example, trekking routes in Tirthan Valley were closed to protect the declining Western Tragopan numbers (IUCN, 2013). Furthermore, park trails affected by floods and landslides are either closed or rerouted to allow for necessary maintenance (State Party of India, 2013).
Despite these measures, promoting sustainable tourism in the long term faces challenges. While there are no roads within the national park, the development of link roads within the ecozone may make it easier for more visitors to access the park. Visitor numbers have steadily increased and the latest MEE for GHNPCA points towards increasing pressure on the existing ecotourism zone in the core zone of the GHNP, and the need to explore more areas in the buffer zone to promote trekking and ecotourism activities (Mohan, et al., 2020).
Another key challenge is the lack of a comprehensive tourism carrying capacity assessment for the trekking routes. Such assessments are essential to identify trails and camping areas that can sustain increased visitor numbers, and those that may be too delicate to withstand additional foot traffic (Stevens, 2019). Although the Management Plan mentions the need to conduct these assessments, no details have been provided. Moreover, following the recognition of GHNPCA as a World Heritage Site, commercial tourism infrastructure has increased in the ecozone, especially in the Tirthan Valley area. The development of hotels, restaurants, and homestays has encroached on agricultural land and areas near the Tirthan River floodplain. This expansion has led to negative environmental impacts, including a decrease in forest cover around villages, encroachment on forest land and floodplains, reduced pastureland, and increased fire incidents (Irfan, et al., 2023). There is a pressing need to assess the impact of growing commercial tourism infrastructure on the forest ecosystems in the ecozone and implement measures to regulate it effectively.
Tourism is instead promoted in the buffer zone, which offers easier to moderate treks that pass through villages. Annually, around 6,000 to 8,000 people visit the ecozone area. As part of the ecotourism strategy, the GHNPCA focuses on conservation education for visitors. Several informative materials, including picture books, brochures, posters, and postcards, have been published, featuring details about the park's birds, mammals, plants, ecosystems, and trekking routes. The Sai Ropa Community Training and Tourist Centre in Tirthan Valley offers a variety of facilities, including a Forest Rest House, photo exhibitions, butterfly enclosures, and a 520-meter-long Biodiversity Trail with medicinal plant species transplanted from the park. Similarly, the Larji Information Centre, located outside the park, provides projection facilities to help visitors appreciate and understand GHNP’s endangered species and ecosystems. The BTCA NGO also contributes to education through a Street Theatre group that performs local dances and dramas in Hindi and the local language, delivering messages about biodiversity and nature conservation (State Party of India, 2013).
Local villagers and other stakeholders play a crucial role in promoting ecotourism in the GHNPCA. The BTCA NGO provides local men with opportunities for employment as porters, cooks, and trek guides, while the GHNPCA administration prioritizes the NGO to generate income from ecotourism. Additionally, the authorities engage with local tour operators to manage visitor numbers, ensuring that they stay within the carrying capacity, and promote better waste management practices (State Party of India, 2018).
One of the key objectives of the park’s ecotourism strategy is to control tourism within the strictly protected areas of the GHNPCA. To mitigate the impact of trekking on the park’s biodiversity, the management has implemented measures such as closing visitor access to certain species’ breeding sites in response to population declines. For example, trekking routes in Tirthan Valley were closed to protect the declining Western Tragopan numbers (IUCN, 2013). Furthermore, park trails affected by floods and landslides are either closed or rerouted to allow for necessary maintenance (State Party of India, 2013).
Despite these measures, promoting sustainable tourism in the long term faces challenges. While there are no roads within the national park, the development of link roads within the ecozone may make it easier for more visitors to access the park. Visitor numbers have steadily increased and the latest MEE for GHNPCA points towards increasing pressure on the existing ecotourism zone in the core zone of the GHNP, and the need to explore more areas in the buffer zone to promote trekking and ecotourism activities (Mohan, et al., 2020).
Another key challenge is the lack of a comprehensive tourism carrying capacity assessment for the trekking routes. Such assessments are essential to identify trails and camping areas that can sustain increased visitor numbers, and those that may be too delicate to withstand additional foot traffic (Stevens, 2019). Although the Management Plan mentions the need to conduct these assessments, no details have been provided. Moreover, following the recognition of GHNPCA as a World Heritage Site, commercial tourism infrastructure has increased in the ecozone, especially in the Tirthan Valley area. The development of hotels, restaurants, and homestays has encroached on agricultural land and areas near the Tirthan River floodplain. This expansion has led to negative environmental impacts, including a decrease in forest cover around villages, encroachment on forest land and floodplains, reduced pastureland, and increased fire incidents (Irfan, et al., 2023). There is a pressing need to assess the impact of growing commercial tourism infrastructure on the forest ecosystems in the ecozone and implement measures to regulate it effectively.
Sustainable use
The declaration of GHNP as a national park in 1999 resulted in the cessation of traditional community resource rights within the park boundaries. Management plans enforce these protective measures as per the Wildlife (Protection) Act, 1972. However, the creation of the national park has shifted the burden of resource use to the Sainj and Tirthan Wildlife Sanctuaries, where the rights of the local communities were not extinguished during their notification. Approximately 120 villagers reside within the Sainj Sanctuary, utilizing the area for livestock grazing and medicinal herb collection. Tirthan Sanctuary, while has no settlements, is subject to seasonal grazing by neighboring village communities (State Party of India, 2010).
Biotic pressure from livestock grazing and NTFP collection is a key management challenge for the GHNPCA. A recent study by the WII highlights significant livestock grazing pressure in Tirthan and Sainj Sanctuaries resulting in adverse ecological effects such as soil compaction, erosion, reduced species richness, and restricted wildlife habitat use (WII, 2024). Restrictions on park access have also intensified grazing pressure on village pastures in the ecozone, creating conflicts among locals and stressing high-altitude grazing grounds (Irfan, et al., 2023). Mitigating these impacts requires implementing measures like rotational grazing, restoring degraded pastures, and promoting alternative livelihoods to reduce reliance on grazing (WII, 2024).
Wild collection of medicinal trees and herbs in and around GHNPCA for their barks, roots, tubers, seeds, fruits, flowers, and leaves have led to a significant decline in the occurrence of various species. Highly important medicinal species, including Fritillaria cirrhosa, Trillium govanianum Wall, Nardostachys jatamansi, Arnebia benthamii, Dactylorhiza hatagirea, and Dioscorea deltoidea have vanished from the area (Kumar, et al., 2021). To regulate harvest of medicinal herbs, the Management Plan suggests reviving traditional practices such as herb collection only after seed maturation (Bees Bhadon). Additional strategies include regular training for sustainable harvesting techniques; developing Medicinal Plant Development Areas (MPDA) in ecozone; creating marketing channels or small-scale industries focused on cultivated medicinal plants; and setting up in-situ Medicinal Plant Conservation Areas (MPCA) within park to preserve viable populations (State Party of India, 2010).
Although hunting is banned under Wildlife (Protection) Act, 1972, opportunistic poaching and retaliatory killings of wild animals occurs in remote villages of Sainj sanctuary and surrounding areas. Strengthening patrolling, conducting anti-poaching operations, and enforcing statutory wildlife protections are essential to curb these activities. Additionally, raising public awareness through community training on man-animal conflict and provisions of wildlife compensation can foster support for conservation and reduce retaliatory killings (State Party of India, 2013).
Tourism in the GHNPCA’s core area is limited to approximately 1,000 trekkers annually, but the numbers have grown steadily. Escalating tourism pressures on the ecotourism zone in the core area highlight the need for a comprehensive assessment of trekking capacity to identify sustainable routes and protect sensitive terrains (Stevens, 2019). In contrast, the ecozone sees higher visitation, attracting 6,000–8,000 tourists annually. Since the site's World Heritage designation in 2014, a surge in hotels, restaurants, and homestays has adversely impacted the ecozone's land use, leading to loss of forest cover (Irfan, et al., 2023). It is important to study the ecological effects of this infrastructure growth and implement regulations to minimize its impact on forest ecosystems and biodiversity.
Biotic pressure from livestock grazing and NTFP collection is a key management challenge for the GHNPCA. A recent study by the WII highlights significant livestock grazing pressure in Tirthan and Sainj Sanctuaries resulting in adverse ecological effects such as soil compaction, erosion, reduced species richness, and restricted wildlife habitat use (WII, 2024). Restrictions on park access have also intensified grazing pressure on village pastures in the ecozone, creating conflicts among locals and stressing high-altitude grazing grounds (Irfan, et al., 2023). Mitigating these impacts requires implementing measures like rotational grazing, restoring degraded pastures, and promoting alternative livelihoods to reduce reliance on grazing (WII, 2024).
Wild collection of medicinal trees and herbs in and around GHNPCA for their barks, roots, tubers, seeds, fruits, flowers, and leaves have led to a significant decline in the occurrence of various species. Highly important medicinal species, including Fritillaria cirrhosa, Trillium govanianum Wall, Nardostachys jatamansi, Arnebia benthamii, Dactylorhiza hatagirea, and Dioscorea deltoidea have vanished from the area (Kumar, et al., 2021). To regulate harvest of medicinal herbs, the Management Plan suggests reviving traditional practices such as herb collection only after seed maturation (Bees Bhadon). Additional strategies include regular training for sustainable harvesting techniques; developing Medicinal Plant Development Areas (MPDA) in ecozone; creating marketing channels or small-scale industries focused on cultivated medicinal plants; and setting up in-situ Medicinal Plant Conservation Areas (MPCA) within park to preserve viable populations (State Party of India, 2010).
Although hunting is banned under Wildlife (Protection) Act, 1972, opportunistic poaching and retaliatory killings of wild animals occurs in remote villages of Sainj sanctuary and surrounding areas. Strengthening patrolling, conducting anti-poaching operations, and enforcing statutory wildlife protections are essential to curb these activities. Additionally, raising public awareness through community training on man-animal conflict and provisions of wildlife compensation can foster support for conservation and reduce retaliatory killings (State Party of India, 2013).
Tourism in the GHNPCA’s core area is limited to approximately 1,000 trekkers annually, but the numbers have grown steadily. Escalating tourism pressures on the ecotourism zone in the core area highlight the need for a comprehensive assessment of trekking capacity to identify sustainable routes and protect sensitive terrains (Stevens, 2019). In contrast, the ecozone sees higher visitation, attracting 6,000–8,000 tourists annually. Since the site's World Heritage designation in 2014, a surge in hotels, restaurants, and homestays has adversely impacted the ecozone's land use, leading to loss of forest cover (Irfan, et al., 2023). It is important to study the ecological effects of this infrastructure growth and implement regulations to minimize its impact on forest ecosystems and biodiversity.
Monitoring
The LTEM Strategy, developed by the WII in 1999-2000 forms a very important aspect of biodiversity conservation at the GHNP. Covering 35 sites across the Tirthan, Sainj, and Jiwa sub-watersheds, the LTEM monitors 57 species of flora and fauna, tracking population fluctuations and species statuses to evaluate conservation effectiveness. Results indicate that restrictions on NTFP collection, livestock grazing, and other biotic pressures following the final notification of the park have significantly improved the area's general ecology. GHNPCA staff also monitors wildlife tourism, pilgrimages, and research visits while conducting socio-economic monitoring in ecozone villages to gauge the impacts of eco-development schemes on local demographics and resource dependency (State Party of India, 2010 & 2013).
In March 2020, the Himachal Pradesh Forest Department partnered with UNESCO C2C-WII to implement a project ‘Long-term Monitoring of Outstanding Universal Values of GHNPCA’. The project developed systematic population monitoring protocols for 13 key species, including Western Tragopan, Himalayan Monal, Snow Leopard, and Himalayan Musk Deer. The protocols provided detailed descriptions, habitat preferences, distribution maps, and survey methodologies for these species. Between 2021 and 2023, frontline forest staff received training in ecological survey techniques, habitat assessments, and monitoring protocols. Consultations with forest staff indicated stable or improving populations of Snow Leopard, Himalayan Musk Deer, Goral, and Himalayan Black Bear with a minor increase in Common Leopard conflict in the Ecozone area. Status of threatened avifauna viz., Western Tragopan, Cheer Pheasant, and Himalayan Monal was also reported as stable due to their intact habitat and low disturbance in the protected area zone of GHNPCA. However, a lack of data on the population of Snow Partridge was noted, with recommendations for focused studies on its status and habitat to assess the impacts of climate change in upper Himalayan ecosystems. On the floral front, populations of Rhododendron campanulatum, Rhododendron arboreum, and oak species were reported as stable, with notable increases in oak cover in eco-sensitive zones due to plantation programs. The invasion of Parthenium hysterophorus in ecozone areas, however, emerged as a significant concern. Knowledge from frontline staff was crucial for mapping species distributions, although gaps persist in understanding species occurrences in the eastern part of the region. There was a high degree of consensus that OUVs of key faunal species (in terms of population, habitat and protection) area essentially intact and their overall condition is stable or improving (WII, 2023) (Nath, et al., 2022).
Efforts were made to engage local communities in conservation. In 2023, capacity-building programs educated community members about the global significance of GHNPCA's World Heritage status, emphasizing its potential benefits for livelihoods and the regional economy (WII, 2023).
The recent protocols developed by the UNESCO C2C-WII for monitoring the OUV of the GHNPCA staff should become a part of its official management plan. The current LTEM strategy may be updated or fine-tuned accordingly.
In March 2020, the Himachal Pradesh Forest Department partnered with UNESCO C2C-WII to implement a project ‘Long-term Monitoring of Outstanding Universal Values of GHNPCA’. The project developed systematic population monitoring protocols for 13 key species, including Western Tragopan, Himalayan Monal, Snow Leopard, and Himalayan Musk Deer. The protocols provided detailed descriptions, habitat preferences, distribution maps, and survey methodologies for these species. Between 2021 and 2023, frontline forest staff received training in ecological survey techniques, habitat assessments, and monitoring protocols. Consultations with forest staff indicated stable or improving populations of Snow Leopard, Himalayan Musk Deer, Goral, and Himalayan Black Bear with a minor increase in Common Leopard conflict in the Ecozone area. Status of threatened avifauna viz., Western Tragopan, Cheer Pheasant, and Himalayan Monal was also reported as stable due to their intact habitat and low disturbance in the protected area zone of GHNPCA. However, a lack of data on the population of Snow Partridge was noted, with recommendations for focused studies on its status and habitat to assess the impacts of climate change in upper Himalayan ecosystems. On the floral front, populations of Rhododendron campanulatum, Rhododendron arboreum, and oak species were reported as stable, with notable increases in oak cover in eco-sensitive zones due to plantation programs. The invasion of Parthenium hysterophorus in ecozone areas, however, emerged as a significant concern. Knowledge from frontline staff was crucial for mapping species distributions, although gaps persist in understanding species occurrences in the eastern part of the region. There was a high degree of consensus that OUVs of key faunal species (in terms of population, habitat and protection) area essentially intact and their overall condition is stable or improving (WII, 2023) (Nath, et al., 2022).
Efforts were made to engage local communities in conservation. In 2023, capacity-building programs educated community members about the global significance of GHNPCA's World Heritage status, emphasizing its potential benefits for livelihoods and the regional economy (WII, 2023).
The recent protocols developed by the UNESCO C2C-WII for monitoring the OUV of the GHNPCA staff should become a part of its official management plan. The current LTEM strategy may be updated or fine-tuned accordingly.
Research
UNESCO’s C2C-WII has submitted two important research reports to the GHNPCA management. The first report, submitted in 2023, provided detailed guidelines and protocols for conducting long-term monitoring of the park's OUV (WII, 2023). The second, submitted in October 2024, examined livestock grazing practices in the Sainj and Tirthan sanctuaries. It highlighted the ecological threats posed to pastures and proposed recommendations for more sustainable grazing practices (WII, 2024).
The management plan has identified further areas for research that could significantly enhance conservation decision-making. These include assessing impact of climate change/global warming on snow areas, glaciers; evaluating ecosystem services provided by park’s biodiversity; investigating links between natural and domesticated ecosystems and taxa; documenting community traditions, knowledge with reference to biodiversity at GHNPCA; monitoring changes in populations of vulture, birds of prey and pheasants (State Party of India, 2010).
The management plan has identified further areas for research that could significantly enhance conservation decision-making. These include assessing impact of climate change/global warming on snow areas, glaciers; evaluating ecosystem services provided by park’s biodiversity; investigating links between natural and domesticated ecosystems and taxa; documenting community traditions, knowledge with reference to biodiversity at GHNPCA; monitoring changes in populations of vulture, birds of prey and pheasants (State Party of India, 2010).
Effectiveness of management system and governance in addressing threats outside the site
The management system of GHNPCA faces some challenges in addressing threats outside its boundaries which may affect its ecological integrity. A significant potential threat is the construction of hydropower projects in the Parvati valley and Sainj valley, which will disturb the dense canopies of primary upper temperate forest habitats characterized by coniferous, mixed broad-leaf coniferous, and broad-leaf trees and associated understory vegetation. These habitats are critical for many endangered species, such as Himalayan Musk Deer, Serow, Goral, Black Bear, Common Leopard, and avain species such as Western Tragopan, Cheer Pheasant, Koklass and Monal Pheasant (CISMHE, 2000; Uniyal, 2009). Although the GHNPCA management plan acknowledges the risks posed by dam building near the park, it lacks a site-specific assessment to inform targeted mitigation measures to safeguard the primary Upper Temperate Western Himalayan Forests.
Another pressing issue is the expansion of commercial tourism infrastructure since GHNPCA's recognition as a World Heritage Site in 2014. This growth has resulted in development of hotels, restaurants, and homestays, often encroaching on agricultural land and river floodplains. This unchecked expansion has led to reduction in forest cover around villages, and decline in pasturelands. The management must assess the impacts of tourism growth on the forest ecosystems of the ecozone, analyse carrying capacity and design strategies regulate such developments (Irfan, et al., 2023). However, the current management plan neither acknowledges the impacts of these developments not offers measures to address them.
Additionally, biotic pressures such as grazing and the collection of medicinal herbs continue to affect ecosystems near GHNPCA. The high-altitude thaches and ghasnies (grasslands) within the Ecozone serve as crucial fodder sources during winter. Restrictions on accessing the park’s Core Zone have increased pressure on these areas. Locals often resort to practices like annual grassland burning, which they believe enhances yield. However, these fires frequently lead to forest fires, causing extensive damage to forest patches and altering land use and cover. The heavily grazed grasslands at higher elevations are critical for livestock populations but are now among the most intensively used land types, often triggering conflicts among locals over access and use (Irfan, et al., 2023).
While alternative livelihoods have been developed to reduce grazing pressures, these efforts require significant strengthening, as dependency on pastures persists. Similarly, the decline in medicinal plant species poses a concern. Although the management plan proposes measures like developing medicinal plant propagation areas and reviving traditional sustainable harvesting practices, such as Beed Bhadon, the effectiveness of these initiatives remains unstudied and unrealized.
To effectively address these threats, the GHNPCA management system must prioritize more robust, site-specific assessments, regulate developmental activities, and strengthen livelihood alternatives. Such measures are vital for reducing dependence on natural resources, protecting critical habitats, and ensuring the long-term ecological and social sustainability of the region.
Another pressing issue is the expansion of commercial tourism infrastructure since GHNPCA's recognition as a World Heritage Site in 2014. This growth has resulted in development of hotels, restaurants, and homestays, often encroaching on agricultural land and river floodplains. This unchecked expansion has led to reduction in forest cover around villages, and decline in pasturelands. The management must assess the impacts of tourism growth on the forest ecosystems of the ecozone, analyse carrying capacity and design strategies regulate such developments (Irfan, et al., 2023). However, the current management plan neither acknowledges the impacts of these developments not offers measures to address them.
Additionally, biotic pressures such as grazing and the collection of medicinal herbs continue to affect ecosystems near GHNPCA. The high-altitude thaches and ghasnies (grasslands) within the Ecozone serve as crucial fodder sources during winter. Restrictions on accessing the park’s Core Zone have increased pressure on these areas. Locals often resort to practices like annual grassland burning, which they believe enhances yield. However, these fires frequently lead to forest fires, causing extensive damage to forest patches and altering land use and cover. The heavily grazed grasslands at higher elevations are critical for livestock populations but are now among the most intensively used land types, often triggering conflicts among locals over access and use (Irfan, et al., 2023).
While alternative livelihoods have been developed to reduce grazing pressures, these efforts require significant strengthening, as dependency on pastures persists. Similarly, the decline in medicinal plant species poses a concern. Although the management plan proposes measures like developing medicinal plant propagation areas and reviving traditional sustainable harvesting practices, such as Beed Bhadon, the effectiveness of these initiatives remains unstudied and unrealized.
To effectively address these threats, the GHNPCA management system must prioritize more robust, site-specific assessments, regulate developmental activities, and strengthen livelihood alternatives. Such measures are vital for reducing dependence on natural resources, protecting critical habitats, and ensuring the long-term ecological and social sustainability of the region.
Effectiveness of management system and governance in addressing threats inside the site
A major threat currently affecting GHNPCA is biotic pressure, particularly from livestock grazing and the collection of medicinal herbs. With the closure of the national park boundaries, pressure on natural resources in the surrounding sanctuaries has increased significantly. Unlike GHNP, where all traditional rights of neighbouring communities were ceased, the sanctuaries still allow these communities to exercise their traditional rights. Currently, 120 villagers from three settlements reside within the Sainj Sanctuary and depend on its resources. In contrast, Tirthan Sanctuary has no human settlements but is subject to traditional seasonal grazing from nearby villages. A proposal to upgrade the sanctuaries to national park status was considered but ultimately not recommended by SBWL. The reasoning was based on to avoid relocating villagers and support ongoing efforts by the park administration to engage communities in the Sainj Sanctuary and encourage phasing out grazing from Tirthan Sanctuary (State Party of India, 2018). A research study by the WII highlighted the high grazing pressure on the meadows of both sanctuaries. The study identified significant ecological impacts, including soil compaction, erosion, and altered species diversity. Grazed areas exhibited lower species richness compared to ungrazed zones. Key recommendations from the study emphasized promoting alternative livelihoods and restoring pasture quality (WII, 2024). The GHNPCA management has made efforts to foster alternative livelihoods through WSCGs and the local NGO BTCA. However, these initiatives require further strengthening to effectively reduce dependency on pasture grazing. The management plan also includes habitat development programs, such as the revival and improvement of pastures. However, the effectiveness of these measures remains to be studied and realized, necessitating a more focused and evidence-based approach to address the challenges of biotic pressure.
Additionally, the high commercial value of various medicinal plants within GHNPCA has led to overexploitation of their roots, tubers, seeds, fruits, flowers, and leaves, causing significant declines in many species (Kumar, et al., 2021). The management plan outlines actions such as the development of medicinal plant propagation areas and the establishment of in-situ conservation reserves for threatened herbs (State Party of India, 2010). However, given the ongoing overexploitation, these efforts need to be significantly strengthened, and their effectiveness rigorously evaluated.
Furthermore, as highlighted in the latest MEE, mounting tourism pressure on the ecotourism zone within the park's core area presents another challenge (Mohan, et al., 2020). To mitigate these pressures, the management plan calls for assessing the tourism carrying capacity of trekking routes (State Party of India, 2010). More detailed assessments are needed, including identification of trails and camping areas that can sustainably handle visitor pressure and those requiring stricter protection due to ecological sensitivity.
In conclusion, while GHNPCA’s management has made efforts to address internal threats, these initiatives need to be strengthened, and their effectiveness must be systematically studied and assessed to ensure the park’s long-term ecological and social sustainability.
Additionally, the high commercial value of various medicinal plants within GHNPCA has led to overexploitation of their roots, tubers, seeds, fruits, flowers, and leaves, causing significant declines in many species (Kumar, et al., 2021). The management plan outlines actions such as the development of medicinal plant propagation areas and the establishment of in-situ conservation reserves for threatened herbs (State Party of India, 2010). However, given the ongoing overexploitation, these efforts need to be significantly strengthened, and their effectiveness rigorously evaluated.
Furthermore, as highlighted in the latest MEE, mounting tourism pressure on the ecotourism zone within the park's core area presents another challenge (Mohan, et al., 2020). To mitigate these pressures, the management plan calls for assessing the tourism carrying capacity of trekking routes (State Party of India, 2010). More detailed assessments are needed, including identification of trails and camping areas that can sustainably handle visitor pressure and those requiring stricter protection due to ecological sensitivity.
In conclusion, while GHNPCA’s management has made efforts to address internal threats, these initiatives need to be strengthened, and their effectiveness must be systematically studied and assessed to ensure the park’s long-term ecological and social sustainability.
According to the most recent Management Effectiveness Evaluation (MEE) for 2018–2019, the GHNPCA faces biotic pressures, including livestock grazing and medicinal herb collection. Addressing these challenges requires active engagement with local communities and the promotion of alternative livelihoods. The adoption of participatory management frameworks, such as community-led anti-poaching units and eco-development committees, have strengthened local engagement but lack formal linkages to state-level climate resilience strategies. Transboundary connectivity initiatives, like the proposed Himalayan Bear Corridor linking GHNPCA to neighbouring protected areas, remain hindered by fragmented land-use policies and competing infrastructure agendas. Persistent challenges include inadequate funding for cross-jurisdictional coordination, limited integration of traditional ecological knowledge into formal planning, and climate-driven habitat shifts outpacing adaptive policies. The management plan outlines a landscape conservation framework, yet progress on integrating adjacent protected areas into the GHNPCA has been slow. While approval has been granted for the integration of Khirganga National Park, no significant advancements have been reported regarding the merger of Pin Valley National Park, Rupi Bhabha Wildlife Sanctuary, and Kanawar Sanctuary. The MEE notes increasing pressure on the ecotourism zone within the core area of the national park necessitating identification of additional trekking routes and area for ecotourism activities in GHNP’s buffer area. Conducting carrying capacity assessments is essential to determine areas of capable sustaining visitor pressure and those fragile to withstand increased traffic. Floral and faunal populations are monitored under a LTEM strategy developed in collaboration with the WII. While the MEE acknowledges these efforts, it calls for strengthening census exercises to support science-based interventions for long-term conservation and survival of species and their habitats. Protocols for monitoring OUVs of GHNPCA, developed by the UNESCO C2C-WIIl, should be integrated or used to refine the existing LTEM strategies to ensure effective, long-term biodiversity conservation.
Globally significant habitat
Low Concern
Trend
Stable
The GHNPCA is crucial site for the conservation of Western Himalayan biodiversity. It encompasses 25 distinct forest types, including the unmodified low altitude West Himalayan broad-leaved and coniferous forests with intact understory vegetation. These forests are not only integral to the GHNPCA itself but also play a vital role in sustaining the surrounding ecosystems. At present, these forest ecosystems face no immediate, significant threats. However, the construction of hydropower projects near the GHNP pose substantial risks. The development of dams in the Parvati valley could lead to irreversible loss of upper temperate forests. These habitats are critical for many endangered species, including Himalayan Musk Deer, Serow, Goral, Black Bear, Common Leopard, and avain species such as Western Tragopan, Cheer Pheasant, Koklass and Monal Pheasant (Uniyal, 2009).
The Parvati Valley is home to extensive primary forests, characterized by dense canopies of coniferous, broad-leaf coniferous and broad-leaf type. The loss of these primary forests, especially those adjacent to the GHNP, would significantly impact the biodiversity of the region, including the habitat and movement corridors of key faunal species, as well as avifaunal populations. It is important to note these forest types elsewhere in Western Himalayan region are being lost due to dam construction and increasing human disturbance (CISMHE, 2000).
While the management plan for the GHNPCA acknowledges the potential threats from dam building near the park, it lacks a site-specific assessment to inform targeted mitigation measures aimed at protecting the primary Upper Temperate Western Himalayan Forests.
The Parvati Valley is home to extensive primary forests, characterized by dense canopies of coniferous, broad-leaf coniferous and broad-leaf type. The loss of these primary forests, especially those adjacent to the GHNP, would significantly impact the biodiversity of the region, including the habitat and movement corridors of key faunal species, as well as avifaunal populations. It is important to note these forest types elsewhere in Western Himalayan region are being lost due to dam construction and increasing human disturbance (CISMHE, 2000).
While the management plan for the GHNPCA acknowledges the potential threats from dam building near the park, it lacks a site-specific assessment to inform targeted mitigation measures aimed at protecting the primary Upper Temperate Western Himalayan Forests.
Rich assemblage of faunal species
Low Concern
Trend
Stable
Based on the research conducted by the WII, the GHNPCA management has implemented its LTEM program. A total of 57 taxa have been selected for monitoring across 35 sites within three sub-watersheds viz., Tirthan, Sinj and Jiwa Nal. As of 2012, LTEM result indicate that ban on NTFP collection, livestock grazing and other biotic pressure have significantly improved the national park’s ecology. Populations of rare and threatened species, including Himalayan Musk Deer have shown substantial increase (State Party of India, 2013).
Between 2020 and 2023, the UNESCO C2C-WII developed systematic protocols for monitoring OUV of the site, along with the training program for the frontline forest staff in data collection. Evaluation by forest officials revealed that sightings of species such as Snow Leopard, Himalayan Musk Deer, Himalayan Goral and Himalayan Black Bear are stable with minor increase in human-leopard conflict in the Ecozone. Consensus among officials suggests that OUV, including population trends, habitat quality and protection remain stable or overall improving. However, a more robust monitoring design and implementation are necessary to accurately assess population statuses (Nath, et al., 2022; WII, 2023).
No specific study has been conducted on lower vertebrate taxa since the site’s inscription on the World Heritage List, indicating an important research gap (Nath, et al., 2022; WII, 2023).
Between 2020 and 2023, the UNESCO C2C-WII developed systematic protocols for monitoring OUV of the site, along with the training program for the frontline forest staff in data collection. Evaluation by forest officials revealed that sightings of species such as Snow Leopard, Himalayan Musk Deer, Himalayan Goral and Himalayan Black Bear are stable with minor increase in human-leopard conflict in the Ecozone. Consensus among officials suggests that OUV, including population trends, habitat quality and protection remain stable or overall improving. However, a more robust monitoring design and implementation are necessary to accurately assess population statuses (Nath, et al., 2022; WII, 2023).
No specific study has been conducted on lower vertebrate taxa since the site’s inscription on the World Heritage List, indicating an important research gap (Nath, et al., 2022; WII, 2023).
Rich assemblage of floral species
Low Concern
Trend
Stable
The LTEM program covers 33 plant species, comprising 10 trees, 10 shrubs and 13 herbs, selected based on their economic importance, conservation significance and threats to survival (State Party of India, 2013). However, there is lack of specific data on the results of floral monitoring, such as population trends, threats faced by species in the wild and effectiveness of conservation management programs.
An assessment by forest officials, as a part of UNESCO C2C-WII’s OUV monitoring research, indicates that population of plant species such as Semru (Rhododendron campanulatum), Buransh (Rhododendron arboreum), Oak, Kharshu (Quercus semecarpifolia) and Oak, Banjh (Quercus leucotrichophora) are stable. There has been an increase in the distribution of Oak species in the Ecozone, attributed to the success of plantation programs. The Himalayan Yew has also shown improved distribution, supported by reduced lopping and other human disturbances, which have contributed to better forest cover (Nath, et al., 2022; WII, 2023).
Despite positive outcomes, concerns were raised about the invasion of Parthenium hysterophorus in the Ecozone which poses a threat to the native flora (Nath, et al., 2022; WII, 2023).
An assessment by forest officials, as a part of UNESCO C2C-WII’s OUV monitoring research, indicates that population of plant species such as Semru (Rhododendron campanulatum), Buransh (Rhododendron arboreum), Oak, Kharshu (Quercus semecarpifolia) and Oak, Banjh (Quercus leucotrichophora) are stable. There has been an increase in the distribution of Oak species in the Ecozone, attributed to the success of plantation programs. The Himalayan Yew has also shown improved distribution, supported by reduced lopping and other human disturbances, which have contributed to better forest cover (Nath, et al., 2022; WII, 2023).
Despite positive outcomes, concerns were raised about the invasion of Parthenium hysterophorus in the Ecozone which poses a threat to the native flora (Nath, et al., 2022; WII, 2023).
Assessment of the current state and trend of World Heritage values
Stable
The development of dams could lead to the irreversible loss of dense upper temperate forest habitats, which are critical for many endangered species, including the Himalayan Musk Deer, Serow, Goral, Black Bear, Common Leopard, and avian species such as the Western Tragopan, Cheer Pheasant, Koklass, and Monal Pheasant. The GHNPCA management plan acknowledges these threats but lacks a site-specific assessment for designing targeted mitigation measures to protect the primary Upper Temperate Western Himalayan Forests. Although recent specific data on population trends are lacking, assessments by forest officials as of 2021 indicate that the OUV of GHNPCA, including population trends, habitat quality, and protection, have remained stable, though there is a need for a more robust monitoring design and implementation. Sightings of species like the Snow Leopard, Himalayan Musk Deer, Himalayan Goral, and Himalayan Black Bear have remained stable with a slight increase in human-leopard conflict in the Ecozone. The status of avifaunal species, including the Western Tragopan, Snow Partridge, Cheer Pheasant, and Himalayan Monal, has also remained stable due to their intact habitats and minimal disturbance in GHNPCA’s core zone. Opportunistic hunting was identified as a direct threat to the local avifauna, while the absence of specific studies on lower vertebrate taxa since the site's inscription remains a research gap. Additionally, limited information on species occurrence in the eastern part of the GHNPCA represents another area requiring further investigation. Regarding flora, populations of species such as Semru (Rhododendron campanulatum), Buransh (Rhododendron arboreum), Oak, Kharshu (Quercus semecarpifolia), and Oak, Banjh (Quercus leucotrichophora) have been evaluated as stable. The distribution of the endangered Himalayan Yew has increased, supported by reduced lopping and other human disturbances, contributing to improved forest cover. However, studies have noted declines in the occurrence of species such as Fritillaria cirrhosa and Trillium govanianum, attributed to unsustainable harvesting. Other valuable medicinal plants, including Nardostachys jatamansi, Arnebia benthamii, Dactylorhiza hatagirea, and Dioscorea deltoidea, are also becoming increasingly rare in the area. Taxus wallichiana found in the Sainj, Jiwa Nal and Tirthan Valleys is under constant threat as well for its bark and leaves are heavily lopped as they contain Taxol.
Assessment of the current state and trend of other important biodiversity values
Low Concern
Data Deficient
Bird diversity: Between 2020 and 2023, the UNESCO C2C-WII developed systematic protocols for monitoring OUVs of the site, along with the training program for the frontline forest staff in data collection. Evaluation by forest officials revealed that status of key avifauna species, including Western Tragopan, Snow Partridge, Cheer Pheasant and Himalayan Monal was assessed as stable due to intact habitats and minimal disturbance in GHNPCA’s core area. However, the Snow Partridge had not been previously assessed, given the challenges of surveying difficult terrain limited manpower within the forest department. It is now recommended that focused studies on Snow Partridge and its habitat be undertaken, as this species could serve as an important case study for climate change research in the upper Himalaya (Nath, et al., 2022; WII, 2023). Despite the positive outcomes, opportunistic hunting was reported as a direct threat to the avifaunal species, with reported instances of poaching targeting the Western Tragopan. (Nath, et al., 2022) (WII, 2023). State- Low Concern; Trend-Stable
High Medicinal Plant Biodiversity: Collection of medicinal herbs poses biotic pressures on the GHNPCA and its ecozone. Historically, village elders followed sustainable harvesting practices, such as extracting herbs only after Bees Bhadon (around October), when plants had completed their annual cycles and seeds had naturally dispersed. These practices were accompanied by sacred ceremonies to select a time and particular plant to extract it for medicinal purposes. However, with the advent of the pharmaceutical industry and the onset of commercialization, such sacred practices have gradually phased out (Pandey, 2019). The high commercial value of various medicinal species has led to the overexploitation of their roots, tubers, seeds, fruits, flowers, and leaves. Field surveys reveal significant declines in the occurrence of species such as Fritillaria cirrhosa and Trillium govanianum Wall, attributed to unsustainable harvesting by locals. Other valuable medicinal plants, including Nardostachys jatamansi, Arnebia benthamii, Dactylorhiza hatagirea, and Dioscorea deltoidea, are also vanishing from the area (Kumar et al., 2021).
Trees having medicinal uses are also under threat. For example, Taxus wallichiana found in the Sainj, Jiwa Nal and Tirthan Valleys is under constant threat for its bark and leaves are heavily lopped as they contain Taxol. Taxol is a potent anti-cancer drug and has uses in Ayurveda medicine as well. The rising price of Taxol in the world market has led to the species’ serious population decline (State Party of India, 2010). To address these challenges, the GHNPCA management has proposed in situ reserves for threatened medicinal species within the park and the establishment of medicinal plant development areas in the ecozone. Training villagers in sustainable harvesting techniques has also been recommended. Although the success of these initiatives remains unclear, recent monitoring by UNESCO C2C-WII indicates that distribution of Taxus baccata is improving since lopping and other human disturbances has decreased leading to better forest cover (WII, 2023). Enhanced monitoring efforts are needed to track population trends of medicinal species, identify ongoing threats, and implement effective conservation measures.
State- Low Concern; Trend-Deteriorating
High Medicinal Plant Biodiversity: Collection of medicinal herbs poses biotic pressures on the GHNPCA and its ecozone. Historically, village elders followed sustainable harvesting practices, such as extracting herbs only after Bees Bhadon (around October), when plants had completed their annual cycles and seeds had naturally dispersed. These practices were accompanied by sacred ceremonies to select a time and particular plant to extract it for medicinal purposes. However, with the advent of the pharmaceutical industry and the onset of commercialization, such sacred practices have gradually phased out (Pandey, 2019). The high commercial value of various medicinal species has led to the overexploitation of their roots, tubers, seeds, fruits, flowers, and leaves. Field surveys reveal significant declines in the occurrence of species such as Fritillaria cirrhosa and Trillium govanianum Wall, attributed to unsustainable harvesting by locals. Other valuable medicinal plants, including Nardostachys jatamansi, Arnebia benthamii, Dactylorhiza hatagirea, and Dioscorea deltoidea, are also vanishing from the area (Kumar et al., 2021).
Trees having medicinal uses are also under threat. For example, Taxus wallichiana found in the Sainj, Jiwa Nal and Tirthan Valleys is under constant threat for its bark and leaves are heavily lopped as they contain Taxol. Taxol is a potent anti-cancer drug and has uses in Ayurveda medicine as well. The rising price of Taxol in the world market has led to the species’ serious population decline (State Party of India, 2010). To address these challenges, the GHNPCA management has proposed in situ reserves for threatened medicinal species within the park and the establishment of medicinal plant development areas in the ecozone. Training villagers in sustainable harvesting techniques has also been recommended. Although the success of these initiatives remains unclear, recent monitoring by UNESCO C2C-WII indicates that distribution of Taxus baccata is improving since lopping and other human disturbances has decreased leading to better forest cover (WII, 2023). Enhanced monitoring efforts are needed to track population trends of medicinal species, identify ongoing threats, and implement effective conservation measures.
State- Low Concern; Trend-Deteriorating
Assessment of the current state and trend of other important values
Good
Stable
Another important value of the GHNPCA is its spiritual and cultural significance for the local communities. Specific sites, including water bodies and forest patches, are considered sacred and revered in their traditions. These sacred sites are protected through rituals, taboos, and cultural practices, many of which are located within the national park and the Ecozone. Currently, there is no data or evidence suggesting threats to these sites or any potential deterioration in their value
Additional information
Traditional agriculture
The two Wildlife Sanctuaries and buffer zone are clearly important to the livelihoods of local people who either reside within Sainj Wildlife Sanctuary or graze livestock within Tirthan Wildlife Sanctuary. Villagers in these areas grow a variety of paddy called Lad Dhan or Red Rice which has therapeutic qualities. The traditional life style includes a diet of millets (buckwheat and barley), wheat, amaranth, maize, potato, meat and local fruits in the face of fast changing world around the mountain people (Pandey and Gaston, 2019).
The resolution of rights to ensure adequate protection of the site's values will likely require careful consideration of alternative livelihoods.
Soil stabilisation,
Water provision (importance for water quantity and quality)
GHNPCA includes the upper (5,000-6,000 metre high) mountain glacial and snow melt water source origins of the westerly flowing Jiwa Nal, Sainj and Tirthan Rivers and the north-westerly flowing Parvati River, which are all headwater tributaries to the River Beas and subsequently, the Indus River. The property includes an elevational range from high alpine peaks of over 6,000 m.a.s.l. to riverine forest at altitudes below 2,000 m.a.s.l. forming a critical catchment area vital to millions of downstream users (WH Committee, 2014). GHNP is critical for soil stabilization and clear water quality in the region, primarily due to its intact forest and grassland cover and the prohibition of any developmental activity.
Biodiversity is fundamental to the ecosystem services that emanate from the GHNPCA (Pandey and Gaston, 2019). Food and water production (Provisioning ecosystem service), climate changes (Regulating), recreational and spiritual benefits (Cultural) and pollination & nutrient cycles (Supporting) flow from the native species of plants and animals on which the local communities have depended for hundreds of years. The GHNPCA is an example to show how community-based-adaptations drawing on participatory approaches to avail alternative livelihoods, can facilitate rejuvenation of environmental services (Pandey, 2008; Pandey and Gaston, 2019).
History and tradition
There are several pilgrimage routes within the property, leading to sacred sites around the source/ origin of the Tirthan & Sainj rivers. These are annually visited by local people. The local community since time immemorial is revering animals, plants and forests. Dedication of a forest area (devban or sacred forest) to a deity or an ancestral sprit is manifestation of divinity in the buffer zone of GHNPCA. The most ubiquitous tree of the area is deodar (cedar or Cedrus deodara) which literally means Tree of Gods (Pandey and Gaston, 2019).
With the coming of roads in the buffer zone, the local conservation traditions such as devbans or sacred groves are undergoing massive changes. The village temples and mohras (images of Gods in metal) are artistic or aesthetic representation of religious art and part of local culture and social ethos. One does not know how long such traditions will survive. It is difficult to say if these mountain cultures are getting threatened or they are thriving (Pandey and Gaston, 2019).
Outdoor recreation and tourism
Growing number of trekkers to the GHNP reflect the growing value of its recreational values (GHNP Records, 2017). With several Education & Interpretation centres around the property, it contributes actively to dissemination of knowledge and awareness of the natural wealth present. One can not know the rivers till one has seen them at their sources (Shepherd, 2011). So the headwaters of Parvati, JiwaNal, Sainj and Tirthan in the Park offer very special experience to an accomplished trekker.
Trekking in the GHNPCA needs to be with caution as the area is ecologically very fragile (Gaston and Garson, 1992; Pandey and Wells, 1997; Pandey and Gaston, 2019). All the treks in the Park are of strenuous type which need to be maintained as such for the adventure-loving trekkers. In the buffer zone of the Park, the treks are of Moderate type which can be used by families and children. Remoteness and inaccessibility are attributes of a protected area such as GHNPCA for the conservation of her natural beauty as well as biodiversity. Roadlessness supports it very nicely.
Importance for research,
Collection of genetic material
The GHNP harbours perhaps some of the most genetically pure populations of several birds and Himalayan ungulates. Unique eco-types of several medicinal species are most likely located here. It remains one of the most well researched Protected Area in the country. Permission to collect samples for study and research is accorded to recognised research institutions.
Research and monitoring should go together at the GHNPCA. Park's location at the transition zone of Palearctic and Oriental realms make it very rich ecological reference point for researchers and scientists. A well established research station along with facilities of Long Term Ecological Monitoring (LTEM) will contribute to the knowledge of ecological processes in the area (Pandey, 2008; Pandey and Gaston, 2019). GHNPCA can become a reference point for research on global warming and climate change. The Park is safeguarding exceptional natural beauty, significant geomorphic and physiographic features, many on-going ecological and geological processes which can contribute to the knowledge of evolution and development of terrestrial, fresh water and mountain ecosystems and communities of plants and animals (Pandey and Gaston, 2019).
The management of the Park has taken notable steps to work with the community over many years, reinforcing the links between investment in local livelihoods and successful conservation of biodiversity in the Park. Prior to its establishment, about 2,500 people collected herbs and mushrooms from the Park and about 35,000 sheep and goats grazed the Park. The transition between use and conservation in GHNP has aspired to be a socially responsible and phased process that has included compensation for traditional rights and continuing investments in the Ecozone designed to support people. Successful response strategies have included the empowerment of the poor, given that rural poor are the most dependent on forest resources for livelihood needs, with women being the poorest (IUCN, 2013). The GHNP currently provides at least 6 of the listed Benefit Types as elaborated above. It provides significant benefits associated with Food, Environmental Services, Cultural and Spiritual Values, Health and Recreational Values and for Knowledge building. All these values have tangible and intangible aspects, both of which perhaps need economic valuation for better appreciation and helping the property to figure at the top of the state’s conservation agenda. Its inscription as a World Heritage site provides a basis for the much needed inter-disciplinary research and management GHNP merits.
| № | Organization | Brief description of Active Projects | Website |
|---|---|---|---|
| 1 | WII | Not Available | |
| 2 | UNESCO C2C-WII | Not Available |
References
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