Sanctuaires du grand panda du Sichuan - Wolong, Mont Siguniang et Montagnes de Jiajin

Country
China
Inscribed in
2006
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.
© Our Place

Summary

2025 Conservation Outlook

Finalised on
11 oct 2025
Good with some concerns
The incorporation of the site into the Giant Panda National Park is likely to address a number of threats to the values of the site. Under the reform, management is brought under one organization instead of many different management organizations for separate components and will likely enhance the management effectiveness in the site. Nonetheless, as the natural park system is still under development, the effectiveness of the reform still needs to be evaluated for the Giant Panda Sanctuary. Livestock grazing, especially overgrazing in certain high-altitude regions and forests, is changing the natural ecosystem, species interaction, and habitat quality, including those for giant pandas. The site has not sufficiently addressed this issue in the past few years. Tourism development in and out of the site has been a major concern in the past. The construction of a new railway, increasing tourist flows, and outdoor activity needs pose further pressure on the site. The latest IUCN reactive monitoring mission in 2010 recommended extending the site to enhance its integrity. This has been addressed, albeit not yet through the mechanisms of the Convention, by establishing the Giant Panda National Park, which includes 80% of the natural range of giant panda habitat. As the new National Park Law will be finalized and take effect in 2025 or, at the latest, in 2026, it will help to make the true transition to the new management organization.

Current state and trend of VALUES

Low Concern
Despite some damage from landslides/mudslides caused by extreme precipitation and human developments (roads etc.), the site retains its essential World Heritage values and remains in a very natural state over the majority of its area. It continues to serve as the heart of China’s wild giant panda population and the hub of giant panda conservation, which will likely be further enhanced as part of the Giant Panda National Park.

Overall THREATS

Low Threat
As a part of the Giant Panda National Park, many threats such as mining, dams, poaching have been reduced. Areas adjacent to human developments are somewhat compromised, but are small in total area and peripheral to the core values of the site. However, tourism and small-town development may become of some concern if not managed well. Roads, railways, livestock grazing in alpine grassland and forests, as well as commercial wild plant collection, have posed some impacts on the ecosystem as well as the habitat quality and connectivity of giant pandas. The new railway planned to connect Dujiangyan to Mt Siguniang could further deteriorate the situation, but the impact is unknown so far. Climate change has caused and will cause more frequent extreme weather events, which triggers severe flooding, landslides/mudslides. They have caused the loss of vegetation, habitat and damages on infrastructure and housing of local communities. Nonetheless, there is a lack of emphasis on the natural disaster preparation or plan to improve the resilience under climate change.

Overall PROTECTION and MANAGEMENT

Some Concern
Wolong as the central protected area of the site has always enjoyed first place in concern, financial and human resource investment of all China’s protected areas. Some of the other county sites are still poorly supported and require improvements in staffing, operational budgets, basic ecological training and management capacity. Investment in protection and management of the habitats and ecosystems for which the site is inscribed is relatively low compared to the investment in captive breeding of giant pandas. The headquarter of the breeding centre has moved to Chengdu in 2024, which could cause the loss of research staff who support some of the in situ conservation. There is a lack of integration between conservation of giant pandas and local community development, causing distrust, conflicts and lack of engagement of the local stakeholders. The problem of weak coordination of management between sub-sites via the World Heritage office has been partly addressed by the site becoming a part of Giant Panda National Park. However, it is still very fragmented as the national park system is under development and existing sites are mainly managed through the old system. There is also a major gap in integrating conservation and development policies with effective disaster risk management planning and implementation.

Full assessment

Click the + and - signs to expand or collapse full accounts of information under each topic. You can also view the entire list of information by clicking Expand all on the top left.

Description of values

High proportion of global population of iconic giant panda

Criterion
(x)
The Sichuan Giant Panda Sanctuary includes more than 30% of the world’s population of giant panda and constitutes the largest and most significant remaining contiguous area of panda habitat in the world. It is the most important source of giant panda for establishing the captive breeding population of the species (World Heritage Committee, 2012).

Rich montane flora, with many endemic species

Criterion
(x)
The property is also one of the botanically richest sites of any temperate region in the world or indeed anywhere outside of the tropical rain forests (World Heritage Committee, 2012). The property contains more than 10,000 plant species making it possibly the richest temperate flora in the world with high levels of endemism; for example more than 200 species of rhododendron are located here, almost all endemic to China and many confined to this property. Other significant floral elements include magnolias, orchids, lilies, primulas, alpine flora, relict trees and endangered medicinal plants (State Party of China, 2006; UNEP-WCMC, 2012).

Rare and endemic birds

Criterion
(x)
The property constitutes best protected examples of two Endemic Bird Areas (EBAs) – Central Sichuan Mountains and West Sichuan Mountains (ICBP, 1992) and contains 5 recognised Important Bird and Biodiversity Areas (IBAs) – Wolong, Anzihe, Heishuihe, Fengtongzhai and Labahe (BirdLife International, 2009). The site lists more than 300 resident breeding bird species including many local endemics. This is a radiation centre for pheasants – 11 species (State Party of China, 2006).

Rare and threatened mammals

Criterion
(x)
The property hosts some rare species – snow leopards, wolves, and dholes. Snow leopards are probably in a viable condition (Tang et al. 2017). It also contains viable and significant population of many other rare, endemic and protected mammals including takins, red pandas and golden monkeys (State Party of China, 2006; UNEP/WCMC, 2012; Smith & Xie, 2008).

Diversity of habitats

Criterion
(x)
The property’s biological richness, ecological resilience and scenic values are due to its large size, wide altitudinal range, steep profiles and great diversity of habitats. There is a continuum from the permanent glaciers of Siguniang eastwards through coniferous and temperate broadleaf forests to evergreen subtropical forests and westwards through alpine grasslands to less humid scrub oak, larch and birch woodlands. Mountain streams form breeding catchments of several different rivers (State Party of China, 2006).

Diverse endemic richness of other groups

Criterion
(x)
Overall richness and/or high levels of endemism are repeated in many other taxa including fungi, insects (Bhutanitis, Apollo, etc.), amphibians (salamanders) and fish (rare Yangtze catfish endemics) (State Party of China, 2006).
Additional cultural interests of Qiang and Tibetan minorities and Han temples, Taoism and historical sites including unique Qing Dynasty Catholic Mission
The northeastern gateway to the property is the municipal city of Dujiangyan, famous for its outstanding Taoist temples and famous irrigation works. These have separately, already been recognized as an outstanding cultural area and graced with the title of World Heritage Cultural Site.
Other examples of Han culture can be found in Baoxing and other early settlements in and around the property. The Catholic mission station and church of Dengchigou in Baoxing county remains intact with its unique French/Qing style.
Qiang and Tibetan minorities preserve their own cultural values with distinctive house styles, dress, language, ethnobotanical knowledge, dances, religion and other traditions (State Party of China, 2006).

Assessment information

Low Threat
The national park system provides a stronger legal framework to regulate the threats within the World Heritage Site, such as mining, logging, poaching etc. Most of the current threats have been well mitigated or managed. On the other hand, roads, railways, livestock grazing in alpine grassland and forests have posed some impacts on the ecosystem in the site. Mountain pasture and commercial wild plant collection remain key livelihoods for some local residents, posing a threat to habitats. The Grain for Green program along with recent restoration projects have boosted forest regeneration over the past 6-8 years. Although the Giant Panda National Park has improved the situation through measures such as legislation and ecological restoration, the impacts of habitat fragmentation and grazing disturbance have not been completely eliminated. The new railway planned to connect Dujiangyan to Mt Siguniang poses another layer of uncertainty due to the construction and potential impact along the route when it operates. More frequent extreme weather events have triggered multiple landslides/mudslides, which causes the loss of vegetation, habitat and damages on infrastructure and housing of local communities. Nonetheless, there is a lack of emphasis on the natural disaster preparation or plan to improve the resilience under climate change.
Roads, Trails & Railroads
(Roads and railroads)
High Threat
Inside site
, Scattered(5-15%)
Outside site
A few roads cross the property and/or are likely to impact the values of the property, including the Wolong to Xiaojin Highway and farming land on both sides; the highway from Chengguan to Qiaoqixiang in Baoxing County; the highway of Baishahe in Tianquan County (Sichuan Forestry and Grassland Bureau, 2016). The road from Balangshan from Wenchuan to Aba prefecture is especially sensitive (Smith & Xie, 2008; Liu et al., 2012); however, with the opening of the Balangshan Tunnel, the impact on the mountain above the tunnel has been greatly reduced. Recently a project was prepared to build a new electric railway line from Dujiangyan to Mt Siguniang (100 km) to provide faster transportation for tourists (IUCN Consultation, 2020). While the road connecting the mountain area with lowlands let local people access to the outside world, it may increase the possibility of habitat fragmentation. The increasing traffic volume may cause more environmental disturbances. The Dujiangyan-Mount Siguniang Rail which has been submitted to the World Heritage Center will reduce the impact of the existing ground transportations on the
heritage after completion, according to the State Party (State Party of China, 2023). Nonetheless, the environmental impact of the construction and operation is not fully understood. Some parts of the linear infrastructure are facing unstable slopes, which increase the probability of potential failure (Huang et al., 2020). This potentially poses threats to wildlife habitat as well as secondary geological hazards. Studies on the Giant Panda National Park show that 80% of the area has remained intact, however, 14% of the GPNP was degraded mainly in the areas below 1200 m with severe human activities. Land use and cover change and road construction were the main driving factors for the decrease of ecological intactness (Luo et al. 2022).
Residential Areas
(Villages and small towns)
Low Threat
Inside site
, Localised(<5%)
Outside site
Many small villages and some towns within the property or buffer enclaves create disturbance (Liu, 2011; Smith & Xie, 2008). There are 16662 residents living in Qingchengshan-Dujiangyan Landscape and Historical Site (Deng et al. 2019). Whilst recognised as a high threat, the expansion of small villages and some towns within the property or buffer has been greatly alleviated due to restrictions on population immigration in protected areas, and related problems are improving (IUCN Consultation, 2020). Furthermore, following strict environmental inspections between 2018 and 2020, the issue of illegal housing construction in Qingchengshan-Dujiangyan-related areas has been addressed (IUCN Consultation, 2020). 
Invasive Non-Native/ Alien Species
(Inappropriate planting roadside trees, bamboos and reforestation of bare lands)
Low Threat
Inside site
, Localised(<5%)
Planting of non-native species – including metasequoia, cryptomeria, gingko, non-local bamboos plus reforestation on landslide areas may be inappropriate for the conservation of the values of the site. Therefore this is considered a low threat, which has the potential to increase should these non-native species begin to have negative effects on the species which comprise the site's OUV (IUCN Consultation, 2020).
Logging, Harvesting & Controlling Trees
(Cutting for fuel, housing and mushrooms.)
Low Threat
Inside site
, Localised(<5%)
Outside site
Former commercial logging farms have been closed since 1980s. However, villagers cut trees for fuel, house construction and growing mushrooms (Liu, 2011).
Recreational Activities
(Growing tourism industry)
Low Threat
Inside site
, Scattered(5-15%)
Outside site
Tourism declined after the 2008 earthquake, but reopened and increase greatly (Liu et al., 2012). New investments have been made into large-scale tourism development in Tianquan and Lushan after the 2013 earthquake.  There is a crossing route through Xiao Jin across the Wolong Reserve. During June~November is the peak period, leaving large amounts of domestic waste and tree-cutting for heating (Cheng et al. 2016).
Dams & Water Management/Use
(Major dam at Qiaoqi, small dams in Wolong)
Low Threat
Inside site
, Localised(<5%)
Outside site
Dams create new still water habitat but greatly change annual water flow critical to fish and rare salamanders (Liu et al., 2012). Whilst acknowledged as a high threat due to the threat that these hydropower stations have posed to date, improvements have been made. Since 2017, China has enforced strictly and extensive evaluation on illegal construction in all national and many provincial nature reserves. As such, the government has gradually shut down small hydropower stations in this region, with more than 80% of hydropower stations now no longer operating (IUCN Consultation, 2020; State Party of China, 2023). Only a small number of hydropower stations have been retained after rigorous biodiversity impact assessments. Licenses for these hydropower stations will not be renewed and a commitment has been made that there will be no new hydropower stations in the World Heritage site in the future (IUCN Consultation, 2020).
Water-borne & other effluent Pollution
(Agricultural effluents)
Low Threat
Inside site
, Localised(<5%)
Outside site
Fertiliser and insecticide run-off from agricultural lands is thought to represent a low level threat to the values of the site (Smith & Xie, 2008), although more recent monitoring data is not available.
Garbage & Solid Waste
(Dumping in river)
Very Low Threat
Inside site
, Localised(<5%)
Outside site
Fly tipping of waste into the rivers is quite common in most towns and villages (Smith & Xie, 2008; Liu et al., 2012) and therefore represents a low level threat through solid waste pollution
Terrestrial Animal Farming, Ranching & Herding
(Livestock grazing)
High Threat
Inside site
, Scattered(5-15%)
Outside site
Livestock husbandry serves as a crucial economic income for the local communities in Wolong National Nature Reserve, with 4403 agro-pastoralists relying on livestock grazing for their livelihoods. In 2019, livestock numbers reached 14,971, including 4270 yaks (Li et al. 2023). Livestock grazing, including cattle and horses in forests has led to altered understory vegetation structure and species composition (with long-term implications for forest regeneration) and reduced bamboo biomass for pandas (UNEP-WCMC, 2012; IUCN, 2010; Hull et al., 2014). Generally, in Wolong forests, cattle and goats are much more common than horses, and they generally cause less damage. However, in recent years, livestock grazing has become more common in giant panda habitats. Due to tourism, there is an increasing trend of raising horses. For example, in Wolong Nature Reserve the total number of livestock had increased by 43.37% in 2015 compared to 2003 (Wang et al. 2018). These livestock are free-ranging in the forests and cause degradation of giant panda habitat (Hull et al., 2014; Wang et al. 2019).
Yaks graze on most high pastures, competing with wild ungulates and leading to illegal human persecution of carnivores (Liu et al., 2012). There is an increasing trend of yaks, due to the increasing tourism as well as the market demand. Yaks roam freely in the mountains for most days of the year and would be sold off in winter to outside markets. Considering that herders depend on livestock for their livelihood, it is unlikely that grazing will be completely banned in the reserve in a relatively short period. It has been recommended that the local government could gradually limit the grazing area and intensity to reduce livestock disturbance toward snow leopards and alpine ecosystems. Understanding the impact of grazing on snow leopard and its wild preys in protected areas is the basis for scientific guidance on grazing management and conservation (Li et al. 2023).
Hunting, Collecting & Controlling Terrestrial Animals
(Poaching by local villagers)
Low Threat
Inside site
, Localised(<5%)
Outside site
Snare lines are set in remote forests. Local villagers and outsiders also illegally use guns and dogs for poaching and local herders set snares and use poison around pasture land (Liu, 2011; He et al., 2008; Smith & Xie, 2008). The issue of illegal hunting by local villagers is now subject to management interventions (IUCN Consultation, 2020). Wolong consistently carry out anti-poaching patrol to remove snares and other traps. According to the State Party, hunting and other illegal activities have been strictly banned, taking place only occasionally, with a decreasing trend (State Party of China, 2023).
Air-borne Pollutants
(Acid rain and smog)
Low Threat
Inside site
, Localised(<5%)
Outside site
Atmospheric pollution sourced from industrial activities outside the site has impacted the natural values of the site. For example, the leaves of trees in the eastern parts of the site have previously been reported to have been coated with a layer of black soot from smog due to heavy industry on the Chengdu Plain and in surrounding areas (IUCN Consultation, 2020).
Geological Events
(Earthquakes and landslides)
Low Threat
Inside site
, Localised(<5%)
Outside site
The Richter 8 Wenchuan earthquake in 2008 and Richter 6.6 Lushan/Yaan earthquake in 2013 both caused landslides and much destruction to forest and infrastructure. It was found that the forest coverage in the post-earthquake, Wolong and Caopo nature reserves decreased from 56.66% to 48.11%, with a decrease of 8.55%. As of March 2011, forest cover had increased to 48.52 per cent, with an additional area of 9.19 sqkm, or 13.24 per cent of the damaged area. The study shows that the 2008 Wenchuan earthquake caused damage to the forest of giant panda habitat, but the forest cover of habitat is gradually recovering through natural restoration and artificial intervention (Zhou and Chen 2017). The forest is a mosaic of former landslides and earthquakes. Damage to giant pandas appears to be not so serious and dynamic geology may indeed be biologically enriching. Therefore landsides are assessed as a low threat only.
Gathering, Harvesting & Controlling Terrestrial Plants & Fungi
(Harvesting medicinal plants)
Other targeted species names
Gastrodia elata, Paris polyphylla, Fritillaria thun-bergli, Rheum officinale, Rhodiola rosea, Saussurea medusa, Notopterygium root, Radix Ginseng, Buddha’s palm
Data Deficient
Inside site
, Localised(<5%)
Outside site
Several medicinal plants have been harvested to critical levels, including gastroidea, gentians, caterpillar fungus amongst others (He et al., 2008; Liu, 2012; Smith & Xie, 2008; Liu et al., 2012; Tan 2017). However, the current level of this threat is unknown.
Changes in Precipitation & Hydrological Regime
(Increasing extreme precipitation)
High Threat
Inside site
, Throughout(>50%)
Outside site
Extreme precipitation has frequently triggered flash floods and debris flows, which cause great damage to the valley area, including infrastructure, loss of habitat, and reduction in connectivity. The reconstruction of villages, roads, and infrastructure causes consistent disturbance to wildlife habitats (Xiong et al., 2021).
Mining & Quarrying
(Impacts from abandoned and operating mining sites)
Low Threat
Inside site
, Localised(<5%)
Outside site
A few mining sites in the buffer zone are still in operation, which existed before the site was inscribed. With the requirements of tailings and slag outward transportation and comprehensive utilization of the mining wastes (such as for making building materials), the negative impact has been reduced. However, the potential impact needs to be paid attention to (State Party of China, 2023). Old mine shafts remain in Pitiao and other valleys which may be causing toxic run off. This has been used to explain low fish density in and around the site in the past (Liu, 2011). There is no information to indicate that this particular issue has been addressed and therefore remains a threat, albeit very low due to the inactivity of any mining operations. Marble mines in Baoxing and coal mining in Tianquan cause disturbance, noise, dust and rubble. Now being contained and controlled (Liu, 2011; Smith & Xie, 2008).
Low Threat
Some new threats may be on the horizon, including management capacity of the Giant Panda National Park Administration and tourism development. Growing pressure from tourism will likely increase in the future, bringing greater impacts to the World heritage site if not actively mitigated against.
Recreation & Tourism Areas
(Increasing tourism and associated infrastructure)
Low Threat
Inside site
, Localised(<5%)
Outside site
The site is now a part of the Giant Panda National Park, increasing the pressure for tourism development in and outside of the site, and also small town development outside of the national park. However, since the national park will be managed strictly and current now the extent of the pressure is unclear (Sichuan Forestry and Grassland Bureau, 2019).
Involvement of stakeholders and rightsholders, including indigenous peoples and local communities, in decision-making processes
Some Concern
The local communities are consulted for certain decisions. Nonetheless, there is a lack of trust from the local communities in the local authority due to unrealized promises from past experiences. The engagement of local communities in decision-making process of the local development and conservation is still very limited.
The provincial government has issued the "Opinions on Strengthening the Construction of the Sichuan Area of the Giant Panda National Park", and "carrying out the construction of entrance communities and friendly demonstration communities" is one of the important contents. The "Opinions" make it clear that priority will be given to recruiting Indigenous residents in and around the national park to engage in ecological management and protection work such as field patrols and resource monitoring, and to participate in social services such as nature education and ecological experience. At the same time, the administrative villages of the Giant Panda National Park (Sichuan Area) and some of the surrounding administrative villages will be included in the scope of leading villages for rural revitalization in the province, and the relevant policies, projects and funds of rural revitalization will be fully utilized to build villages with thriving industries, ecological liveability and rich life, so as to continuously improve the sense of gain and happiness of the indigenous residents in and around the Giant Panda National Park (People's Political Consultative Conference Daily, 2024). Nevertheless, the extent to which these plans have been realised is unclear.
Legal framework
Mostly Effective
The Environmental Protection Law of the People's Republic of China defines the overall protection goals, principles, management structures, responsibilities and general measures for protection (State Party of China, 2023). The site is covered by a range of laws and regulations at national and provincial levels. These include the ‘Regulations of the People’s Republic of China on Nature Reserves’, ‘Regulations on the Management of Nature Reserves of Sichuan Province’, and 'Regulations on the Management of Sichuan Giant Panda National Park'. A specific regulation relating to the protection of World Heritage in Sichuan Province has been developed to apply to the site, which represented the first of its kind in China. These regulations provide an adequate legal framework for the protection of the site. Challenges to date have centered around their effective implementation and the effective coordination between all relevant agencies and stakeholders (Liu et al., 2012). When the official National Park Law is passed, the site will be under stronger legal protection. The proposed Law on National Parks was presented during the 11th session of the Standing Committee of the 14th National People's Congress on Tuesday, marking the first legislation at the national level for the parks. Nonetheless, the conflicts between conservation and development have not been fully addressed in the current legal framework, and the creation of a national park has caused new conflicts.
Governance arrangements
Some Concern
The National Forestry and Grassland Administration is responsible for guiding the management of natural heritage sites nationwide. The property was managed by
its 4 cities, 10 counties, Sichuan Forestry and Grassland Administration (SFGA) and 18 management units (nature reserves, scenic spots) under the common
protection and management planning framework. After the establishment of the Giant Panda National Park, the management of the property is guided and
coordinated by the SFGA. The WH site is managed under the auspices of the Sichuan World Heritage Management Committee (SWHMC) and has a cascading structure of governance that includes representatives from the relevant government ministries and agencies involved in the site. The state of conservation report submitted to the World Heritage Committee at 34 COM mentions that “the management authority should establish regular reporting on the property’s state of conservation to the SWHMC, including information on habitat, wildlife populations and the conditions of local people, in order to allow the Committee to proactively manage the property and identify issues of concern early on” (State Party of China, 2010; Sun et al., 2006; Liu, 2011; He et al., 2008; Smith & Xie, 2008; Liu et al., 2012). The site has since been included in the Giant Panda National Park, and follows the regulation and management of the National Park System. However, the management of the World Heritage site is still fragmented. Although included in the national park, previous nature reserve units still manage different areas, and there is a lack of coordination between protected areas. For example, in Siguniangshan, tourism development has a higher priority for site management than conservation and does not follow similar governance from the rest of the world heritage site.
In July 2023, the Standing Committee of the Sichuan Provincial People's Congress adopted the decision on strengthening the coordinated protection and management of the Giant Panda National Park and the regulations on the management of the Giant Panda National Park. In the same month, Gansu Province and Shaanxi Province also adopted a decision on strengthening the coordinated protection and management of the Giant Panda National Park. Today, the three provinces of Sichuan, Shaanxi and Gansu are working together to build the Giant Panda National Park in the form of "Sichuan Regulations + Decision of the Three Provinces" (People's Political Consultative Conference Daily, 2024).
Integration into local, regional and national planning systems (including sea/landscape connectivity)
Mostly Effective
China has implemented top-down spatial planning, including the delineation of the ecological redline. With the establishment of the Giant Panda National Park, the component protected areas of the Sichuan Giant Panda Sanctuaries World Heritage site have been integrated within the wider framework, which should result in better integration into regional and national planning systems concurrently, including a unified and stronger management mechanism through which to coordinate with such planning systems (National Forestry and Grassland Administration, 2019). Nevertheless, the passing of the National Parks Law has not occurred yet.
Boundaries
Mostly Effective
Through inclusion into the Giant Panda National Park, the IUCN recommended areas are included in the national park and, therefore, protected under the highest level of national designation in China. Consideration is required to better coordinate with the Zoning Control of Giant Panda National Park with respect the boundaries of the World Heritage site (IUCN Consultation, 2020). Although there is a clear boundary setting for the map provided by the authority and the core visiting sites hold clear signs of the world heritage site, the boundary is not clear to the public or the local residents. Recent field surveys found that some parts of the boundaries do not fit to the actual situation including giant panda habitat and other wildlife species distributions and human settlements. Some parts of the boundaries are not recognised by local communities and other local stakeholders. Therefore, minor modifications to the boundaries are suggested (State Party of China, 2023).
Overlapping international designations
Mostly Effective
Wolong Biosphere Reserve is entirely within the heritage site, which is uniformly managed by the Administration Bureau of the Wolong National Nature Reserve in Sichuan Province.
Implementation of World Heritage Committee decisions and recommendations
Some Concern
At the time of inscription, the World Heritage Committee requested the State Party to implement certain measures regarding management effectiveness, existing infrastructure within the property, existing and proposed dams and tourism development (World Heritage Committee 2006). Certain progress has been achieved in addressing some of the issues as evidenced by the 2010 Mission report – “Efforts are being made on the part of the State Party to enhance management so as to improve the integrity of the property. The problems of hydropower stations and dams have now been reportedly alleviated. A large number of hydropower stations have been shut down and there will be no more hydropower stations or dams (IUCN Consultation, 2020). While action has been taken on all issues identified at the time of inscription, a number of issues remain in addition to some issues arising subsequent to inscription” (Liu et al., 2012). In response of the World Heritage Committee's recommendations to develop better tourism management plan and to consider including more area in south of the property, tourism plans were developed at local level but an integrative tourism plan is still being prepared, and the new land inclusion is under assessment (State Party of China, 2023).
Climate action
Some Concern
The master plan of the Giant Panda National Park requires the site to reinforce the existing system of natural disaster prevention and control. Coordinating with other departments, the park needs to carry out natural disaster evaluation, monitoring and response. However, there is no specific emphasis on climate action or linking natural disasters to climate change. Considering past events related to extreme precipitation, concerns remain about the lack of emphasis on this issue.
Management plan and overall management system
Mostly Effective
The original conservation management plan is based on 18 conservation management units of the property. Most of the 18 conservation management units have
been integrated. With the establishment of Giant Panda National Park, which is partly overlapped with the property, and restructuring of the management units
(many of them integrated into the national park), the management plan needs to be updated (State Party of China, 2023). A master plan of the Giant Panda National Park was released in 2023, which details requirements and further improvements needed between 2023-2030 regarding the spatial planning, management system, monitoring, research, education programs and, tourism, and community development. The master plan is comprehensive and evidence-based. Most of the existing activities follow the master plan closely with sufficient funding support and institutional support.
Law enforcement
Some Concern
China has implemented strict law enforcement in nature reserves regarding illegal construction, mining and logging (Chinese Government, 2017; Aba Government, 2017). However, due to the restructuring of the law enforcement system in China, many protected areas are facing the problem of lacking law enforcement capacity and lack of coordination with law enforcement departments. Although the national park system is addressing this issue, concerns still remain as the efficiency of law enforcement still needs improvement (Chen and Wang, 2024).
Sustainable finance
Mostly Effective
The site enjoys overall relatively high levels of finance, with a high level of variation between national and regional level protected areas. Provincial and county level protected areas and buffer areas do not receive enough finance for monitoring and management activities (Liu et al., 2012). The financing structure of the component protected areas, which comprise the World Heritage site under the Giant Panda National Park, has received sufficient funding for infrastructure building and maintenance, and local community development. The funding related to monitoring, conservation and sustainability livelihood still needs to be assessed under the national park system.
Staff capacity, training and development
Mostly Effective
Various training and capacity building have been done for the staff working in the national park. However, Shortcomings have been previously noted, with capacity building in disaster risk management especially needed (Liu et al., 2012). A site-based capacity building plan or programme is in place and partially implemented; some technical skills are being transferred to those managing the property locally, but most technical work is carried out by external staff (State Party of China, 2023).
Education and interpretation programmes
Some Concern
Increased education programs are running at Giant Panda National Park. There is a Giant Panda Eco-tourism Festival held in Ya'an, and a Giant Panda Culture Alliance was established in 2018 to promote education on Giant Panda (Sichuan Forestry and Grassland Bureau, 2019). However, compared to the traffic of tourists in the World Heritage Site, the education and interpretation programs are still insufficient (State Party of China, 2023).
Tourism and visitation management
Mostly Effective
Management of tourism development activities has been greatly strengthened in recent years. Since 2017, the construction of illegal tourism infrastructure in Wolong and other places have been significantly curbed, and all tourism development activities have been subject to strict planning consistency and biodiversity impact reviews (IUCN Consultation, 2020). However, less attention has been paid to increasing tourism staff capacity or tourist visitor awareness of conservation issues (Liu et al., 2012), which could be improved upon further.
Sustainable use
Some Concern
Unsustainable tourism and other forms of unsustainable land use have been reported as a concern in the past (Liu, 2011; He et al., 2008; Liu et al., 2012; Smith & Xie, 2008). There is a lack of evidence to suggest that this has been sufficiently addressed and therefore remains of some concern. However, environment-friendly agriculture and sustainable tourism is recognised by the management authority as an important way to promote sustainable resource utilization and a direction of efforts towards these ends is currently being pursued (IUCN Consultation, 2020). There are no guidelines for the sustainable use of natural resources within the site or the national park. The existing regulation either bans certain ways of natural resource use or vaguely mentions traditional livelihood is allowed without specifying whether it is still within the sustainable limit. This creates problems such as overgrazing in certain parts of the site, over-harvest of certain medicinal plant species etc.
Monitoring
Mostly Effective
There is a comprehensive survey of giant pandas every 10 years, with conservation efforts assessed periodically every 5-8 years (State Party of China, 2023). Monitoring programs for the species can be considered highly effective. The most recent survey (the fourth survey) was finished in 2014. Compared with the third survey, the results of the fourth giant panda survey showed the following characteristics: 1) the number of wild populations increased steadily. The number of wild giant pandas in the country increased by 268 to 1864, an increase of 16.8%, compared with the third survey, and the average population density was 0.072 per square kilometer. Among them, there are 1387 pandas in Sichuan Province, accounting for 74.4% of the total wild pandas in the country. Second, the scope of habitat is obviously expanded. Habitat area increased by 11.8% and potential habitat area increased by 6.3% (National Forestry and Grassland Administration, 2015). In recent years, there have been increasing efforts to monitor snow leopards in the alpine area (Tang et al., 2017). Comparatively, the monitoring of other species is less systematic (World Heritage Committee, 2012).

Key indicators: Conservation effects (giant panda population and habitat conditions, species richness, rare and endemic species population, invasive species, etc.), management
effectiveness ( the intensity of human activities, forest fire-prevention, pest control, illegal hunting prevention, etc.), management features (protection management
organization, rules and regulations, etc.), the sustainable development (poverty population and poverty alleviation, etc.) capacity building (the number of staff etc.)
Research
Some Concern
Much research has been done in the site, but this is still not enough to meet the existing challenges. Especially needed is research that would integrate biodiversity conservation, rural development and disaster risk reduction for overall sustainability and resilience of the World Heritage site.
Effectiveness of management system and governance in addressing threats outside the site
Mostly Effective
Giant panda habitat conservation has a long history and China has put significant efforts towards this end. Since 2018, the area has been included in the new development of the Giant Panda National Park, which should extend protection of key habitats outside the site and improve ecological connectivity. Concerns regarding tourism management and urban development outside of the site are subject to attention from the management authorities, having been a concern in the past. Overall, the management system does not have the capacity or power to address the conservation issues outside the site.
Effectiveness of management system and governance in addressing threats inside the site
Some Concern
Some concerns were expressed at the time of the inscription of the property with regard to the management effectiveness. The World Heritage Committee requested the State Party to “Ensure the Sichuan World Heritage Management Committee has sufficient powers, resources and authority to ensure it can effectively carry out its role in relation to the management of the property, including in relation to the review and approval of any major development proposals which may impact on the natural values of the nominated property” (World Heritage Committee, 2006). However, even with the establishment of the Giant Panda National Park, several conservation threats persist, such as extensive livestock grazing, trespassing of illegal hikers, poaching, and illegal natural resource exploitation.
Wolong as the central protected area of the site has always enjoyed first place in concern, financial and human resource investment of all China’s protected areas. Some of the other county sites are still poorly supported and require improvements in staffing, operational budgets, basic ecological training and management capacity. Investment in protection and management of the habitats and ecosystems for which the site is inscribed is relatively low compared to the investment in captive breeding of giant pandas. The headquarter of the breeding centre has moved to Chengdu in 2024, which could cause the loss of research staff who support some of the in situ conservation. There is a lack of integration between conservation of giant pandas and local community development, causing distrust, conflicts and lack of engagement of the local stakeholders. The problem of weak coordination of management between sub-sites via the World Heritage office has been partly addressed by the site becoming a part of Giant Panda National Park. However, it is still very fragmented as the national park system is under development and existing sites are mainly managed through the old system. There is also a major gap in integrating conservation and development policies with effective disaster risk management planning and implementation.
Good practice examples
Xiaojin county carries out the green development mode of rose planting industry which is "company + agricultural cooperative + farmers + agricultural industrialized base" in the buffer zone of the Heritage. In this mode, the company implements the planting, processing, and sales of Jinshan rose. Agricultural cooperative provides farmers with agricultural materials, training and technical services. Meanwhile, the cooperative unified purchase farmers' roses. This development mode has led more than 3300 households in 40 villages of 13 townships to join the cooperative, creating an annual output value of more than 7.74 million US dollars. This case alleviates the local people's dependence on the traditional resources of the giant panda habitat, and mitigates the contradiction between the heritage management and local economic development (State Party of China, 2023).

High proportion of global population of iconic giant panda

Good
Trend
Improving
Continued improvement of bamboo habitat following the flowering and die-off in the 1980s plus good protection and connectivity and low mortality in earthquakes supported by periodic new surveys indicate a healthy and increasing population. The population of giant pandas in the wild in China is currently around 1,900 rising from about 1,100 in the 1980s, the National Forestry and Grassland Administration (The State Council, 2024). The Giant Panda National Park is home to 1,340 wild giant pandas, accounting for 71.89% of its total population in China, among which 1,200 or 93% are found in the Sichuan Section. The Sichuan Giant Panda Sanctuaries, on the other hand, cover over 1.5 million hectares and 58.48% of China’s giant panda habitat (UNESCO, 2023).

Rich montane flora, with many endemic species

Good
Trend
Stable
Satellite imagery indicates forests and vegetation remain in good condition so, apart from over-collected rare medicinal plants, richness of flora should be retained and resilient against climate change.

Rare and endemic birds

Data Deficient
Trend
Data Deficient
The bird fauna seems to be undisturbed and there are no indications of declines, however there is a lack of updated data to be certain of the state and trend overall. Between 2005 and 2020, 232 wild bird species belonging to 13 orders, 45 families and 132 genera were recorded via camera-trap monitoring in 51 protected areas within GPNP (Tian et al. 2021).

Rare and threatened mammals

Low Concern
Trend
Improving
Despite a small amount of illegal poaching, with the strengthening of protection measures, the number of mammals has risen in a restorative manner. The monitoring of Wolong snow leopards has shown increased population size than previously thought as well as prey species population increases, such as blue sheep. Wildlife populations are mostly stable or improving. Giant pandas, golden monkeys, takins, and red pandas are all at least stable, with some improvement.

Between 2005 and 2020, 71 wild mammal species belonging to 6 orders, 22 families and 55 genera were recorded via camera-trap monitoring in 51 protected areas within GPNP. Among the four mountain ranges within GPNP. The numbers of species recorded in national protected areas were significantly higher than those in provincial protected areas (19 ± 8.9). Four large carnivores of Felidae and Canidae (leopard Panthera pardus, snow leopard P. uncia, wolf Canis lupus and dhole Cuon alpinus) were recorded in the GPNP (Tian et al. 2021).

Diversity of habitats

Good
Trend
Stable
Full range of habitats maintained.

Diverse endemic richness of other groups

Low Concern
Trend
Data Deficient
General condition for many species in the site is improving, although there are some concerns on aquatic species and economic important species.
Assessment of the current state and trend of World Heritage values
Stable
Despite some damage from landslides/mudslides caused by extreme precipitation and human developments (roads etc.), the site retains its essential World Heritage values and remains in a very natural state over the majority of its area. It continues to serve as the heart of China’s wild giant panda population and the hub of giant panda conservation, which will likely be further enhanced as part of the Giant Panda National Park.
Assessment of the current state and trend of other important values
Data Deficient
Data Deficient
Previous related work has paid insufficient attention to cultural heritage. The Giant panda national park master plan (2023-2030) emphasized the need to strengthen the exploration and protection of cultural heritage in the Giant Panda National Park, promote the preservation of intangible cultural heritage, collaborate with authorities to conduct surveys, and establish heritage archives and databases.

Additional information

Outdoor recreation and tourism
Tourism is becoming the major commercial industry for many villages and towns around the property. Recent earthquakes have demonstrated that this is a vulnerable reliance. Benefits from tourism could be better distributed among local communities to encourage greater participation.
Water provision (importance for water quantity and quality)
The property forms part of the critical water catchment of the Yangtze River on which hundreds of millions of people depend and vast hydro-investments (Three Gorges Dam, Zhouba, etc.) are also dependent. Water supply and flood prevention are crucial services.
Soil stabilisation
Healthy forests in the property provide protection for human settlements from small-to-medium scale landslides and debris flows, and may contribute to reduced economic loss and mortality in major disaster events (e.g. the earthquakes).
Carbon sequestration
The area is a large healthy forest contributing to carbon sequestration and local climate amelioration, serving as a wonderful green lung on the edge of the densely populated Sichuan basin.
Collection of genetic material
Although not very developed, the property constitutes a vast gene bank of rare trees, valuable horticultural plants (rhododendrons, magnolias, etc.), wild fruit relatives (plums, cherries, apples, pears) and valuable medicinal plants.
The property is recognised as a valuable generator of tourism industry (both direct and indirect) and provider of vital ecosystem services. It is zoned as an ecological priority area in both the National Biodiversity Strategy and Action Plan and also the National Hydrological map of key areas for conservation.  It has been included in the Giant Panda National Park, which is the highest rank of protected area management categories in China since 2017 and will benefit much wider visitors from China and other countries.
Organization Brief description of Active Projects Website
1 Shan Shui (domestic NGO) Long-term interest in panda monitoring and some community projects.
Shan Shui, Beijing (www.shanshui.org)
2 WWF Original foreign partner in developing Wolong research and breeding centres. Continued support for monitoring and some community projects.
WWF China, Beijing
3 NFGA (National Forestry and Grassland Administration) NFGA manages several major national projects within the property including Natural Forest Protection Program, Sloping Land Conversion Program, Post-earthquake Ecological Restoration Programme, panda breeding centre and release trials. Now it will manage the Giant Panda National Park directly.
4 CAS (Chinese Academy of Sciences) CAS has several institutions in Beijing and Chengdu which are doing various project in the site, such as species research, ecosystem monitoring, remote sensing assessment and many others.
http://www.cas.cn/
5 Peking University Students in the university are doing many studies in the site, including species conservation and community development.
https://www.pku.edu.cn/
6 Duke Kunshan University Duke Kunshan university is doing research on grazing impact to giant panda.

References

References
1
Aba Government (2017).  Wenchuan County to promote the rectification of nature reserves. Available at: http://www.abazhou.gov.cn/abazhou/c101989/201708/d28dcb42aa… (Accessed on 1 May).
2
BirdLife International (2009). Directory of Important Bird Areas in China (Mainland): Key Sites for Conservation. Cambridge, UK: BirdLife International.
3
Chen, Z. and Wang, L. (2024). Practice Patterns, Dilemmas and Optimization Paths of Integrated Administration of Nature Reserves. Administration and Law, 7, 63-78.
4
Cheng, Y., Chen, C., Feng, J., Qiao, M., Yang, J., He, M. (2016). Research on Conservation Management Strategy for the Reshuihe Area in Wolong National Nature Reserve. Agriculture and Technology 36(3): 150-152.
5
Chinese Government (2017). Special Supervision and Inspection of National Nature Reserves. Available at: http://www.gov.cn/xinwen/2017-07/21/content_5212176.htm (Accessed: 28 April 2020).
6
Deng, W., Song, L., Wang, X., Yu, H. (2019). Planning Method of Harmonious Development between Scenic Area and City for Scenic Area of City: A Case Study on General Planning of Qingchengshan-Dujiangyan Scenic Area. Development of Small Cities and Towns, 37(6): 1009-1483.
7
He, G., Chen, X., Liu, W., Bearer, S., Zhou, S., Cheng, L.Y., Zhang, H., Ouyang, Z. and Liu, J. (2008). Distribution of Economic Benefits from Ecotourism: A Case Study of Wolong Nature Reserve for Giant Pandas. China Environmental Management, 42(6), pp.1017–1025.
8
Huang, Q., Fei, Y., Yang, H., Gu, X., & Songer, M. (2020). Giant Panda National Park, a step towards streamlining protected areas and cohesive conservation management in China. Global Ecology and Conservation, 22, e00947.
9
Hull, V., Zhang, J., Zhou, S., Huang, J., Vina, A. Liu, W., Tuanmu, M., Li, R., Liu, D., Xu, W., Huang, Y, Ouyang, Z., Zhang, H. and Liu, J. (2014). Impact of Livestock on Giant Pandas and their Habitat. Journal for Nature Conservation, 22(3), pp.256–264. DOI:10.1016/j.jnc.2014.02.003.
10
IUCN (2006). World Heritage Nomination – IUCN Technical Evaluation, Sichuan Giant Panda Sanctuary – Wolong, Mt. Siguniang and Jiajin Mountains (China) – ID N° 1213. In: IUCN World Heritage Evaluations 2006, IUCN Evaluations of nominations of natural and mixed properties to the World Heritage List. WHC-06/30.COM/INF.8B2. [online] Gland, Switzerland: IUCN. Available at: http://whc.unesco.org/archive/2006/whc06-30com-inf8b2e.pdf (Accessed: 13 February 2019).
11
IUCN (2010). Report on a Monitoring Mission to Sichuan Giant Panda Sanctuaries (China). [online] Gland, Switzerland: IUCN . Available at: http://cmsdata.iucn.org/downloads/sichuan_giant_panda_sanct… (Accessed: 13 February 2019).
12
IUCN Consultation (2020). IUCN Confidential Consultation- Sichian Giant Panda Sanctuaries- Wolong, Mount Siguniang & Jiajin Mountains, China. 
13
International Council for Bird Preservation (ICBP) (1992). Putting Biodiversity on the Map: Priority Areas for Global Conservation. Cambridge, UK: ICBP.
14
Li, J., Shi, X., He, X., Li, D., Hu, Q., Zhang, Y., & Ran, J. (2023). Free‐ranging livestock affected the spatiotemporal behavior of the endangered snow leopard (Panthera uncia). Ecology and Evolution, 13(4), e9992.
15
Liu, W. (2011). A Preliminary Investigation of Alpine Conservation Status and Its Implication on Snow Leopard Conservation in Wolong Nature Reserve, Sichuan, China. Snow Leopard Network. [online] Available at: http://www.snowleopardnetwork.org/GrantFinalReports/LiuFina… (Accessed: 07 July 2019).
16
Liu, W. (2012). Patterns and impacts of tourism development in a coupled human and natural system. PhD Thesis. East Lansing: Michigan State University.
17
Liu, W., Vogt, C., Luo, J., Frank, K., He, G. and Liu, J. (2012). Drivers and Socioeconomic Impacts of Tourism Participation in Protected Areas. PLoS One, 7(4), p.35420.
18
Luo, C., Yang, H., Luo, P., Liu, S., Wang, J., Wang, X., ... & Xie, W. (2022). Spatial-temporal change for ecological intactness of giant panda national park and its adjacent areas in sichuan province, China. Diversity, 14(6), 485.
19
National Forestry and Grassland Administration (National Park Administration) (2019). Overall Plan of Giant Panda National Park (for review). Available at: http://www.forestry.gov.cn/main/153/20191017/11241342619361… (Accessed on 1 May).
20
People's Political Consultative Conference Daily (2024). For the harmonious coexistence of "national treasures" and "villagers" - the wisdom of the Sichuan CPPCC in the construction of the Giant Panda National Park. People's Political Consultative Conference Daily. Published 9 August 2024.
21
Rao, J., Bai, W., Zhang, J. Dong, X. (2018). A Study of Spatial Utilization and Habitat Selection of Giant Pandas in Caopo Nature Reserve. Journal of Sichuan Forestry Science and Technology 39(3): 7-12.
22
Sichuan Forestry and Grassland Bureau (2016).  Giant Panda Population - Sichuan Population. Available at http://lcj.sc.gov.cn/scslyt/decpc/2016/4/8/234db254c57b468e… (Accessed: 28 April 2020)
23
Sichuan Forestry and Grassland Bureau (Giant Panda National Park Sichuan Administration), (2019). China (Sichuan) Giant Panda International Ecotourism Festival Closing Ceremony in Ya'an. Available at: https://www.sohu.com/a/283149825_100245361 (Accessed on 1 May).
24
Smith, T. and Xie, Y. (eds.) (2008). A Guide to the Mammals of China. Princeton, NJ: Princeton University Press.
25
State Party of China (2003). The World Heritage Sichuan Giant Panda Sanctuary- Wolong, Mt. Siguaniang and Jiajin Mountains Overall Management Plan. [online] Available at: https://whc.unesco.org/en/list/1213/documents/ (Accessed: 05 July 2019).
26
State Party of China (2006). Nomination of Sichuan Giant Panda Sanctuaries – Wolong, Mount Siguniang & Jiajin Mountains as a World Heritage site. [online] Ministry of Construction of the People’s Republic of China. Available at: https://whc.unesco.org/en/list/1213/documents/
(Accessed: 16 January 2019).
27
State Party of China (2023). Periodic Reporting Cycle 3, Section II: Sichuan Giant Panda Sanctuaries - Wolong, Mt Siguniang and Jiajin Mountains. Available at: https://whc.unesco.org/en/list/1213/documents/
28
State Party of China. (2010). Report of the State Party to the World Heritage Committee on the state of conservation of the Sichuan Giant Panda Sanctuaries - Wolong, Mt Siguniang and Jiajin Mountains (China). [online] Available at: < https://whc.unesco.org/en/soc/535>; (Accessed 13 February 2019).
29
Sun, J., Baker, B., Bachelet, D., Daly, C., Ma, J. and Liu, L., (2006). "Impact of climate change in the Hengduan Mountains of northwestern Yunnan, P.R. China: vegetation distribution change in the foretime and future", Proc. SPIE 6296, Earth Observing Systems XI, 62960X.
30
Tan, H., Cheng, Y., Qiao, M., Yang, P., He, M (2017). Medicinal Plants Harvesting in Wolong National Nature Reserve. J. Resour. Ecol. 2017 8(3) 304-312.
31
Tang, Z., Yang, J., Liu, X., Wang, P., & Li, Z. (2017). Research on snow leopards (Panthera uncia) using camera-trapping in Wolong National Nature Reserve, China. Biodiversity Science, 25(1), 62.
32
The State Council (2024). China's wild panda population nears 1,900. People's Republic of China. Published 25 January 2024. Available at: https://english.www.gov.cn/archive/statistics/202401/25/con…
33
Tian, J., Zhu, S., Zhang, X., He, L., Gu, X., Guan, T., & Li, S. (2021). The diversity of large-and medium-sized terrestrial mammals and birds in the Giant Panda National Park: A meta-analysis based on camera-trapping data. Biodiversity Science, 29(11), 1490.
34
UNEP-WCMC (2012). Sichuan Giant Panda Sanctuary – Wolong, Mt. Siguniang and Jiajin Mountains (China). UNEP-WCMC World Heritage Information Sheets. [online] Cambridge, UK: UNEP-WCMC. Available at: https://yichuans.github.io/datasheet/output/site/sichuan-gi… (Accessed: 05 July 2019).
35
UNESCO (2023). UNESCO Builds Capacity for Giant Panda National Park Managers in Sichuan Province. UNESCO News. Published online 5 May 2023. Available at: https://www.unesco.org/en/articles/unesco-builds-capacity-g…
36
Wang, X., Li, Y., Li, C., Zhang, J. (2018). Impact of Grazing to Giant Panda in Wolong Nature Reserve. Journal of China West Normal University (Natural Sciences) 39(1): 12-15.
37
Wang, X., Zhang, J. (2019). Advances in the Impact of Livestock Grazing on Giant Pandas. Sichuan Journal of Zoology38( 6) : 714 - 720.
38
World Heritage Committee. (2006). Decision 30 COM 8B.22. Sichuan Giant Panda Sanctuaries - Wolong, Mt Siguniang and Jiajin Mountains (China). [online] Vilnius, Lithuania: UNESCO World Heritage Centre, WHC-06/30.COM/19, p. 135-136. Available at: < https://whc.unesco.org/document/6728>; (Accessed 13 February 2019).
39
World Heritage Committee. (2012). Decision 33 COM 8E. Sichuan Giant Panda Sanctuaries – Wolong, Mt Siguniang and Jiajin Mountains (China). [online] Saint Petersburg, Russian Federation: UNESCO World Heritage Centre, pp.224-225. Available at: < https://whc.unesco.org/en/decisions/4841>; (Accessed 13 February 2019).
40
Wu, S., Fang, Z., Sun, N. (2018). The restoration effect of ecological environment in Wenchuan earthquake area is obvious. Available at http://www.qstheory.cn/zoology/2018-05/14/c_1122831032.htm (Accessed: 28 April 2020).
41
Xiong, J., Tang, C., Gong, L., & Chen, M. (2021). Variability of rainfall time distributions and their impact on peak discharge in the Wenchuan County, China. Bulletin of Engineering Geology and the Environment, 80, 7113-7129.
42
Xu, J., Wei, J., & Liu, W. (2019). Escalating human–wildlife conflict in the Wolong Nature Reserve, China: A dynamic and paradoxical process. Ecology and evolution, 9(12): 7273-7283.
43
Ye, P., Wang, J., Cheng, Y., Fu, Y., Jiang, H., Tang, Z., Tang, L., Zou, S. (2018). Preliminary Study on the Application of Gridded Management in Nature Reserves - Take Wolong Nature Reserve as an Example. Sichuan Forestry Exploration and Design (3): 84-90.
44
Zhou, X., Chen, F. (2017). Change Detection of Forest Coverage in Sichuan Giant Panda Sanctuaries Using PALSAR Time Series Data. Remote Sensing Technology and Application 32(6): 110-1106.

Indigenous Heritage values

Would you like to share feedback to support the accuracy of information for this site? If so, send your comments below.

CAPTCHA
This question is for testing whether or not you are a human visitor and to prevent automated spam submissions.