Mount Emei Scenic Area, including Leshan Giant Buddha Scenic Area

Country
China
Inscribed in
1996
Criteria
(iv)
(vi)
(x)
The conservation outlook for this site has been assessed as "good" 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.
The first Buddhist temple in China was built here in Sichuan Province in the 1st century A.D. in the beautiful surroundings of the summit Mount Emei. The addition of other temples turned the site into one of Buddhism's holiest sites. Over the centuries, the cultural treasures grew in number. The most remarkable is the Giant Buddha of Leshan, carved out of a hillside in the 8th century and looking down on the confluence of three rivers. At 71 m high, it is the largest Buddha in the world. Mount Emei is also notable for its exceptionally diverse vegetation, ranging from subtropical to subalpine pine forests. Some of the trees there are more than 1,000 years old. © UNESCO
Jacques Beaulieu CC BY NC 2.0

Summary

2020 Conservation Outlook

Finalised on
02 Dec 2020
Good
The conservation outlook for Mount Emei Scenic Area, including Leshan Giant Buddha Scenic Area is Good overall. The site is a very significant national sacred place and is an internationally renowned religious site, which attracts huge numbers of tourists and pilgrims. The management of the property is being improved under strong protection legislation and planning provisions. Although there is some overcrowding at times, current visitor impacts are recognized and controlled through management intervention, however, the impact of tourism is still significant. Apart from the recent flooding event in August, which was the first of its kind since the 1940s, there are few other threats and pressures on natural values in particular, and are considered to be of low impact. However, greater monitoring and research is required to ensure that this is the case and to inform better management of the biodiversity related values of the site in future. The likely increase in climate change effects on species and habitats should also be closely watched.  A better balance of management effort between the protection of cultural values, which are given priority, and natural values would ensure the values listed under natural criteria are well conserved in the long term.

Current state and trend of VALUES

Low Concern
There are some low-level concern about the condition of natural values of the property, particularly in areas where tourism is concentrated and which therefore face both direct impacts from tourism disturbance and indirect impacts, such as atmospheric pollution and the as yet unknown effects of the recent flooding in the site. Insufficient management effort is directed at monitoring of the highly significant natural values and there may be undesirable trends that remain undetected. The imbalance between management of cultural and natural values should be redressed.

Overall THREATS

Very Low Threat
Overall threats to the property are generally of low impact. The most obvious threats stem from the large and increasing numbers of tourists and pilgrims, and the consequential development of facilities infrastructure and the recent flooding in the site. A cable and monorail provide ready access to high summits but can cause overcrowding at the most popular spots and introduce people to sensitive vegetation habitats. The recent flooding event in August 2020 is concerning, the effects of which on the World Heritage values should be assessed and mitigated against should future flooding events occur in the site in the future. Additional threats relate to acidification of freshwater bodies and soil from air pollution.

Overall PROTECTION and MANAGEMENT

Mostly Effective
Protection and management in recent years, especially with increased tourist pressure, is mostly effective and being improved. However, there is a lack of available monitoring data to indicate its effectiveness fully. Management of the property is well-founded in law and guided by a comprehensive management plan providing regulations and other measures for effective management intervention and rapid measures were put into place in response to the flooding event in August. There is a full scientific programme and research results are used to improve management. Some concerns relate to the lack of monitoring of human impacts on biodiversity values.

Full assessment

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Description of values

Exceptionally rich plant diversity of special significance to conservation and science

Criterion
(x)
Located transitionally between the Sichuan Basin and the eastern Himalayan mountains, Mt Emei has an exceptionally rich floral diversity consisting of some 3,200 plant species, of which more than 100 species are endemic (World Heritage Committee, 2012). Among the important plants are orchids, primulas, rhododendrons, camellias, ginkgos, cycads and tree ferns (Foster et al. 2010; Li & Shi,2007). Mt. Emei has the most typical and well preserved subtropical mountain vegetation landscape, developing complete forest vertical band from low to high. Over an altitudinal range of 2,600 m there are many vegetation zones including subtropical evergreen broad-leaved forest, mixed evergreen and deciduous broad-leaved forest, mixed broad-leaved and conifer forest, and subalpine conifer forest. Rare and threatened subtropical plants, such as Alsophila, Cibotium barometz and other ombrophyte species can be found here. Endangered relict plants like Davidia involucrata, Cercidiphyllum, Tetracentron sinense are preserved in evergreen and deciduous mixed forest (World Heritage Committee, 2012; IUCN Consultation, 2017). 

Rich fauna of global importance

Criterion
(x)
The diverse vegetation habitats support more than 2,300 species of animals, including several threatened at the global scale such as the red panda, Asiatic black bear and golden cat, Tibetan macaque and Chinese giant salamander (State Party of the People’s Republic of China, 1995; World Heritage Committee, 2012; UNEP-WCMC, 2011).
Other biodiversity values
The Mt Emei property is within a WWF Global 200 Freshwater Eco-region and a Birdlife International Endemic Bird Area. It is identified as a Key Biodiversity Area by Conservation International and an Alliance for Zero Extinction Site. It is noteworthy that protection of the natural values of the site has been enhanced by its long-standing status as a national sacred site.

Assessment information

Low Threat
Threats to the site’s value mainly stem from tourism developments and operations. Tourism impacts on plant biodiversity and soil, and indirect threat on other species such as amphibians are of a concern (Ni, 2016). Recent flooding in the site gives cause for concern for the values of the site, even if the extent of damage sustained by these floods is not yet fully understood, in addition to worrying prospects for similar flooding events in the future.
Water-borne & other effluent Pollution
(Acidification of freshwaters.)
Low Threat
Inside site
, Extent of threat not known
Acid rain from air pollution has detrimentally affected streams, rivers, ponds and lakes (Foster et al. 2010).
Recreation & Tourism Areas
(Tourist infrastructure and facilities development, overcrowding and rubbish production.)
Low Threat
Inside site
, Scattered(5-15%)
There is intensive tourism development inside the property. The impact along the tourism sites and trails on vegetation is significant and tourist disturbance also has an impact on soils (Ni, 2016). Feeding of Macaque monkeys by tourists remains a problem, having been previously identified (Priston, 2013). Management efforts have been made to control the impact of tourism but their effectiveness remains to be demonstrated. (Lu, 2013, Wang, 2013, Zhu 2013, Fan, 2012, IUCN Consultation, 2017). in particular, construction of tourism facilities has increased significantly around Fuhu Temple and impacts have been observed on the landscape of subtropical evergreen broad-leaved forest of Mt. Emei (IUCN Consultation, 2017).
Roads, Trails & Railroads
(Transport systems for visitors)
Low Threat
Inside site
, Scattered(5-15%)
A cable car carries hundreds of thousands of visitors annually to Golden Summit and has accentuated crowding pressure at this popular spot. It also brings more people into the sensitive montane forest belt. A 2.1 km-long light monorail was installed in 1998 to carry people from Golden Summit to Wanfoding Summit. (ICOMOS, 1995; IUCN, 1995; SOC Report, 2000).The monorail is currently not being operated and therefore its impacts are minimal. Plans for a new cable car to be built to Wanfoding Summit have been discussed (Emei official website, 2017); and potential impacts of this development are unclear.
Other Biological Resource Use
(Harvesting of plants and animals)
Low Threat
Inside site
, Extent of threat not known
There are reports that harvesting of some animal species, including some endemic amphibian species, continues despite management efforts to prevent it; however, the extent of impacts is unclear (IUCN Consultation, 2017; Huaxi Daily, 2014).
Storms/Flooding
(Flooding)
Low Threat
Inside site
, Extent of threat not known
On 19th August 2020, severe flooding brought water levels to extremely high levels not seen since the 1940s, posing a threat to the vaules of the site, including the Leshan Buddha, whose toes were flooded. Sichuan province has activated its highest level emergency response after weeks of heavy rain caused record high water levels in order to mitigate the threat with flood alerts are in place for provinces around the Yangtze (BBC, 2020). 
Mostly Effective
The property is managed under local administration and a management plan exists along with specialized plans (People’s Republic of China, 1995; WCMC, 2012).
Mostly Effective
Management appears to be implemented and effective (UNESCO, 2000, Lu, 2013). With increased tourism pressure in recent years, more stringent management measures will be required (Ni, 2016).
Mostly Effective
The boundaries of the property are considered adequate. Due to its size and relative inaccessibility, much of the area remains under low pressure or conflict regarding the site's boundaries  (World Heritage Committee, 2012).
Data Deficient
Data deficient.
Mostly Effective
Ongoing relocation of local residents have continued and there are now around 12,00 permanent residents in the site, mainly peasant farmers and Buddhist monks (IUCN Consultation, 2020), a decrease of 8,000 since the last Outlook assessment in 2017 (WCMC, 2012; IUCN Consultation, 2017). Residents have participated in a community based enterprise development study and trial (FAO, 2006). Monks have been encouraged to play a larger role in supporting and managing the property (20COM VIII.B).
Mostly Effective
There are good national and local laws for protection and management of natural and cultural values and attributes (People’s Republic of China 1995; ICOMOS 1995; IUCN 1995; UNESCO, 2000). Less is known about enforcement processes and capability.
Mostly Effective
The local government and the Scenic Spot's Management Committee are reported to effectively enforce relevant laws in accordance with the Regulations on Scenic Spots, the Regulations on the Protection of World Heritage in Sichuan Province, and the Regulations on the Protection of Mount Emei World Cultural and Natural Heritage (IUCN Consultation, 2020).
Mostly Effective
State Party has generally responded to Committee requests and recommendations.
Some Concern
The main use of the property is for tourism. However, there are some concerns with regards to increasing pressure from tourism numbers and associated facilities and developments (IUCN Consultation, 2020).
Mostly Effective
Most of the scenic spot ticket income is reported to be used for the protection of the property (IUCN Consultation, 2020). The Scenic Spot's Management Committee has also raised nearly 2 billion yuan through other fund-raising channels for the ecological relocation of native villagers from the scenic spot down the mountain and into the city, as well as for the facility construction work and its protection work, such as supplying and constructing sewage treatment stations in the property.
Data Deficient
The local government and the Scenic Spot's Management Committee regularly train managers and scientific researchers to facilitate the further protection of the property (IUCN Consultation, 2020). There is little information however on the scope of the training.
Data Deficient
The Mount Emei Museum is the main resource for the education and display of Mount Emei heritage resources, however, there is no information on the effectiveness of the museum in conveying the values of the site to visitors.
Some Concern
Some concerns have been raised about infrastructure development, overcrowding at sites and on trails, and littering (ICOMOS 1995; IUCN 1995; WCMC, 2012). Whilst these concerns remain, the maximum number of visitors admitted per day is limited, which means tourists will no longer be received when the daily maximum carrying capacity is reached. The garbage in the scenic spot is also now cleared and transported out of the scenic spot for disposal on a daily basis (IUCN Consultation, 2020).
Some Concern
Concern has been noted regarding the lack of monitoring of impacts on natural values in the past (WCMC, 2012). However, there are now three atmospheric automatic monitoring stations and forest resource positioning research stations and other heritage monitoring facilities in the scenic spot, with the monitoring data released through the official website (IUCN Consultation, 2020).
Mostly Effective
There has been much research effort on natural and cultural features both by international and domestic scientists. There are 15 specialized scientific and technical institutions in the area including a botanical garden. Plant and animal specimens are held in many international collections (WCMC, 2012).
Assessment of the effectiveness of protection and management in addressing threats outside the site
Data Deficient
Data Deficient
Assessment of the current state and trend of World Heritage values
Data Deficient
Assessment of the current state and trend of other important biodiversity values
Data Deficient
Data Deficient
Data Deficient

Additional information

History and tradition
The property is of exceptional cultural and spiritual significance as the birthplace of the Buddhist religion in China and the place from where it spread widely through the East. It is one of the four holy lands of Chinese Buddhism. It also contains a magnificent array of religious monuments and treasures, including the largest carved statue of Buddha in the world.
Outdoor recreation and tourism
The Mt Emei property is one of the most important Buddhist worship centres in the world and attracts huge numbers of domestic and international pilgrim visitors.
Mt Emei is of major global significance for profession and promotion of Buddhist religious faith, and an internationally important centre of religious tourism. The property is also of global significance for the protection of plant and animal diversity within the Asia region. As such, Mt Emei is a place of major benefit to the world community for protection of outstanding universal cultural and natural values.
Organization Brief description of Active Projects Website
1 Emei Captive Panda Breeding Centre Introduced 3 pandas from Wolong Panda Research Centre and the number increased to 7 in 2016. Scientific research is ongoing.
2 Sichuan Natural Resource Research Institute Forest pest survey
3 Sichuan Natural Resource Research Institute Emei Biological Resource Station. This is a research platform that have facilitated multiple long-term species and ecosystem researches and education programs, as well as establishing a botanical garden in Emei.

References

References
1
BBC. (2020). China record floods wet feet of Leshan Buddha. [online] London, UK: BBC. Available at: https://www.bbc.co.uk/news/world-asia-china-53831271 [Accessed 25 November 2020].
2
FAO. (2006). Community-based commercial enterprise development for the conservation of biodiversity in Mount Emei World Heritage Site, Sichuan, China. Forestry Policy and Institutions Working Paper No. 17, Rome, Italy.
3
Fan W J, Sun J H, Sun K Q. (2012). A synthetic analysis on the effective Protection and management of World Heritage Sites in the geological disaster area: a case study of Sichuan, China. Advanced Materials Research. Trans Tech Publications, 524, 2702-2711.
4
Fan Z, Zhong S, Zhang W. (2012). Harmonious tourism environment and tourist’s perception: An empirical study of mountain-type world cultural heritage sites in China. Journal of Service Science and Management, 5(01), 95.
5
Foster, M.N. et al. (2010). Synergies between World Heritage sites and key biodiversity areas. World Heritage Paper No. 56, Paris, France: UNESCO.
6
Huaxi Daily. (2014). Rare species Emei Mogophrys frog sold to restaurant at a high price. 
7
ICOMOS. (1995). World Heritage Nomination – ICOMOS Technical Evaluation, Mount Emei, including the Leshan Buddha Scenic Area (China). In: IUCN World Heritage Evaluations 1995, ICOMOS Evaluations of nominations of natural and mixed properties to the World Heritage List. [online] Paris, France: ICOMOS. Available at: https://whc.unesco.org/en/list/779/documents/ [Accessed 25 November 2020].
8
IUCN Consultation. (2020). IUCN Confidential Consultation- Mount Emei Scenic Area, including Leshan Giant Buddha Scenic Area, China
9
IUCN. (1995). World Heritage Nomination – IUCN Technical Evaluation, Mount Emei, including the Leshan Buddha Scenic Area (China). In: IUCN World Heritage Evaluations 1995, IUCN Evaluations of nominations of natural and mixed properties to the World Heritage List. [online] Gland, Switzerland: IUCN. Available at: https://whc.unesco.org/en/list/779/documents/ [Accessed 25 November 2020].
10
Jiang WJ, et al., (1996). Impact of tourism on ecological environment in Emei and conservation strategies. Environmental Sciences, 03, 48-51
11
Li, Zhen-Yu & Shi, Lei. (2007). Plants of Mount Emei.
12
Lu S, Xie K P, Li C H. (2013). Preliminary studies on the evaluation system of endangered wild officinal plants in Mount Emei[J]. Guihaia, 33(2), 229-235.
13
Ni, S.S., et al., (2016). Impact to tourism disturbance on soil and vegetation in Emei. China Agricultural Resources and Zoning, 37(03), 93-96.
14
People’s Republic of China. (1995). Nomination of Mt Emei and Leshan Giant Buddha as a World Heritage Site. Beijing, China: People’s Republic of China.
15
Priston N E C, McLennan M R., (2013). Managing humans, managing macaques: Human– macaque conflict in Asia and Africa. The macaque connection. Springer New York, pp 225-250.
16
UNEP-WCMC. (2011). Mt Emei Scenic Area, including Leshan Giant Buddha Scenic Area, China. UNEP-WCMC World Heritage Information Sheets. [online] Cambridge, UK: UNEP-WCMChttps://yichuans.github.io/datasheet/output/site/mount-emei… [Accessed 25 November 2020].
17
UNESCO. (1999). Report on the State of Conservation of Mount Emei, including the Leshan Buddha Scenic Area, China. State of Conservation Information System of the World Heritage Centre. [online] Paris, France: UNESCO World Heritage Centre. Available at: https://whc.unesco.org/en/list/779/documents/ [Accessed 23 February 2017].
18
UNESCO. (2000). Report on the State of Conservation of Mount Emei, including the Leshan Buddha Scenic Area, China. State of Conservation Information System of the World Heritage Centre. [online] Paris, France: UNESCO World Heritage Centre. Available at: https://whc.unesco.org/en/list/779/documents/ [Accessed 23 February 2017].
19
World Heritage Committee. (2012). Decision 36 COM 8E. Adoption of retrospective Statements of Outstanding Universal Value- Mount Emei Scenic Area, including Leshan Giant Buddha Scenic Area (China). [online] Paris, France: UNESCO. Available at: http://whc.unesco.org/en/decisions/4841 (Accessed 10 October 2019).
20
Yao, X., Hao, G., Ping, X., Hu, J., & Hao, J. (2018). Outstanding universal value of plant diversity and conservation in Emeishan World Heritage Site. Guangxi Zhiwu/Guihaia, 38(12), 1605-1613.
21
Zhu Y, Li N. (2013). Groping for stones to cross the river: Governing heritage in Emei. Cultural Heritage Politics in China. Springer New York, pp 51-71.
22
Zhu Y, Li N. (2013). Groping for stones to cross the river: Governing heritage in Emei. Cultural Heritage Politics in China. Springer New York, pp 51-71.

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