Biodiversity Conservation in Xishuangbanna, China: Diversity Analysis of Traditional Knowledge Related to Biodiversity and Conservation Progress and Achievement Evaluation
Abstract
:1. Introduction
2. Material and Methods
2.1. Study Area
2.2. Study Methods
2.2.1. Literature Research
2.2.2. Survey and Cataloging
2.2.3. Traditional Knowledge Diversity Analysis
3. Results and Discussion
3.1. Protection of Traditional Knowledge Related to Biodiversity in Xishuangbanna
3.1.1. Survey and Cataloging of Traditional Knowledge Related to Biodiversity of the Jinuo People
3.1.2. Diversity Analysis of Traditional Knowledge Related to Biodiversity of the Jinuo People
3.2. Progress in Biodiversity Conservation in Xishuangbanna
3.2.1. In Situ Conservation in Xishuangbanna
3.2.2. Ex Situ Conservation in Xishuangbanna
3.3. Achievements in Biodiversity Conservation in Xishuangbanna
3.3.1. Ecosystem and National Key Protected Wildlife Protection
3.3.2. Increased Public Awareness of Biodiversity Conservation
4. Challenges
- (1)
- The loss of traditional knowledge related to biodiversity is serious. In the long-term production and living practices, ethnic groups have accumulated a large amount of traditional knowledge and technology related to the utilization of biological resources. The traditional knowledge involves many aspects such as agriculture, forestry, medicine, diet, the literature and art. Under the imperfect intellectual property system, a lot of traditional knowledge is lost to foreign countries and used for business or patent applications, but the holders of traditional knowledge do not enjoy the benefits [67]. As production and lifestyle changes, traditional knowledge also faces the risk of disappearing. The Jinuo people living in Jinuo Mountain have developed a slash-and-burn livelihood that is compatible with the environment. The slash-and-burn cultivation contains rich ecological wisdom and embodies the rational development and utilization of land [68]. With the development of the times, this way of livelihood has been abandoned and the related traditional knowledge such as agricultural calendars and sacrificial rituals have also disappeared. How to protect and inherit traditional knowledge and promote fair and equitable sharing of benefits arising from the utilization of traditional knowledge is a focus that the Xishuangbanna government should pay attention to in the process of protecting biological diversity.
- (2)
- The protection of species is insufficient and there is a protection gap in Xishuangbanna. At present, relevant government departments pay more attention to the protection of rare and endangered species with economic value, social value and scientific research value, while not paying enough attention to the protection of other species, resulting in certain deviations in the scope of protection [69]. Xishuangbanna has established a relatively complete protected area system, but the protection scope of the designated protected areas is limited. These protected areas are separated by villages, farmland, roads, etc., and lack of connectivity, which hinders species exchange. Due to population growth and rapid economic development, forest land has been encroached and natural forest area has been reduced, resulting in serious fragmentation of wild animal habitats and the risk of population degradation and extinction, further leading to the loss of biodiversity.
- (3)
- Land use changes dramatically. Land is the carrier of biodiversity, and the change in land use will lead to the loss of biodiversity and the decline of ecological service functions. Rational use of land is an important means to protect biodiversity. Due to population pressure and rapid socioeconomic development, land use in Xishuangbanna has undergone significant changes in recent years, mainly manifested in the sharp decrease in the area of natural forests, the fragmentation of tropical rainforests, and the continuous expansion of the areas of economic plantations such as rubber plantations and tea gardens. In the ten years from 2000 to 2010, rubber prices tripled, and the rubber planting area in Xishuangbanna increased by 1374.1 km2. The expanded rubber forests were mainly converted from forestland. As a result, there are a large number of unsuitable planting areas with “super altitude, super latitude and super slope”, resulting in negative ecological effects such as water shortage, soil quality decline and biodiversity decrease in some areas. Due to the slowdown in rubber demand and the reduction in available land area after 2010, the rubber area of the whole state only increased by 97.1 km2 in 2018 [70,71]. In addition, as Xishuangbanna Pu er tea becomes more and more accepted by the public, the area of Xishuangbanna tea gardens increased dramatically between 2011 and 2016. The soaring price of tea makes tea farmers in high-altitude areas see business opportunities and they even cut down forests to grow tea. Unreasonable deforestation for tea planting changes the original habitat environment, and also changes the traditional planting methods of tea trees and the ecosystem of tea gardens [72].
5. Recommendations
- (1)
- Protect the traditional culture of ethnic minorities, conduct surveys and catalogs of traditional knowledge related to biodiversity, and promote benefit sharing. Taking the Jinuo people as an example, through investigation and quantitative analysis, it has been found that the Jinuo people have rich traditional knowledge related to biodiversity, especially traditional culture related to biodiversity and traditional knowledge related to agricultural genetic resources. For thousands of years, this traditional knowledge has played an important role in the protection of natural sacred sites, agricultural germplasm resources and religious plants, and has had a profound impact on the long-term maintenance of biodiversity habitats. Therefore, it is necessary to carry out a background survey of traditional knowledge, not only for the Jinuo people, but also for other ethnic groups. It also conducts registrations and document cataloging, and establishes online databases to timeously understand and update the preservation status of traditional knowledge related to biological resources in ethnic minority areas. Meanwhile, a system of obtaining and benefit-sharing genetic resources and related traditional knowledge will be established in Xishuangbanna to provide a model for the utilization of biological resources in China and even the world.
- (2)
- Formulate local regulations for biodiversity protection in Xishuangbanna, strengthen the protection of wild animal and plant resources, and promote the improvement in the legal system for biodiversity protection. The legalization of biodiversity is the main path to mainstreaming biodiversity and is also a basic requirement for fulfilling the GBF. Xishuangbanna is one of the most biodiverse areas in China. In order to protect the local biological resources, the state government has formulated regulations on the management of nature reserves and the protection of forest resources. However, the scope of protection of these separate regulations is limited and the object of protection is relatively simple. Therefore, it is necessary to introduce a special law for biodiversity protection to make the scope of protection more comprehensive and make it possible to reverse biodiversity loss [73]. In terms of the protection of wild plants, we actively promote the protection of PSESP, the rescue of ancient tea trees, and the establishment of rare and endangered plant protection communities. In terms of the protection of wild animals, we should actively promote the preparatory work for the establishment of the Asian Elephant National Park, and continue to promote the cross-regional protection of the Asian elephant population and the construction of food source bases. At the same time, the construction of biological protection corridors is carried out to enhance the connectivity between nature reserves and prevent population isolation to achieve the purpose of biodiversity protection [74].
- (3)
- Rationally utilize land resources to promote biodiversity conservation and sustainable resource utilization. Land use change has been the direct driving factor with the largest negative impact on nature since 1970 and is one of the major threats to biodiversity loss. Target 1 of GBF emphasizes the protection of highly important areas for biodiversity (including ecosystems with high ecological integrity) through spatial planning so that biodiversity loss is close to zero before 2030 [75]. In order to fulfill Target 1, the state government will strengthen spatial planning, rationally utilize land, build single rubber plantations and tea gardens into environmentally friendly rubber gardens and ecological tea gardens, and pay attention to the improvement in land utilization rate and the overall protection of the ecosystem [76]. Meanwhile, ecological protection red lines and cultivated land protection red lines must be strictly observed. The land use in the protected areas and ecological red lines is relatively stable, but the land use in the edge areas of the red lines changes rapidly, so attention should be paid to it and rational planning should be carried out.
6. Conclusions
Author Contributions
Funding
Institutional Review Board Statement
Data Availability Statement
Acknowledgments
Conflicts of Interest
References
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Category | Subcategory | Number of Species under National First-Grade Protection | Number of Species under National Second-Grade Protection |
---|---|---|---|
Wild plants | Gymnosperm | 4 | 5 |
Angiosperm | 6 | 141 | |
Lycophyte and Fern | - | 17 | |
Bryophyte | - | 1 | |
Total | 10 | 164 | |
Wild animals | Bird | 15 | 117 |
Mammal | 21 | 17 | |
Amphibian | - | 1 | |
Reptile | 3 | 5 | |
Total | 39 | 140 |
Major Category | Subcategory | Number | Proportion |
---|---|---|---|
Traditional knowledge related to breeding of agricultural genetic resources | TK related to breeding of crop genetic resources | 36 | 21.43% |
TK related to breeding of domestic animal genetic resources | 6 | 3.57% | |
TK related to breeding of aquatic organism genetic resources | 5 | 2.98% | |
TK related to breeding of forest genetic resources | 20 | 11.90% | |
TK related to breeding ornamental plant genetic resources | 22 | 13.10% | |
TK related to wild plant genetic resources conservation | 49 | 29.17% | |
TK related to terrestrial wild animal genetic resources | 20 | 11.90% | |
TK related to breeding of microbial genetic resources | 10 | 5.95% | |
Traditional knowledge related to medicine | TK on the introduction, domestication, cultivation and conservation of traditional medicinal biological resources | 223 | 92.53% |
Traditional medicine theories | 5 | 2.07% | |
Traditional therapies | 3 | 1.24% | |
Traditional processing technology of medicinal materials | 3 | 1.24% | |
Traditional prescriptions | 5 | 2.07% | |
TK of health care and disease prevention | 2 | 0.82% | |
Traditional technologies related to sustainable use of biological resources | Traditional agricultural production technologies | 8 | 29.63% |
Traditional printing and dyeing and textile technologies | 5 | 18.52% | |
Traditional food processing technologies | 8 | 29.63% | |
Traditional planning, design and construction techniques | 3 | 11.11% | |
Other traditional technologies | 3 | 11.11% | |
Traditional culture related to biodiversity | Religious beliefs and ecological ethics | 6 | 13.33% |
Traditional festivals | 13 | 28.89% | |
Customary law | 4 | 8.89% | |
The traditional literature and art | 14 | 31.11% | |
Traditional food culture | 2 | 4.44% | |
Other traditional cultures | 6 | 13.33% | |
Traditional knowledge of biogeographical indication products | TK related to food indication products | 3 | 33.33% |
TK related to craft-marked products | 5 | 55.56% | |
TK related to other geographical indication products | 1 | 11.11% |
Name | Total Number | Number of Subcategories | Diversity Index |
---|---|---|---|
Traditional knowledge related to breeding of agricultural genetic resources | 168 | 8 | DTK1 = 0.82 |
Traditional knowledge related to medicine | 241 | 6 | DTK2 = 0.14 |
Traditional technologies related to sustainable use of biological resources | 27 | 5 | DTK3 = 0.79 |
Traditional culture related to biodiversity | 45 | 6 | DTK4 = 0.86 |
Traditional knowledge of biogeographical indication products | 9 | 3 | DTK5 = 0.64 |
No. | Name | Main Protection Type | Administrative Region | Main Protected Object | Area (hm2) |
---|---|---|---|---|---|
1 | Xishuangbanna National Nature Reserve | Forest ecosystem | Jinghong City, Mengla County, Menghai County | Forest ecosystems such as tropical rain forest and tropical monsoon forest, and rare wild animals and plants such as Asian elephants and Parashorea chinensis | 242,510.0 |
2 | Xishuangbanna Naban River Watershed National Nature Reserve | Forest ecosystem | Jinghong City, Menghai County | Tropical forest ecosystems dominated by tropical rain forest and tropical seasonal rain forest, and rare wild animals and plants | 26,600.0 |
3 | Xishuangbanna Lancang-Mekong River Watershed State Nature Reserve | Wild animal | Mongla County | Fish resources such as soft-shelled turtle and gyrinocheilus aymonieri | 67.0 |
4 | Xishuangbanna Luosuo River State Nature Reserve | Wild animal | Mongla County | Aquatic wildlife and their habitats | 600.0 |
5 | Xishuangbanna Bulong State Nature Reserve | Forest ecosystem | Jinghong City, Menghai County | Forest ecosystems dominated by montane rain forest and rare wildlife resources | 35,485.0 |
6 | Xishuangbanna Yiwu State Nature Reserve | Forest ecosystem | Mongla County | Ancient tea tree resources and national key protected wildlife resources | 33,369.9 |
7 | Jinghong County Nature Reserve | Forest ecosystem | Jinghong City | Unique forest ecosystem and wild animals and plants under state key protection | 47,258.0 |
8 | Menghai County Nature Reserve | Forest ecosystem | Menghai County | Forest ecosystems and rare and endangered wild animal and plant resources | 28,315.7 |
9 | Mengla County Lancang River Green Triangle County Nature Reserve | Forest ecosystem | Mongla County | Forest ecosystems dominated by mountain rain forest, and rare and endangered wildlife resources | 14,752.0 |
Plant Group | Family | Chinese Name | Scientific Name |
---|---|---|---|
Gymnosperm | Cycadaceae | Bichisutie篦齿苏铁 | Cycas pectinata |
Cycadaceae | Changyesutie长叶苏铁 | Cycas dolichophylla | |
Cycadaceae | Danyusutie单羽苏铁 | Cycas simplicipinna | |
Taxaceae | Xumihongdoushan须弥红豆杉 | Taxus wallichiana | |
Angiosperm | Dipterocarpaceae | Wangtianshu望天树 | Parashorea chinensis |
Dipterocarpaceae | Guangxiqingmei广西青梅 | Vatica guangxiensis | |
Combretaceae | Echiteng萼翅藤 | Getonia floribunda | |
Nyssaceae | Yunnanlanguoshu云南蓝果树 | Nyssa yunnanensis | |
Orchidaceae | Piaodaidoulan飘带兜兰 | Paphiopedilum parishii | |
Orchidaceae | Zimaodoulan紫毛兜兰 | Paphiopedilum villosum |
Animal Groups | Family | Chinese Name | Scientific Name | Endemism |
---|---|---|---|---|
Birds | Phasianidae | Heijingchangweizhi黑颈长尾雉 | Syrmaticus humiae | — |
Phasianidae | Huikongquezhi 灰孔雀雉 | Polyplectron bicalcaratum | Endemic to Yunnan | |
Phasianidae | Lukongque绿孔雀 | Pavo muticus | — | |
Columbidae | Xiaojuanjiu小鹃鸠 | Macropygia ruficeps | Endemic to Yunnan | |
Gruidae | Chijinghe赤颈鹤 | Grus antigone | Endemic to Yunnan | |
Laridae | Heyanou河燕鸥 | Sterna aurantia | Endemic to Yunnan | |
Threskiornithidae | Caihuan彩鹮 | Plegadis falcinellus | — | |
Accipitridae | Heiwujiu黑兀鹫 | Sarcogyps calvus | Endemic to Yunnan | |
Accipitridae | Wudiao乌雕 | Clanga clanga | — | |
Bucerotidae | Baihouxiniao 白喉犀鸟 | Anorrhinus austeni | Endemic to Yunnan | |
Bucerotidae | Guanbanxiniao 冠斑犀鸟 | Anthracoceros albirostris | — | |
Bucerotidae | Shuangjiaoxiniao 双角犀鸟 | Buceros bicornis | — | |
Bucerotidae | Zongjingxiniao 棕颈犀鸟 | Aceros nipalensis | — | |
Leiothrichidae | Languanzaomei 蓝冠噪鹛 | Garrulax courtoisi | — | |
Emberizidae | Huangxiongwu 黄胸鹀 | Emberiza aureola | — | |
Reptiles | Testudinidae | Aojialugui 凹甲陆龟 | Manouria impressa | — |
Testudinidae | Miandianlugui 缅甸陆龟 | Indotestudo elongatea | — | |
Varanidae | Yuanbijuxi 圆鼻巨蜥 | Varanus salvator | — | |
Mammals | Lorisidae | Fenghou蜂猴 | Nycticebus bengalensis | — |
Cercopithecidae | Beitengweihou北豚尾猴 | Macaca leonina | Endemic to Yunnan | |
Cercopithecidae | Yinzhihuiyehou 印支灰叶猴 | Trachypithecus crepusculus | Endemic to Yunnan | |
Hylobatidae | Baijiachangbiyuan北白颊长臂猿 | Nomascus leucogenys | Endemic to Yunnan | |
Manidae | Chuanshanjia 穿山甲 | Manis pentadactyla | — | |
Canidae | Chai豺 | Cuon alpinus | — | |
Ursidae | Malaixiong马来熊 | Helarctos malayanus | — | |
Viverridae | Dabanlingmao大斑灵猫 | Viverra megaspila | — | |
Viverridae | Dalingmao大灵猫 | Viverra zibetha | — | |
Viverridae | Xiaolingmao 小灵猫 | Viverricula indica | — | |
Viverridae | Xiongli熊狸 | Arctictis binturong | — | |
Viverridae | Xiaochili小齿狸 | Arctogalidia trivirgata | Endemic to Yunnan | |
Viverridae | Gaolingmao缟灵猫 | Chrotogale owstoni | Endemic to Yunnan | |
Felidae | Conglinmao丛林猫 | Felis chaus | — | |
Felidae | Jinmao金猫 | Catopuma temminckii | — | |
Felidae | Yunbao云豹 | Neofelis nebulosa | — | |
Felidae | Bao豹 | Panthera pardus | — | |
Felidae | Hu虎 | Panthera tigris | — | |
Elephantidae | Yazhouxiang亚洲象 | Elephas maximus | Endemic to Yunnan | |
Tragulidae | Weishixilu威氏鼷鹿 | Tragulus williamsoni | Endemic to Yunnan | |
Bovidae | Yeniu 野牛 | Bos gaurus | — |
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Huang, Q.; Kuang, Y.; Zhou, H.; Li, X.; Yin, L. Biodiversity Conservation in Xishuangbanna, China: Diversity Analysis of Traditional Knowledge Related to Biodiversity and Conservation Progress and Achievement Evaluation. Diversity 2024, 16, 260. https://doi.org/10.3390/d16050260
Huang Q, Kuang Y, Zhou H, Li X, Yin L. Biodiversity Conservation in Xishuangbanna, China: Diversity Analysis of Traditional Knowledge Related to Biodiversity and Conservation Progress and Achievement Evaluation. Diversity. 2024; 16(5):260. https://doi.org/10.3390/d16050260
Chicago/Turabian StyleHuang, Qing, Yinzhi Kuang, Hao Zhou, Xunqi Li, and Lun Yin. 2024. "Biodiversity Conservation in Xishuangbanna, China: Diversity Analysis of Traditional Knowledge Related to Biodiversity and Conservation Progress and Achievement Evaluation" Diversity 16, no. 5: 260. https://doi.org/10.3390/d16050260
APA StyleHuang, Q., Kuang, Y., Zhou, H., Li, X., & Yin, L. (2024). Biodiversity Conservation in Xishuangbanna, China: Diversity Analysis of Traditional Knowledge Related to Biodiversity and Conservation Progress and Achievement Evaluation. Diversity, 16(5), 260. https://doi.org/10.3390/d16050260