Citation Detail: Peter Johan Schei, Wang Sung and Xie Yan. 2001. Third Annual Report of the BWG/CCICED. in: Conserving China's Biodiversity (II). China Environmental Science Press. Beijing. 31-50p.

 

BIODIVERSITY WORKING GROUP
(PHASE TWO)
THIRD REPORT (1999)

September 1999 Beijing

¡ï Introduction¡ï Membership of the Working Group ¡ï Terms of Reference ¡ïSummary of Activities of BWG in 1999.¡ï Five Year Work Plan of BWG ¡ï Publications of BWG ¡ïFunding of BWG Activities ¡ï
Major Recommendations of BWG

¡ï
Annex 1:CCICED Biodiversity Working Group17-22 August 1999 Workshop on Biodiversity onservation in Guangdong ProvinceRECOMMENDATIONS
¡ï
Annex 2: RECOMMENDATIONS TO THE TENTH FIVE-YEAR PLAN FROM THE CCICED IODIVERSITY WORKING GROUP

1. Introduction

In the 1997 report of the BWG, the working group presented a work plan for the five year period of the second phase of CCICED. We also reported on the shortage of funds felt by the working group and the need to identify additional funding to undertake some of the activities on the work plan. As anticipated in the 1998 report of the working group, the financial situation has been very weak, and many of the planned activities for the year were not done.

Nevertheless, the working group has achieved good progress in several areas and looks forward to an active programme for the rest of the second phase of CCICED. New sources of funding have been identified, and the group is confident that adequate funding will be realised to complete our 5-year programme.

2. Membership of the Working Group

Some changes were made to the membership of the Working Group. Dr. Peter Raven decided to step down from the group. Prof. John MacKinnon has decided to step down as Co-chair of the group, and Dr. Peter Schei has replaced him in the Co-chair position. John will remain a member of the working group. Mr. Jim Harkness, formerly of the Ford Foundation, has been appointed as the new WWF Representative in China and has replaced his predecessor Mr. Dan Viederman as a member of working group. These changes have been formally approved by the CCICED Secretariat. The Chinese membership of the group remains unchanged.

3. Terms of Reference

Terms of Reference of the Working Group remain unchanged. These are:

1. Create a fertile forum for exchange of ideas and approaches whereby China has access to wider experience beyond her borders and where managers can network with scientists and technicians to solve issues of policy, strategy and action in the field of Biodiversity Conservation.
2. Provide a mechanism whereby priority needs identified by scientists and technicians can be brought to the attention of relevant leaders and decision-makers through a multisectoral forum.
3. Provide an independent view of China's biodiversity and advise the government on areas of concern or sectoral failure.
4. Provide advice and assistance as needed in China's participation in international biodiversity conventions and programs to ensure that China gets maximal benefit from these mechanisms and also presents the most favourable international image of its considerable biodiversity achievements.
5. Initiate studies to demonstrate the contribution of biodiversity conservation to regional economic development in selected ecosystems in China and identify both factors that threaten such systems and appropriate remedies to ensure the sustainability of such benefits.

4. Summary of Activities of BWG in 1999.

Following the order of activities presented in the BWG workplan, the following progress was made during the current reporting year.

4.1 Biodiversity Working Group meetings
Two official meetings of BWG were held during the past year. The first one was a small Chinese Members Meeting, which held on 11 March, 1999 in Beijing. The recommendations to the State Council for the 10th Five Year Plan were drafted in the meeting. The second one was combined with the sectoral meeting in Guangdong in August 1999. The meeting completed the report on the field visits and sectoral meeting in Guangdong, finalised the annual report for CCICED for 1999, completed recommendations to the State Council for the 10th Five Year Plan, and laid out the plans for group activities for the year 2000.

4.2 Targeted sectoral meetings
The Biodiversity Working Group of the CCICED held a Workshop on Biodiversity Conservation in Guangdong Province from 17-22 August 1999. Guangdong Province has a high proportion of China's biodiversity as well as a large human population. In addition, Guangdong has experienced explosive economic growth and development during the last few decades.

As part of the workshop, groups were privileged to visit several nature reserves (Dinghushan Man & Biosphere Reserve, Nankunshan Nature Reserve and Neilingding-Futien National Nature Reserve) as well as the Xinyan Wildlife Market, Huadu Yingjili Peacock Farm, Nanhai Bird Farm, Wutongshan Nursery, Xiangjiang Wildlife Park and Shenzhen Wildlife Park. The people from these facilities were extremely gracious hosts and patiently answered all questions.

Two days of meetings with national, international and regional experts and authorities, covered many valuable presentations and resulted in lively and frank discussions. A full report was prepared and submitted to the provincial authorities and is appended as Annex 1 to this report.

The BWG were impressed by the great work that has been done by the provincial authorities in the field of biodiversity conservation and the ambitious plans for further strengthening the protected area system and measures to control the trade and use of wildlife.

The BWG team is concerned by the high levels of utilisation of wildlife and question the sustainability of this utilisation, and noticed some areas in protected areas management that could be improved. In addition the BWG were alarmed at reports that some species of carnivore and raptors may be extinct over wide areas of the province.

4.3 Illustrated guidelines for biodiversity conservation in economic development
Compilation of the illustrated book -- Guidelines for the Conservation of Biodiversity

The value of biodiversity, especially the indirect value from ecological services, has increasingly attracted the attention of the public and government. The heavy floods during the last two summers in China provided people with a harsh lesson in the cost of biodiversity loss. In order to ensure that the public as well as decision-makers realise the significance of biodiversity conservation and push the movement forward, we invited several scientists to compile the illustrated book, Guidelines for the Conservation of Biodiversity. The text and drawings for the book have been completed, but the book needs circulation for comments before going to press. It is hoped that the book can still be published by the end of this year.

4.4 Biodiversity Conservation Database
The checklist for birds has been reviewed by Dr. John MacKinnon; reptiles, by Prof. Zhao Ermi; and amphibians, by Prof. Fei Liang. The checklist for mammals was reviewed by Dr. Robert Hoffmann and Prof. Wang Sung, but more work needs to be done on the bats and rodents. The Biodiversity Conservation Database is now using the newest taxonomic classification for these four vertebrate groups.

More functions have been added into the China Species Information System (CSIS) to assist with the recall of data. Distribution information at the county level is still being entered based on faunistic works at both state and regional levels and from major journals in the fields of Zoology, Taxonomy, Mammalogy, and Biodiversity. Results of scientific surveys concerning species and distributions at regional levels or in reserves are also being quoted and entered. Locality records of mammal specimens in the National Museum of Natural History, USA, are also now entered in the system. By August, 1999, historical records at the county level have been expanded to 120,000. The distribution and synonym information for Insectivora have been carefully checked and corrected. Nearly 1,800 river names and GIS data have been combined into CSIS. The number of records for river distribution of fresh water fish is now more than 40,000. All this distribution information has been transferred into GIS points and lines, and can be shown on GIS maps with a background of China or of individual provinces. At the same time, a total number of about 1,300 photos of mammals, birds and reptiles has been scanned into their respective databases.

The local network was upgraded in early 1999 from Novell to Windows NT, a PII/333 server has replaced the 486 server, and two 586 PCs have replaced two 486 PCs. Five persons could operate CSIS at the same time. For the past six months work on the system has continued, but this has proceeded without any significant funding. Four persons have been retained to enter data, and they have worked every day for three months (January to March, 1999). This situation cannot continue without additional funding; however, there remains much work to accomplish. It is necessary to check and re-organise information in CSIS and to keep updating the system before it can provide the quality and accuracy of scientific information that we desire to enhance effective biodiversity conservation in China. Also, funding is needed to put all the information available in the system on an Internet site to facilitate access.

4.5 Catchment Forest Benefits Analysis, Hubei
A Final Report of the Xingshan Catchment Study has been prepared (in English) entitled "Evaluation of Economic Value for Forest Resources in Xingshan County, Hubei Province." The report is still being revised and edited prior to submission for publication in an international journal.

4.6 Ecosystem Emergy Analysis, Pingwu, Sichuan
Progress Report on the Evaluation of Biodiversity in Pingwu County, Sichuan Province

This study was reported in the 1998 report. BWG are still awaiting a final report from the project executants.

4.7 Grassland Regional Development Plan
Upper Yangtze Integrated Conservation and Development Project (Proposal and Executive Summary Available) To promote biodiversity conservation and sustainable development on the high alpine grasslands of the Qinghai-Xizang (Tibetan) plateau, the BWG has initiated a demonstration project in the upper Yangtze drainage. In conjunction with local governments and with a locally formed NGO (Upper Yangtze Organization -- Suojia Township's and Zhiduo County's first offically established and registered people's organization), the BWG plans to develop an integrated conservation and development plan to promote biodiversity conservation and sustainable use of the alpine grasslands (primarily for animal husbandry). The project calls for establishment of three protected areas for known populations of environmentally and culturally important species (snow leopards, black-necked cranes, and Tibetan antelope), and a demonstration area to investigate rangeland management strategies. The project will include participatory workshops, training, and capacity building as necessary to ensure that Suojia Township develops the experience to implement the project locally. The BWG will use results from this project to encourage similar activities for sustainable development and conservation throughout the alpine grassland ecosystem (an area encompassing 25% of China).

4.8 Economic studies of panda tourism
BWG collaborated in studies of the economic value of biodiversity undertaken and published by the Environmental Economics Working Group. This study showed that more aggressive development and upgrading of eco-tourism ¨C in particular, panda tourism in the Wolong Nature Reserve in Sichuan Province -- could result in very significant profits that would not only pay for the protection activities of the reserve but release funds for much more widespread conservation activity. Part of the funds available would be in the form of a biodiversity stamp built into the airport tax levied on people leaving China, as is successfully done in Costa Rica.

4.9 Field guides to the mammals and birds of China
One of the basic tasks of biodiversity conservation is to identify taxa/species and their occurrence (bio-inventory). Until now, taxonomy, distribution and status of many taxa in China, especially at the species level, still remain very unclear due to limitations on the progress of taxonomic study in China. The quality of databases on endangered species status and conservation relies on up-to-date and accurate taxonomy. One of the reasons why Chinese taxonomy is in a poor state is because for many years Chinese scientists had to work in isolation and could not compare materials with museum materials in neighbouring countries or even at other institutions in China. A high level of synonymy and outdated nomenclature has resulted.

BWG has started to compile a Field Guide to China's Mammals (English and Chinese Versions) based on the latest data and information together with the newest research on taxonomy and distribution (including new techniques such as DNA and karyotype studies). During the past year, manuscript materials on the species of Insectivora (hedgehogs, shrews, moles, etc.) and Pholidota (pangolins) have been created, including keys to orders and families of all Chinese mammals, keys to families and genera of insectivores, and keys to species of red-toothed shrews (Sorex, Soriculus), white-toothed shrews (Crocidura), moles (Talpidae) and hedgehogs (Erinaceidae). Distributional records for these species of insectivores in CSIS have been collected and geo-coded, and new distribution maps produced. Work is continuing on individual species accounts. It is hoped that the book will be an important reference for research, management and conservation of Chinese mammalian fauna, as well as to eco-tourism based on China's mammals.

Prof. John MacKinnon has meanwhile completed the Chinese bird field guide. This is now in press and will be published in early 2000 by Oxford University Press, UK. A grant has been secured by the BWG through IUCN to publish a Chinese language edition of this book. More than half the book has been translated, and this work will be completed by the end of the year. A publisher has been contacted, and it is hoped that the Chinese edition will be also released in the first half of 2000.

4.10 Wildlife trade survey at the border in Yunnan Province
Two reports, 'Preliminary survey on wildlife trans-frontier trade in Yunnan' and 'The status of live wildlife trade near the port areas in Yunnan', have been submitted by the wildlife trade monitoring team in Yunnan province.

Yunnan province borders Burma, Vietnam, and Laos. One of the main threats to wildlife protection in Yunnan is the wildlife trade, in both live animals and their products, across the borders. Our study was carried out from May 1998 to March 1999.

There are 17 international ports in Yunnan province: 5 primary ports -- Kunming, Ruili, Wangding, Hekou, Mengla (Mohan); and 12 secondary ports -- Longchuan, Yingjiang, Tengchong, Jinhong, Daluo, Simao, Menglian, Mengding, Nansan, Piema, Malipo and Jiping. So far the ports of Ruili, Wangding, Longchuan, Daluo, Hekou, Mengla (Mohan) have been surveyed.

Our investigation found that the trade is very easy between the borders of Yunnan and neighbouring countries. Even though there are laws to protect the wildlife, live wildlife and their products are still traded across the borders. Local people smuggle wildlife via rivers or across hills into China and such shipments are not checked or quarantined by customs.

Wildlife has long been used as food, as medicines, for pets and for raw materials. We surveyed the markets, wildlife collecting stations and centres of Yunnan Provincial Forestry Bureau, restaurants, drugstores and pet trade markets in each port. Wildlife and their products imported to Yunnan from neighbouring countries were identified. So far 134 species of wildlife have been found for sale including 54 species of birds belonging to 11 orders and 17 families; 33 species of mammals belonging to six orders and 16 families; and 47 species of reptiles belonging to three orders and 14 families.

The wildlife came from Burma, Laos and Vietnam (or indirectly from Thailand, Cambodia, Nepal, India and other adjacent countries) and were destined to be transported to several provinces in China, although some of them were for local consumption. The majority of consumption of the wildlife is for food. Many restaurants have been selling different kinds of wildlife as special dishes and medicinal liquor. Although selling wildlife food and liquor is prohibited by the government, it is very difficult to control. Wildlife dish names were listed in the menus of the restaurants in Hekou area, while in other port areas, even though they may not appear on menus, wildlife dishes can still be obtained. Many of these species are listed in the Appendices of the "Convention on International Trade in Endangered Species of Wild Fauna and Flora" (CITES), and the "Animals under State's Special Protection" (ASSP).

Yunnan Provincial Forestry Bureau adopted a new policy to set up wildlife refuges to deal with the huge mount of wildlife confiscated during illegal exports and imports. The ports of Ruili, Wanding and Longchuan have refuges to keep live animals imported from Burma. In the wildlife refuge in Ruili, people from the refuge can take over or purchase the wildlife, then the wildlife will be allocated and resold to other places.

Yunnan ports are centralised and act as transfer stations for wildlife transfrontier trade. There are two ways to smuggle wildlife across the port. One is through big domestic and foreign traders who import large quantities of wildlife and then transfer the shipments to other provinces through Yunnan; the other is public or underground selling centres that collect scattered wildlife goods which local people bring in illegally, and then resell them to other provinces.

Several recommendations are made to address this high level of illegal wildlife trade:

The trade studies in Yunnan augment the findings of earlier studies by BWG in Guangxi, Macao, Hong Kong, Guangdong and Shenzhen and the BWG field visits to markets in Hainan and Guangdong. The findings confirm that the scale of the problem is very great and that wildlife trade networks are complex, dynamic and reaching ever further beyond China¡¯s borders. Studies of trade routes in neighbouring countries undertaken by TRAFFIC and WWF also confirm these findings and the alarm that is felt by China¡¯s neighbours over the scale of this trade.

The fact that China must import wildlife from ever greater distances is evidence that the trade is unsustainable. The fact that protected species continue to cross the border points but do not emerge in the public markets indicates that there is a separate underground trade in protected wildlife.

Two issues are involved: firstly, the fate of the many wildlife species involved in this trade and secondly, the image and reputation of China as an environmentally responsible member of the global community. The second matter will have a much greater impact on China¡¯s development and international trade. It is important that the authorities get on top of this problem. BWG welcomes the idea of the Guangdong authorities to limit wildlife trade to only a small number of the many transborder trade gates, and hope that this can be extended also to the borders of Guangxi and Yunnan. BWG would also recommend a temporary moratorium of all transfrontier wildlife imports into the three provinces to allow stock-taking in the source countries whilst China puts in place the controls necessary to regulate such trade.

5. Five Year Work Plan of BWG

The proposed work plan remains unchanged, but completion of the activities listed will be dependent upon finding some way to continue funding the operation of the working group.

One priority new activity was proposed in our 1998 report. In view of the disastrous floods that affected China during 1998, we proposed to pull together the findings of previous work and experience on such flooding with international examples and prepare a special report for the Council entitled "The Use of Natural Vegetation in the Control of Floods".

China has again experienced a summer of disastrous floods, although the rainfall has not been outside normal patterns. The cause of the floods seems to be both that the vegetation sponge which holds back rainwater, improves soil penetration and uses water for transpiration has been reduced to critical levels, and that at the same time the siltation of lakes and riverbeds (also due largely to deforestation) has blocked the drainage system, preventing the swift dispersal of flood waters. The BWG is convinced that better protection of remaining original forests and better design of newly planted forests can have a major effect in reducing the damage from floods and in improving the flow of water in seasons of reduced rainfall. BWG have not had the funding needed to undertake the planned studies, literature surveys and experiments needed to make the planned report for the Council, but feel this is an urgent task and hope to undertake this project as soon as funding is secured.

Work Plan for 1999-2000

The following activities are therefore proposed for the coming year.

6. Publications of BWG

7. Funding of BWG Activities

The above-mentioned activities have received assistance from CCICED, MOF, NEPA and SOA, and also financial assistance from CIDA, WWF and IUCN/World Bank. As shadow ministers of BWG, Council members of CCICED, Claude Martin, and Maritta R. von Bieberstein Koch Wesser, have provided assistance to the work of BWG. We sincerely appreciate the assistance of these sources of support.

Proposals have been prepared and submitted to a variety of agencies including GEF, British Government, Italian Government and Norwegian Government to cover the basic operations and project work of the working group. Preliminary responses are optimistic.

8. Major Recommendations of BWG

A summary of specific recommendations for biodiversity conservation in Guangdong are given in the summary activities in section 4 above. A fuller draft of these recommendations, as presented to the provincial authorities is appended to this report as Annex 1.

The working group was asked to submit its major recommendations to CCICED for consideration for inclusion in the 10th Five Year Plan of China. The final draft of these recommendations is appended to this report in Annex 2.

In addition, BWG wish to repeat their first recommendations of last year, since the matter remains very urgent and the recommendations remains precisely relevant.

Recommendation 1:

Flood control can be achieved by taking better protection of natural vegetation in critical regions of China, particularly the catchments of the Yellow River and Yangtze River. Measures should include: Banning the logging of remaining natural forests, reducing pressure on existing forests by subsidising electricity and alternative fuel costs to local households; redirecting moneys from the beneficiaries of good water control to the individuals and agencies living and working in critical catchments responsible for ensuring good vegetation cover; reduce overgrazing on critical grassland areas; continue reforestation projects but with specific design for good "water sponge" rather than timber production (i.e. broadleaf or mixed forests rather than monocultures and too many conifers).

Recommendation 2:

It is important that China retains a good image internationally as a country of high environmental responsibility. Chinese citizens, companies and government agencies working overseas are endangering this image by embarking on environmentally damaging projects. We recommend that the government ensures that Chinese agencies embarking on potentially damaging projects have to undertake the same level of EIA for such projects as they would in China, even if the laws of the country concerned are weaker. The large-scale clearing of tropical rainforests to make way for a pulp mill in Sabah, Malaysia is a potentially embarrassing case in point.
Annex 1:

CCICED Biodiversity Working Group
17-22 August 1999

Workshop on Biodiversity Conservation in Guangdong Province
RECOMMENDATIONS

The Biodiversity Working Group of the CCICED held a Workshop on Biodiversity Conservation in Guangdong Province from 17-22 August 1999. Guangdong Province has a high proportion of China's biodiversity as well as a large human population. In addition, Guangdong has experienced explosive economic growth and development during the last few decades.

As part of the workshop, groups were privileged to visit several nature reserves (Dinghushan Man & Biosphere Reserve, Nankunshan Nature Reserve and Neilingding-Futien National Nature Reserve) as well as the Xinyan Wildlife Market, Huadu Yingjili Peacock Farm, Nanhai Bird Farm, Wutongshan Nursery, Xiangjiang Wildlife Park and Shenzhen Wildlife Park. The people from these facilities were extremely gracious hosts and patiently answered all questions.

The BWG were impressed by the great work that has been done by the provincial authorities in the field of biodiversity conservation and the ambitious plans for further strengthening the protected area system and measures to control the trade and use of wildlife.

The BWG team is concerned by the high levels of utilisation and question its sustainability, and noticed some areas in protected areas management that could be improved. In addition the BWG were alarmed at reports that some species of carnivore and raptors may be extinct over wide areas of the province.

This report contains our recommendations, arising from discussions held during the survey visits as well as discussions held during the plenary sessions of the workshop. The recommendations do not report on all the factual information collected during the field investigations, except where such facts are necessary to support recommendations made.

1. Trade in Wildlife

On the face of it, the trade in wildlife through the Xinyan Wildlife Market must be unsustainable. The estimated 200 individual shops each had several hundred to several thousand snakes of various species, totalling several hundred thousand individual snakes. This trade may represent a significant ecological impact on the surrounding countryside, and on the countries of Southeast Asia that are contributing to this trade. What, for example, is the impact on rodent prey populations? Without the snakes do the rodent populations increase and heavily impact rice and other economically important food crop harvests? The answer is that we simply do not know the ecological impacts of this trade, nor indeed whether the trade is sustainable.

Many of the wildlife species traded in Guangdong are threatened, but not protected by existing laws or conventions. On the other hand, some of the species listed in wildlife protection laws are common and widespread. In addition, the high levels of observed trade of non-listed species could jeopardise those species so rapidly that corrective conservation actions may not be able to keep pace with the declines. Further, trade in species that are not native to China also needs to be regulated here, because China is a significant importer of wildlife and it has a responsibility to ensure that its levels of consumption are not breaking regulations elsewhere, or having negative impacts on wild populations. It is disturbing that the trade appears to be increasing; for example, a new block of 60 or so shops has just been completed. These facts highlight the danger of over-exploitation.

Trade in other taxa that were seen, including turtles, lizards, mammals and birds, was difficult to assess as there are also other markets in the city specialising in these taxa. However, the conditions under which even the relatively limited numbers of these taxa were kept were unsatisfactory, with overheating an obvious problem, few animals having access to water, and untreated wounds common.

We therefore recommend that:

a) a comprehensive study of the volume and ecological impact of the trade be initiated as soon as possible, in collaboration with an appropriate local university and experts on fauna and flora, the various provincial authorities, the traditional medicine community, the wildlife traders, customs officers, and TRAFFIC (to build in the international component); this study of trade should include investigation of the import pathways for non-native species, as a basis for appropriate regulation and enforcement of trade agreements;
b) regular monitoring of trade be instituted to ensure that trade is carried out in a sustainable manner;
c) a professional Wildlife Traders Association be established that could agree and enforce standards of operation (and perhaps achieve economies of scale in negotiations with importers);
d) a simple guide to legal and illegal species be prepared for the wildlife traders, in Chinese, so that they will know which species are protected under which legislation;
e) an educational programme be designed on the basis of the results of the study under point a), aimed - over the long-term - at reducing public demand for wildlife;
f) protected species legislation be revised using the most up-to-date information available in consultation with relevant experts; and,
g) a ban on hunting or trade in species being unsustainably harvested be instituted and remain in force until such time as the trade or hunting is no longer a threat to the species' survival.

2. Involving the Private Sector in Biodiversity Activities

The phenomenal success in breeding peacocks (30,000 individuals, 2000 birds per month to the market), emus (10,000 produced per year from a single facility), canaries, and others indicate that the technology is available to breed virtually unlimited numbers of at least certain species in captivity, and that this technology is held primarily by the private sector. The private sector has a valuable relationship with the South China Agricultural University for conducting research on bird diseases, and they offer a range of other services to the Provincial Forest Department (breeding Green Peafowl -- a protected species -- and holding confiscated bears). In the new economic conditions, the private sector is going to become increasingly important as a contributor to biodiversity objectives. In the long term, the imbalance between supply and demand will be regulated by the market, but in the short term, government support may be required to enable the private sector to contribute to biodiversity objectives.

We therefore recommend that:
a) the private sector and government work together to determine the most supportive policy framework for current conditions. This framework should include clarified registration and permit procedures, certification procedures for captive bred/propagated individuals, developing international markets, and clear positions at CITES negotiations; and,
b) the private sector be systematic in recording and sharing the methodology for captive breeding and cultivation, in co-operation with government captive breeding efforts for species that are unlikely to show an economic return but which are critical for biodiversity conservation.

3. Wildlife Parks/Safari Parks

The growing popularity of Wildlife Parks and Safari Parks, usually as private commercial enterprises, demonstrates the great interest of the Chinese people in wildlife. Far more could be done, however, to ensure that they also learn about China's native biodiversity, how people relate to wildlife, what needs to be done to ensure that levels of exploitation are sustainable, and so forth. In addition, these parks should follow the example of their counterparts in Southeast Asia, Europe and North America in contributing to international ex situ and in situ conservation efforts.

We therefore recommend that:
a) wildlife parks/safari parks in Guangdong be active participants in the Chinese Association of Zoological Gardens including maintaining accurate records/studbooks and encouraging exchanges of information both within China and internationally, and agreeing to standards for management;
b) each Wildlife/Safari Park should develop a comprehensive educational plan, perhaps drawing on the experience of relevant non-governmental organisations and government agencies and highlighting in particular native Chinese wildlife; and,
c) wildlife parks/safari parks should consider exhibiting native fauna and flora on an 'ecoregion' theme to make such facilities into biodiversity parks.

4. Nature Reserves

The nature reserves visited provided some excellent examples of good reserve management. In the course of the meetings, with our colleagues at these facilities, we learned of the successful results of halting fishing in some coastal areas to increase fish stocks, plans to create 'ecological forests' and the activity to increase the network of reserves in the province, and plans to complete a provincial biodiversity inventory. In addition, our colleagues shared with us some of the difficulties they currently experience in reserve management, including the difficulty for the staff to be put into the position of having to generate their own funds for reserve operation. Staff from some reserves (eg. Nankunshan) desire to increase funding by generating hydroelectric power or engaging in ecotourism. Significant modifications in the management of these parks must be undertaken before either of these options should be entertained.

For the provincial nature reserve network we recommend that:

a) the central government invest a higher percentage of funds in support of these forest areas and the staff entrusted with their management, and consider increasing the percentage of incoming generated through entry fees in order to fund an increase in public education and research activities in reserves;
b) the reserves should establish regular monitoring schedules for the biodiversity in the reserve;
c) reserves should develop ecotourism materials including species lists and educational materials, that are developed from an ongoing inventory of biotic resources;
d) development of hydroelectric power within reserves should proceed with caution if at all. We encourage only micro-hydroelectric power to support the ecotourism infrastructure, and not large-scale building of dams, etc.; and,
e) As a matter of general policy, any large-scale potentially disruptive project in China's nature reserves should be evaluated by an independent environmental impact assessment (conducted by SEPA) to determine the costs and benefits of the project compared with potential loss of native biodiversity.

Additional recommendations for nature reserves are included in Annex 1.1. In addition, some specific information and recommendations for the individual reserves visited are mentioned below:

Dinghushan Biosphere Reserve

This NR provided an excellent example of a well-run nature reserve. We are particularly impressed by effort being made in public education, such as tags on trees indicating the importance of those trees, and the medicines and other human resources obtained from them. The reserve deserves praise for developing lists of species occurring in the reserve and publishing articles based on research carried out in the reserve. The present zoning of the reserve (core area, buffer zone and experimental zone) seems to be well drawn. The temple area in the buffer zone is heavily visited, but it is well maintained and attractive to visitors. The presence of shops and vendors (gifts, food, etc.) provides visitors with many opportunities to enjoy their visit to that area.

For Dinghushan Man & Biosphere Reserve we recommend that:

a) it would be worthwhile to expand educational efforts to reach both eco-tourists and cultural tourists. The Kadoorie Farm and Botanic Garden (Hong Kong) is experienced in producing various educational materials and could be helpful to the nature reserve in expanding this very important aspect of their public programs;
b) researchers on the staff should be encouraged to expend greater effort in developing more complete species list for animals and plants in the reserve. The existing lists, while a good beginning, are incomplete. The BWG should be able to provide lists of species of birds, mammals, etc. likely to be found in the reserve;
c) the present mounted specimens of birds and mammals at the reserve headquarters are mislabelled or unlabeled and in such poor condition that they ought to be replaced as a public display by good quality photographs;
d) the attraction of the natural portion of the buffer zone could be increased by establishing several "nature-walks" that could be located along existing pathways and could provide visitors educational opportunities of how the forest functions and what roles its component species play in the life of the forest;
e) these trails should also be kept as free of trash as possible; and,
f) providing some shops catering to eco-tourists might increase the number of visitors to that area of the buffer zone.

Nankunshan Nature Reserve
The forest in the general vicinity of Nankunshan Nature Reserve (NNR) is expansive and apparently healthy. Few signs were seen of any logging or man-caused disturbances. We viewed this area as one of high national importance - a real natural asset (especially considering its proximity to such a large urban area as Guangzhou). The actual area of NNR is considerably smaller than the total forest, but we were provided no maps to judge accurately the extent and location of the reserve. It was also unclear who has the ultimate responsibility for different aspects of management of NR and the surrounding forest - for planning, implementation of plans, funding, etc. This confusion was not only apparent to us, but also to those nominally responsible for administration of management of this forest. The NNR has much promise for biodiversity conservation - but we did not witness any concerted evidence that biodiversity conservation is being addressed directly in elements of park management. There are only three full time staff and none are involved in research. The relatively pristine state of the park at present is due more to a lack of funding than active management to protect the area.

For Nankunshan Nature Reserve we recommend that:
a) an understanding concerning the division of responsibilities for managing the reserve be clarified;
b) the reserve be expanded to encompass the forests of Nankunshan range. Such enlargement would not only result in greatly enhanced protection of the biota in these mountains, but would better protect the water resources of several rivers whose headwaters are in these mountains. The great importance of water in this densely inhabited part of Guangdong is obvious; and,
c) means should be found to begin an inventory of the biota of the Nankunshan. Since the staff of the reserve itself are inadequate to conduct such inventories, consideration should be given to identifying suitable specialists from elsewhere in the Province or region who might be able to assist the reserve staff.

Neilingding-Futien National Nature Reserve
This site is clearly important at a national level, being an extension of the Mai Po Reserve in Hong Kong. The reserve is well situated to be a National Nature Reserve because a major new highway offers an excellent boundary. The reserve also has considerable potential as an educational site, being the mangrove forest closest to Guangzhou and Hong Kong. In order to make it more valuable for education, greater investment will be required for management, including dealing with the difficult problem of tide-born trash. The on-going research on mangrove restoration is excellent, and should be continued and applied in other parts of the Pearl River estuary. The success of the reserve depends ultimately on solving the problem of land tenure with the local people currently occupying the Reserve area.

For Neilingdingfutien NNR, we therefore recommend that:
a) the government reach agreement with the local people regarding long-term tenure/ rights to sustainably exploit the resources of the site;
b) the Reserve seek recognition under the Convention on Wetlands of International Importance (Ramsar Convention), perhaps as an extension to Mai Po (which is already listed);
c) a belt of trees and shrubs be planted along the highway to buffer the site from the impacts of vehicle and pedestrian traffic;
d) the reserve capitalise on its potential as an educational site for the general public and include in its buffer zone functioning fish ponds that would not only maintain an important part of the culture of the local peoples, but could provide a practical example of sustainable use of resources; and,
e) avoid the introduction of exotic species in any restoration work on mangrove forests .

5. Benefits from Biodiversity for all Stakeholders

The involvement of the private sector and government in the sustainable use of biodiversity was obvious during our visits. However, it was unclear that people at the source of biodiversity, either local villagers or local governments, were receiving a fair share of the benefits from use of their biodiversity resources. Breeding limited numbers of endemic orchids or pheasants, for example, could earn a significant benefit for these people and help them to recognise that conservation and sustainable use have direct value to them. The quantities and species they deal with would be unlikely to compete with the commercial private sector or state enterprises.

We therefore recommend that:
a) transfer of technology and sharing of benefits derived from captive breeding/propagation of wildlife resources be implemented at all levels, in particular to local people in remote areas, as a means of helping them to earn some economic benefits from sustainable use of biodiversity; and,
b) trading companies should invest in small ventures run by villagers at the source of biodiversity, especially species that have specialised habitat or nutritional requirements that are not easily created in captivity.

6. A Comprehensive Provincial Approach to Biodiversity

As part of her commitment to the Convention on Biological Diversity (CBD), China has completed a National Biodiversity Action Plan. However, China is one of the megadiversity countries of the world and it is important to follow this national level Action Plan with a national strategy that would specify national policy on biodiversity. This should be implemented through planning at the provincial level to account for conditions specific to Guangdong, to define the roles for the various economic sectors, and to outline the major activities needed to implement the CBD at the provincial level. As a starting point, at the end of 1999, the Forest Department of Guangdong Province will have completed a provincial biodiversity survey.

We therefore recommend that:
a) the Province of Guangdong should prepare a Provincial Biodiversity Strategy and Action Plan, led by the State Planning Commission and with the active participation of the Provincial Forestry Department, the Provincial Environmental Protection Agency, provincial agricultural, fisheries, marine, tourism, science and technology, transport, energy, trade, education agencies, and the private sector. The strategy and action plan should address county and township issues as well. The Strategy and Action Plan would set out the major policy directions for the province, to ensure that any use of biological resources is sustainable, and that biodiversity is able to continue to play its critical role in the welfare of the people of Guangdong; and,
b) a means for providing adequate resources for implementation should be included in the Guangdong Biodiversity Strategy and Action Plan, drawing on a wide range of funding mechanisms (ranging from admission fees to special taxes to linkages to water resources).

7. Guangdong's Responsibility for Hainan:

Guangdong province retains a historical responsibility for biodiversity in Hainan province. Hainan lacks a university or any biological institutes to undertake its important biodiversity conservation programme.

We therefore recommend that:
Scientists from Guangdong should support the Hainan authorities, through helping train Hainan biologists and field managers and providing vital data and reference collections to Hainan. This is particularly important for marine areas as Hainan is quite unequipped to control the huge area of rich tropical seas, whose management is confused by overlapping international claims.

8. Need for higher levels of provincial investments in biodiversity:

Biodiversity is providing massive and valuable services to the province in the form of water catchment functions - providing a year-round supply of clean water, reducing flood impact, protecting soils, refreshing the atmosphere and nutrient cycling. The soil itself derives from natural ecosystems and their component organisms. These services create large economic gains to many sectors, including agriculture, hydropower, industry, and fisheries.

We therefore recommend that:
The benefits of investments in biodiversity are realised by the provincial authorities and that these economic gains are reinvested into vital protection operations so as to secure sustainability of these services and as a long-term insurance against natural disasters. Successful demonstration of the soundness of such investment would help lead the way for national biodiversity care.

Annex 1.1. Additional recommendations on protected areas

Coverage of the whole range biodiversity in a protected areas system At the species level, a large proportion of biodiversity includes invertebrates, lower plants, fungi etc. Generally diversity is higher in tropical forests - in Guangdong there is a large gradient with both latitude and altitude. Particular emphasis should thus be placed on the natural forests in the south (e.g. Gutien NR) and at lower elevations (e.g. Chebaling NNR, Heishiding NR).
 

Small forests, though of minor significance to mammals etc., may be important to invertebrates etc. E.g. feng shui woods, traditional sacred groves near villages, may be of great importance to conservation of smaller forest species.

  Wetlands should also be covered adequately in protected areas.
  Globally and regionally restricted species should be given adequate coverage and attention. Recommendations concerning these will arise from the current Kadoorie Farm & Botanic Garden survey. E.g. some reptiles and amphibians have highly restricted ranges and need adequate protection.
  Continuity of stream ecosystems is very important. Dams may prevent recolonisation of upper stream after seasonal spates etc. - dams should not be allowed in important streams in NRs.
mproving effectiveness of nature reserve staff

I A series of ten training manuals are being produced by SFA's Division of NRs, for different levels of nature reserve staff. This is a great step forward, but donors are still needed for training courses.

 

Staff need to receive salaries reliably

  Operating expenses should be guaranteed for NRs
 

Education staff need specific training.

  We support SFA's attempt to implement job descriptions for NR staff . Job duties often need to be clarified. E.g. if there are three staff, who is responsible for education?
 

If possible, auditing of expenditure should be improved.

  Expenditure allocated from central sources needs to be monitored, to ensure it has gone where it was allocated to.
  Training courses should involve some kind of assignment afterwards (as practised by WWF HK at Mai Po), before certificate is granted.
  A corps of training officers should be established, active in each biological region. Should include experts from outside Forestry Dept.
  Training courses should include biome-specific elements.
  Education of future Forestry officials very important. Should include strong biodiversity component. This should be coordinated by Chinese Academy of Forestry (for provincial officials), and the training department responsible for educating local officials.
Education All available visual aids (photos etc.) and information should be used, e.g. that available in Hong Kong.
  Education needs guides. Visitors should be charged for guided tours.
Protected species The new Red Data Books are a great improvement. But so far there is little emphasis on species whose habitats are restricted - more on species which are heavily traded. Needs amendment.
  All Red Data Book species should be also on the national protected list, or at least on the provincial list in those provinces where they are threatened.
  New Red Lists should incorporate all up-to-date information from reliable sources. Should ideally include data from the SFA's national surveys.
Improving effectiveness of protection Poisoning of streams is a big problem in South China. Those stream systems that have not been badly damaged, e.g. Qixingkeng in SW Guangdong, should be given high priority for protection. Elsewhere poisoning needs to be controlled in natural habitats. Need to encourage the reporting of incidents (liming etc.) to police, and the response of the police to these reports.
  The ban on hunting and fishing should be extended from nature reserves to all natural forests, including Forest Parks and Scenic Areas. Guns, nets etc. should be confiscated when encountered, and the owners should not be allowed to reclaim them (this occurs in some places).
  EIAs should be conducted on all projects impacting natural ecosystems.
Revenue from ecotourism Game fishing might be considered in future, using native species (e.g. Sinoperca perches). Only after depleted populations have recovered.
Investing in taxonomy etc. Should part of the budget of EIAs be invested in training specialists, on which they ultimately depend for their effectiveness?

Annex 2:

RECOMMENDATIONS TO THE TENTH FIVE-YEAR PLAN

FROM THE CCICED BIODIVERSITY WORKING GROUP

RECOMMENDATION 1: ESTABLISH A CROSS-SECTORAL COORDINATING BODY FOR BIODIVERSITY AT THE NATIONAL LEVEL

Objective: To establish a scientific authority for nation-wide biodiversity conservation and/or to empower existing conservation institutions with new and clear responsibilities and authority.

Background:

Measures Proposed:

RECOMMENDATION 2: ENABLE BIODIVERSITY TO EARN ECONOMIC RETURNS

Objective: The economics of biodiversity well understood by decision-makers and policies put in place to return profits from biodiversity investments to better manage biodiversity.

Background:

Measures Proposed:

RECOMMENDATION 3: REVISED LAWS AND IMPROVED ENFORCEMENT IN THE AREA OF BIODIVERSITY SHOULD BE PROMOTED

Objective: An adequate legal and logistic basis established for biodiversity conservation, environmental security, control of illegal trade, and gene bank development.

Background:

Measures Proposed:

RECOMMENDATION 4: UNDERTAKE A NEW BIODIVERSITY INVENTORY OF CHINA

Objective: Strengthen research on taxonomy and biodiversity information systems. Establish baseline biodiversity data for future monitoring programmes and revitalise and coordinate links between biodiversity museums and collections

Background:

Measures Proposed:

RECOMMENDATION 5: INCREASE PUBLIC EDUCATION ON THE IMPORTANCE OF BIODIVERSITY CONSERVATION

Objective: Through public education on biodiversity, enhance the awareness of the general public to improve biodiversity conservation

Background:

Measures Proposed:

RECOMMENDATION 6: MANAGE BIOLOGICAL RESOURCES TO ENSURE THAT USE, TRADE AND CONSUMPTION IS SUSTAINABLE

Objective: To stop unsustainable use of biodiversity

Background:

Measures Proposed:

RECOMMENDATION 7: EXTEND BIODIVERSITY STRATEGIES AND ACTION PLANS TO THE PROVINCIAL LEVEL

Objective: Implement the Convention on Biological Diversity at the provincial level

Background:

Measures Proposed: