Biodiversity and
Conservation of Changbai Mt. Biosphere Reserve;
Current Status, Problems and
Perspectives
Institute of Geographic Science and Natural Resources,
Chinese Academy of Sciences, Beijing 100101, China
Changbai Mountain Biosphere Reserve located in N.E. of China
is one of the biggest reserves in China and is very rich in biodiversity. For
many reasons resulted from the social and economical factors, there are serious
problems on biodiversity conservation in this area now. The current status of
biodiversity, the problems on biodiversity conservation and the strategy
dealing with research and management in this reserve are presented in this
paper.
1. Introduction
Changbai Mountain Biosphere Reserve is located in N.E.China, rest-ing between 41 41 49 -42 25 18 N. and 127 42 55-128 16 48 E. It was established in 1960 and was nominated as a biosphere reserve in 1979. Its size is 190,582 ha, in which is a core area of 133,841 ha and buffer zone of 83,394 ha. There are no villages within the core area (see Fig.1).
The highest peak in the Changbai ranges is Baitou Mountain, a
magnificent dormant volcano dating back geologically to the second swell of
Neocathaysian. Reflecting a long history of volcanic activity, today Baitou
Provides a model of a volcanic cone, titled lava plateau and lava tableland.
Many small volcanic islands can be found in this plateau and tableland, whose
gradient diminishes as it reaches lower elevations.
On the north
and west side of the Reserve, the land surface is smooth, while it undulates on
the south and southwest region. Due to organic movements and fluvial
activities, many gorges are formed in the area. The overall elevation of the
Changbai Reserve ranges from 720 at its nadir to Baiyun Peak¡¯s 2,691 m summit,
the tallest in Northeast China. From the heights of Baiyun and Wangtian¡¯s peak,
radiating water systems have developed into the rivers of Toudaobaihe,
Erdaobaihe, Caozihe, Jingjiang and others, among which Redaobaihe is a major
fountainhead of the Second Songhuajiang River. Originating on the south slopes
of Baitou, the Yaiujiang is a border river between Korea and China.

Fig.1 Changbai Mountain
Biosphere Reserve (northern part)
Since the
Asiatic monsoon affects the reserve¡¯s temperate continental mountainous
climate, the seasons are characterized as dry and windy spring, short and rainy
summer, cool and foggy autumn, and long and cold winter. The mean annual
temperature range from 7.3 to 3.3, with July¡¯s mean spanning 8.7 to 19.3, and
January¡¯s -23.3 to -16.1. The lowest recorded temperature on Baiyon¡¯s peak is
-44. Precipitation measurements lie between 700 mm and 1,240 mm; annual
irradiant is 124.01 kcal per sq. cm; and the reserve remains frost free
anywhere from 60 to 123 days.
In 1961, the
Reserve established a management institution in the town of Erdaobaihe, Antou
County, 277 km away by rail from the closest big city, Tonghua. North of
Erdaobaihe lies the cities of Dunhua and Antu, accessible to the convenient
highway infrastructure of Changbai. On Baitou Mountain, a thoroughfare rises to
Taiwen Peak, while the southern and western slopes are accessed by a good road
network.
Surrounding
the reserve are five local forestry units designed for timber production. There
are many conflicts between timber production and conservation along the border
of the reserve.
The local
administration is Changbai Mountain Natural Reserve Bureau, located in Tonghua
County, Jilin Province. The total staff of the Bureau is 244: 72 protection
workers, 28 professional workers, 12 construction workers and 132 support
workers. In order to improve understanding and management of natural resources
in this area, Changbai Mountain Forest Ecosystem Research Station, sponsored by
the Institute of Applied ecology, Chinese Academy of Sciences, was founded in
1979. Since then, an integrated long-term ecological research project
¡°Structure, Function and Productivity of Forest Ecosystems in Changbai
Mountain¡± has been operated. Up to now, about 100 scientists from eleven
institutions have been involved in this project, and about 200 scientific
papers have been published. This station was nominated as an international
station by Chinese Academy of Sciences in 1989, and the project as a
international pilot project by the Headquarters of MAB in Paris. Thorough joint
efforts of scientists, Changbai Mountain Biosphere Reserve has become an
important research center of biodiviersity conservation and management of
natural resources in China.
2. Biodiversity resources
Complex
landscape types, climate variations, and favorable water and temperature
conditions divide the Reserve¡¯s abundant species of vegetation into distinct
attitudinal zonations. As such, Changbai is regarded as Northeast China¡¯s
natural treasure house of biological resources.
Broad-leaved
species/Korean pine forest is the zonal vegetation in this area, called as
¡°Changbai Flora¡±, with some elements of South Okhotsk and Polar Flora. From the
reserve¡¯s lowest to its highest points, the vegetation can be divided into four
attitudinal zones (see Fig.2):
Below 1,100 m:
Broad-leaved species/Korea pine forest
mainly consisting of Pinus koraiensis,
Fraxinus mandshurica, Tilia amurensis,
Tilia mongolica, Juglans manshurica,
Phyllodendron amurense etc..
Between 1,100 and 1,700 m: Coniferous forest mainly consisting of
Picea jezoensis var. komarovii, Pinus
koraiensis, Abies
holophylla, A. nephro-
lepis etc..
Between 1,700 and 2,000 m: Subalpine ermanii birch forest mainly
consisting of Betula ermanii

Fig.2 Altitudinal zonation
of vegetation on north slope of Changbai Mountain
Above 2,000 m:
Alpine tundra mainly consisting of
Rhododendron
confertissimum, R.
redowskianum, R. aureum, Vaccinium
vitis-idaea, etc.
As to
nonzonal vegetation types:
the forest of
Larix olgensis, Pinus sylvestris var. sylverstriformis.
According to
statistics, about 2,400 species of plants, including 1,500 vascular species,
can be found here. Of the seventeen (17) listed as Nationally Protected, the Panax
ginseng C.A.Mey is on the first level list, while the second level is
represented by Malus komarovii (Sarg.) Rehd., Ophioglossum thermale
Kom., Oplopanax elatus Nakai and Phyllitis japonica Kom.
The third level encompasses Astragalus membranaceus, Boschniakia rossica,
Salix macrolepis, Chosenia arbutifolia, Fraxinus mandshurica, Fritillaria
ussuriensis, Gastrodia elata, Glycine soja, Juglans mandshurica, Phillodendron
amurense, Pinus sylvestris var. sylvestriformis, Salix tschanbaishanica and
Thuja koraiensis.
The fauna of
the Changbai Mountain Biosphere Reserve belongs to the Changbaishan subregion,
Northeast Region, Palaearctic Realm. However, there still exist some remnants
of the North China Region, Palaearctic Realm as well as from the Oriental Group
and some cosmopolitans.
Vertebrates
in the area include nine aquatic species, nine amphibian, ten reptilian, 260
avian, and 51 mammalian, while more than 1,000 species of insects are
represented. Animals currently listed under the national protection system
number 53, eight in the first level and forty-five in the second. The Martes
zibellina, Panthera pardus, Panthera tigris longipilis, Cervus nippon, Cioconia
nigra, Mergus squamatus, Aquila chrysaetos, and Aquila heliaca comprise
the first level group. Significant species among the forty-five second level
protected animal species are the Cuon alpinus, Setenarctos
thibetanus, Ursus arctos, Lutra lutra, Felis lynx, Moschus moschiferus, Cervus
elaphus, Naemonrhedus goral, Cygnus cygnus, Aix galericulata, Lyrurus tetrix,
Tetrastes bonasia, Crus grus, Anthropoides virgo, Pernis ptilorhyncus, Aegypius
monachus, Pandion holiaetus, Falco peregrinus, Fako subbuteo, Otus scops, Bubo
sp., and Luehdorfia puziloi.
3. Problems of conserving biodiversity
3.1 Baseline
of biodiversity in Changbai Mountain Biosphere Reserve is not very clear yet.
According to the definition of biodiversity, it contains all of the life forms
presented in levels of landscape, ecosystem, species and genes. Through
continuous efforts in the last decades, although great achievements have been
obtained, there is still a long way to go for getting clear picture about the
baseline of this biodiversity in this reserve.
3.2 Damages of
human activities to biodiversity, such as hunting animals and collecting
economic and medical plants, are very serious. Because of these continuous
damages, tiger and Panax ginseng are nearly extinct in the reserve, and many
others have already become endangered species. The most important reasons
causing these damages are local people¡¯s low income and poor education.
3.3 Island
effect. Because large amounts of forest which have been felled for timber
production in the surrounding area, and much habitat is already lost in the
surrounding area, many animals and plants in the reserve are becoming
endangered and rare. This had caused the reserve to become a shrinking habitat
¡®island¡¯ in an ¡®ocean¡¯ of transformed landscape.
3.4 No
suitable design of reserve management, based on scientific research. There was
a design, which was finished by officers who knew very little about scientific
principle of reserve management. As a consequence, the current design of
reserve management is not acceptable. For example, very little of the most
valuable forest type ¡°virgin broad-leaved species/Korean pine forest¡± is
included in the core area, many facilities for tourists like hotels and
training base of ski are put in the most sensitive part of the core area etc.
3.5 Lack of professional personnel and
chances available for the reserve managers to improve their knowledge on
conservation.
3.6 No enough
and continually provided budget for the reserve management. So it is impossible
for managers to build or improve the facilities like the information center,
booklets, signs, maps and guide survey etc. in the reserve, which are very
important for the public education.
4. Strategy
The strategy
dealing with solving the problems of conserving biodiversity in Changbai Mt. BR
is related with the socioeconomic and scientific aspects.
4.1
Socioeconomic aspects
4.1.1
Population control. The implementation of population control policy has been
very successful in the last tow decades in China. But due to the extremely
large base number of the total population, the increase is still the most
serious issue. There are many villages, town and cities in the surrounding area
of Changbai Mountain Biosphere Reserve. Because the most important income of
many local people is from the harvesting and hunting of the natural resources,
population control is a key factor of improving biodiversity conservation in
this area.
4.1.2
Developing local economy and increasing the income of local people.
Another most
important reason for local people to damage the biodiversity is that they don¡¯t
have other kinds of sources of earning money. Therefore, developing local
economy and helping local people to get more income under the framework of
sustainable using of the natural resources also is a key factor for
biodiversity conservation.
4.1.3
Improving local education system.
Because of
the poor local education system, most of the local people know little about the
consequences of damaging biodiversity. Our suggestion is to pay more attention
to the education of the children and put the conservation and other ecological
knowledge in the text books in primary and high schools.
4.1.4
Provding enough and continuous financial assistance for reserve management.
4.1.5 Establishing
suitable environment policies at both national and provincial levels to
guarantee all of points mentioned above can be put into effect.
4.2
Scientific Aspects
In order to
meet the challenges of conserving biodiversity in Changbai Mt. BR and
surrounding area, the Changbai Mt. Forest Ecology Ecosystem Research Station
was founded in 1979 and sponsored by the Institute of Applied Ecology, Chinese
Academy of Sciences. Since then, about one hundred scientists from thirteen
institutions have been working on a long-term ecological research project
¡°Structure, Function and Dynamics of Forest Ecosystems in Changbai Mt.¡±. This
project has been divided into three phases. The aim in Phase One, from
1979-1982, was to survey the baseline of natural resources and conditions,
while Phase Two, from 1983-1986, was focused on the features of Korean Pine
forest and its management. Phase Three runs from 1987. Its main aims are, on
the one hand, to conduct further research on the basic features of the forest
ecosystems, and most importantly on the other hand, to synthesize and analyze
the data already collected, and to obtain some reliable results which can be
used to improve reserve management and forest ecosystems research for
sustainable development. About 150 papers have been published up to now, and
some of the results have already been widely applied. The project joined the
MAB Program in 1980, and became an International Pilot Project of MAB in 1989.
In recognition of its international significance, the Changbai Mt. Forest
Ecosystem Research Station was nominated as an International Research Station
by the Chinese Academy of Sciences in 1989. This station has already become a
major research center for biodiversity and management of temperate forest
ecosystem and reserve management in China.
As to
research projects operated in this station they can be classified as following
groups:
4.2.1 survey
of baseline on biodiversity and environment.
In first
three years (1979-1982), about 70 scientists concentrated on the survey of
baseline on animals, plants, microorganisms, meteorology, hydrology, soil etc.
Then a series of books and papers had been published. they have provided a base
for understanding biodiversity at species and ecosystem level.
4.2.2 Monitoring
changes of biodiversity and environment.
From 1980 to
1981, 7 permanent plots with size 1 ha or 0.25 ha, and many small plots with 1m2
for ground cover and 4 or 9 m2 for undergrowth in every plot in
different types of vegetation were set along vertical zonations. Since then,
the traditional methods recording and monitoring species changes have been
used.
As to
animals, sampling and other kinds of approaches have been used for monitoring
the changes of species density. At the same time, we set 6 meteorological
stations in plots and on opened area to collect the meteorological data
continuously.
We have
started to establish GIS of Changbai Mt. BR since 1988. Through this system,
all of information on this reserve, including topography, vegetation, land use,
hydrological maps and potential distribution maps of several endangered both
plant and animal species have been stored in computers through ARC/INFO
software. We have also developed a approach to link models with GIS to predict
the landscape changes of Korean pine/broad-leaved species forest.
4.2.3
Reintroducing endangered species.
Panax ginsen
C.A.M. is an important medical plant, which has widely been used by Chinese for
a long time. Because this species have been heavily collected. it has already
became an endangered species and almost disappeared. In 189, we developed a
research project to reintroduce it into Korean pine/broad-leafed species
forest. Through experiments, we are going to examine ecological conditions
essential for Genseng¡¯s growth and grow them under canopy of natural woods.
4.2.4
Breeding of endangered animals.
An endangered animal Roe Deer has been chose as example for breeding,
and then reintroduced into natural forest to increase its population. Changbai
Mt. BR and surrounding area will be one of major sites to develop research
projects on biodiversity, global change and sustainable development of forestry
in China. The Institute of Applied Ecology is going to play key role to carry
on these projects. The fund is available already for next five years. It can be
predicted that the conservation of biodiversity in this region will be improved
soon through joint and continuous efforts of scientists, administrators and
local people.
Referneces
Management Bureau of National Changbai Mt. Natural Reserve,1988, Introduction to Changbai Mt. Natural Reserve.
Zhao Shidong and Zhao Guang. 1989. Management of Changbai Mountain Biosphere Reserve: Current situation, problem and perspectives. Nature and Resources: 27-30.