Pasture Degradation and the Impact of Grazing in Qinghai (Tibet) · 2003. 10. 15. · The three...

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Population Growth Conversion to Agriculture Sedentarisation of Nomads Collectivization Non-Adapted Herd Structure Chinese Pasture Management Policies Fencing of Pastures Overgrazing/ Exploitation of Pastoral Land Increasing Demand for Fuel (Wood, Dung) Pasture Degradation Increasing Livestock Numbers Shortage of Pastoral Land Supplementary Sources of Income 0 100 200 300 400 500 600 700 800 1960 1965 1970 1975 1980 1985 1990 1995 2000 Year Precipitation (mm) -4,0 -3,0 -2,0 -1,0 0,0 1,0 2,0 3,0 4,0 Temperature (°C) Precipitation Temperature Trend (Precipitation) Trend (Temperature) Figure 4: The development of the population in the area of investigation displays a significant increase (1949-1985, 49.900 inhabitants in 2001) Year 1945 1950 1955 1960 1965 1970 1975 1980 1985 1990 Number 0 10000 20000 30000 40000 50000 Urban Population Rural Population Herders Total Population Year 1945 1950 1955 1960 1965 1970 1975 1980 1985 1995 2000 2005 Livestock numbers in 1000 0 500 1000 1500 2000 Total (adapted*) Large Herbivores Sheep Goats Methods The three pasture types examined in the area of investigation were Achnatherum splendens-, Kobresia/Stellera- and Orinus/ Stipa-dominated societies. Vegetation transect studies were conducted in twelve fenced pasture patches (four of each society) following the Braun-Blanquet approach. The data on the distribution of species under different levels of grazing collected in 144 vegetation surveys along transects has been analyzed with multivariate techniques. The classification was carried out using TWINSPAN (Two-Way INdicator SPecies ANalysis). For Ordination DCA (Detrended Correspondence Analysis) was applied (figure 5). Additionally, dung and soil samples were collected along the transects in order to get information on the distribution of livestock in the fenced pastures through the frequency of dung pellets and the concentrations of nitrate and phosphate. Literature: Qinghai History Editors Committee (2000): A History of Qinghai County. Xian (in Chinese) Acknowledgements: DAAD (German Academic Exchange Service) for financial support of the fieldwork, Northwest Institute of Plateau Biology (Xining, China), Prof. Dr. Georg Miehe & Dr. Sabine Miehe for cooperation Correspondence: [email protected], Katja Koch, Department of Geography, Philipps-Universität Marburg, Deutschhausstr. 10, 35037 Marburg, Germany Pasture Degradation and the Impact of Grazing in Qinghai (Tibet) A contribution to sustainable Rangeland Management Introduction The Chinese Province of Qinghai is one of the largest pastoral regions in China with extensive rangeland resources. In most regions livestock production is still the most important source of income for the local population. Political changes, socio-economic transition and the adjustment of the economy to market mechanisms caused transformations in live- Katja Koch Department of Geography, Biogeography Working Group, University of Marburg, Germany Northwest Institute of Plateau Biology, Chinese Academy of Sciences, Xining stock production in many parts of Tibet over the last decades. Interviews with herders in the study area (Xinghai County, Qinghai Province, see figure 2) showed that conditions for livestock production have deteriorated together with the state of pastures over the last decade (figure 1). In the present study the occurrence of pasture degradation was examined on three common pasture types of the Tibetan Plateau on the terraces of the Yellow River . Figure 1: The comparison between fenced and non-fenced areas shows the intensive utilization of pastures Figure 2: The locations of Qinghai Province (China) and the area of investigation (red square) 250 km C H I N A INDIA BHUTAN Xizang Qinghai Xinjiang Yunnan Sichuan Gansu Inner Mo. KYRGYZSTAN Conclusions Interviews with herders, vegetation surveys and evaluation of population, livestock and climate data indicate that a complex interaction of factors led to a decline in pasture productivity (figure 7). The changing political interventions as well as high stocking rates and climatic changes have had an impact on the condition of pastures today. Reduced herd sizes would probably be the only possibility to initiate rangeland regeneration. As a result, the income of herders might decrease dramatically. Therefore, rangeland improvement is only possible in cooperation with political decision makers. Number of Species Vegetation Cover Distance Amount of Dung Axis 1 Axis 2 Distance (m) 0 100 250 500 Results Significant population growth and subsequently increasing livestock numbers have had an effect on pasture productivity during the last 50 years (figures 3 and 4). The continual decline of livestock numbers since at least 1995 possibly indicates the limit of carrying capacity on pastures in the study area. It is still under discussion whether changing levels of temperature and precipitation have an impact on pasture productivity (figure 6). The study showed that severe degradation on pastures in Xinghai County occurs especially on Achnatherum splendens-dominated pastures, were stocking rates were above the carrying capacity. As the tussocks of Achnatherum are less eaten by livestock, pasture productivity is much lower than on patches dominated by Kobresia or Orinus. Because of the relative grazing resistance of Cyperaceae, Kobresia pastures are in a fairly stable condition. Orinus-dominated grazing grounds reach their carrying capacity in the investigated areas. An obvious gradient of decreasing degradation with increasing distance from the gate was identified in the more severely degraded pasture plots (figure 5). Figure 3: The development of livestock numbers show a marked increase (Xinghai County, 1949-2001, * weighted according to FAO). Figure 5: The DCA of 4 fenced Orinus/ Stipa- dominated pastures shows gradients mainly with distance from the gate in the number of species, plant cover and dung amount (n=48, Eigenvalue/ Post- hoc correlation Axis 1: 0,17/0,58; Axis 2: 0,08/ 0,17) Figure 6: The development of the annual average temperature and the annual amount of precipitation in Xinghai (1961-2001, China Meteorological Survey) Figure 7: Factors of pasture degradation in the study area

Transcript of Pasture Degradation and the Impact of Grazing in Qinghai (Tibet) · 2003. 10. 15. · The three...

Page 1: Pasture Degradation and the Impact of Grazing in Qinghai (Tibet) · 2003. 10. 15. · The three pasture types examined in the area of investigation were Achnatherum splendens-, Kobresia/Stellera-

PopulationGrowth

Conversion to Agriculture

Sedentarisationof Nomads

Collectivization Non-AdaptedHerd Structure

Chinese PastureManagement

Policies

Fencing of Pastures

Overgrazing/Exploitation of Pastoral Land

IncreasingDemand for Fuel

(Wood, Dung)

PastureDegradation

IncreasingLivestockNumbers

Shortage of Pastoral Land

SupplementarySources of

Income

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500

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1965

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Year

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-2,0

-1,0

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1,0

2,0

3,0

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pera

ture

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)

Precipitation Temperature

Trend (Precipitation) Trend (Temperature)

Figure 4: The development of the population in the area of investigation displays a significant increase (1949-1985, 49.900 inhabitants in 2001)

Year19

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stoc

k nu

mbe

rs in

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MethodsThe three pasture types examined in the area of investigation were Achnatherum splendens-, Kobresia/Stellera- and Orinus/ Stipa-dominated societies.Vegetation transect studies were conducted in twelve fenced pasture patches (four of each society) following the Braun-Blanquetapproach.The data on the distribution of species under different levels of grazing collected in 144 vegetation surveys along transects has been analyzed with multivariate techniques. The classification was carried out using TWINSPAN (Two-Way INdicator SPecies ANalysis). For Ordination DCA (Detrended Correspondence Analysis) was applied (figure 5).Additionally, dung and soil samples were collected along the transects in order to get information on the distribution of livestock in the fenced pastures through the frequency of dung pellets and the concentrations of nitrate and phosphate.

Literature: Qinghai History Editors Committee (2000): A History of Qinghai County. Xian (in Chinese)Acknowledgements: DAAD (German Academic Exchange Service) for financial support of the fieldwork, Northwest Institute of Plateau Biology (Xining, China), Prof. Dr. Georg Miehe & Dr. Sabine Miehe for cooperationCorrespondence: [email protected], Katja Koch, Department of Geography, Philipps-Universität Marburg, Deutschhausstr. 10, 35037 Marburg, Germany

Pasture Degradation and the Impact of Grazing in Qinghai (Tibet)

A contribution to sustainable Rangeland Management

IntroductionThe Chinese Province of Qinghai is one of the largest pastoral regions in China with extensive rangeland resources. In most regions livestock production is still the most important source of income for the local population.Political changes, socio-economic transition and the adjustment of the economy to market mechanisms caused transformations in live-

Katja KochDepartment of Geography, Biogeography Working Group, University of Marburg, Germany

Northwest Institute of Plateau Biology, Chinese Academy of Sciences, Xining

stock production in many parts of Tibet over the last decades. Interviews with herders in the study area (Xinghai County, Qinghai Province, see figure 2) showed that conditions for livestock production have deteriorated together with the state of pastures over the last decade (figure 1).In the present study the occurrence of pasture degradation was examined on three common pasture types of the Tibetan Plateau on the terraces of the Yellow River .

Figure 1: The comparison between fenced and non-fenced areas shows the intensive utilization of pastures

Figure 2: The locations of Qinghai Province (China) and the area of investigation (red square)

250 km

C H I N A

I N D I ABHUTAN

X i z a n g

Q i n g h a i

X i n j i a n g

Yu n n a n

S i c h u a n

G a n s u In n e r Mo .KYRGYZSTAN

ConclusionsInterviews with herders, vegetation surveys and evaluation of population, livestock and climate data indicate that a complex interaction of factors led to a decline in pasture productivity (figure 7). The changing political interventions as well as high stocking rates and climatic changes have had an impact on the condition of pastures today.Reduced herd sizes would probably be the only possibility to initiate rangeland regeneration. As a result, the income of herders might decrease dramatically.Therefore, rangeland improvement is only possible in cooperation with political decision makers.

Number of Species

Vegetation Cover

Distance

Amount of DungAxis 1

Axi

s 2 Distance (m)

0100250500

ResultsSignificant population growth and subsequently increasing livestock numbers have had an effect on pasture productivity during the last 50 years (figures 3 and 4). The continual decline of livestock numbers since at least 1995 possibly indicates the limit of carrying capacity on pastures in the study area. It is still under discussion whether changing levels of temperature and precipitation have an impact on pasture productivity (figure 6).The study showed that severe degradation on pastures in Xinghai County occurs especially on Achnatherum splendens-dominated pastures, were stocking rates were above the carrying capacity. As the tussocks of Achnatherum are less eaten by livestock, pasture productivity is much lower than on patches dominated by Kobresia or Orinus. Because of the relative grazing resistance of Cyperaceae, Kobresia pastures are in a fairly stable condition. Orinus-dominated grazing grounds reach their carrying capacity in the investigated areas.An obvious gradient of decreasing degradation with increasing distance from the gate was identified in the more severely degraded pasture plots (figure 5).

Figure 3: The development of livestock numbers show a marked increase (Xinghai County, 1949-2001, * weighted according to FAO). Figure 5: The DCA of 4 fenced Orinus/ Stipa- dominated pastures

shows gradients mainly with distance from the gate in the numberof species, plant cover and dung amount (n=48, Eigenvalue/ Post-hoc correlation Axis 1: 0,17/0,58; Axis 2: 0,08/ 0,17)

Figure 6: The development of the annual average temperature and the annual amount of precipitation in Xinghai (1961-2001, China Meteorological Survey)

Figure 7: Factors of pasture degradation in the study area