Priority Programme for China's Agenda 21Priority 6 - Environmental Pollution Control |
6-3 Water Pollution Control and Environmental Recovery of Lakes
6-3a Water Pollution Control and
Demonstration Project for Dianchi Lake
|
| Items | External Inputs |
||
| Research | 0.76 | 0.96 | |
| Design | 0.02 | 0.08 | |
| Instruments | 0.80 | 0.90 | |
| 1.44 | 2.88 | ||
| Total | 3.02 | 4.82 |
5. Benefits
This project is intended to restore water quality
in Dianchi Lake to the 1980s level and combat pollution of the lake environment.
At the same time, technical personnel will be trained. After project implementation,
it is expected that the considerable economic losses due to environmental
pollution and eutrophication can be reduced. Moreover, the project will
benefit human health and social stability. Its economic, social and environmental
benefits are multi-fold, and it will play an important role in the sustainable
economic development of lake basins in China.
Project Scope and Relationship to China's Agenda 21
This project seeks ways to control pollution and improve water quality and stimulate the economic development of the Baiyangdian Lake area. The specific objectives addressed by this project are to restore the eco-environment in Baiyangdian lake. It is based on programme area 14E of China's Agenda 21.
1. Background
Baiyangdian, the largest freshwater lake in North China, has always been known as the pearl of the region thanks to its rich local products, convenient transportation facilities, favourable geographical location, and scenic beauty. It connects the city of Baoding in the west and Tianjin in the east, and is in close proximity to Beijing and Shijiazhuang in the north and south, respectively. However, since the 1960s, it has suffered shrinkage of its water surface, drying up of its water source, increasingly serious water pollution resulting from urban industrial waste, leading to the constant drop of aquatic production, and finally to siltation and sedimentation of the lake. Until the 1980s, the area of Baiyangdian's water surface having a water quality ranking of Grade 4-5 had reached 28%, and the area falling into the category of light pollution (Grade 3) occupied 60%. The management, protection, exploitation and utilization of the lake directly affects the livelihood and economy of the local people, future regional development, and eco-environmental improvements in Beijing, Tianjin, and central Hebei.
The central government has repeatedly given instructions to work out a thorough solution to water pollution issues in Baiyangdian. Baiyangdian lake basin is a semi-closed interlocked ecosystem which is bounded by the piedmont of the Taihang Mountains in the west and by the low-lying wetland of Central Hebei Plain and the Bohai Sea in the east. Constrained and stimulated by factors related to the formation of land-water landscape morphology, this particular type of ecosystem can intercept, filter, migrate and purify certain incoming pollutants. These processes can either benefit pollution control or can generate natural resources with high economic value. What is more, the semi-closed drainage system, together with the complete territorial structure, can aid in engineering control. For these reasons, it is possible to make the lake basin a typical site for an on-the-spot investigation, and to conduct multiple water pollution control technical experiments, a complete set of engineering experiments, as well as a demonstration. By so doing, it is possible to provide much valuable technology for regional pollution control and sustainable economic development, and to make important contributions in exploring water pollution control theory and practice, much needed by developing countries.
There have been a lot of studies and analyses for years on the water pollution control of the Lake, as well as official inspections conducted by governmental leaders at various levels including the detailed investigations on environmental pollution in the area conducted in the 1970s by the Shijiazhuang Institute of Geography (Hebei Province) and the Institute of Zoology, CAS, the studies on the structure, function, environmental effects and prospects for future development of the ecosystem in the water-land interlocked area in the 1990s by the Institute of Geography, the Ecological Centre and the Institute of Zoology under CAS, etc.
Starting in the 1970s, 53 control and prevention projects were initiated by the provincial government of Hebei with the support of the central government. In the beginning of 1992, the two biggest paper-making mills were forced to suspend production or change their product line. Meanwhile, two industrial waste treatment plants with a capacity of 8000 tons/day were under construction to lay a sound foundation for water pollution control and prevention in Baiyangdian. However, further consideration is needed of urban centre treatment and the integrated utilization of resources crucial to Baiyangdian.
The main existing problems are that oxygen-consuming organic pollution and water body nutrient enrichment are increasing while the water quality continues to deteriorate, and effective means to cope with pollution induced by hard-to-degrade toxic organic materials in organisms with severe toxicity are still unavailable in Baiyangdian.
Even after the treatment plants under construction are put into operation, the treated water COD concentration would still fluctuate around 100 mg/l. Furthermore, of the total amount of municipal sewage directly entering Baiyangdian, only a small portion could receive treatment in the plants whereas the larger untreated portion be directly discharged into the lake.
Pollution caused by economic activities (daily life, tourism) and by irrational aquatic farming in Baiyangdian need to be handled. In addition, the relations between resource utilization, eco-environment management planning, pollution control/prevention and socio-economic development in the lake basin and surroundings are also waiting to be tackled.
2. Objectives
Long-term Objectives
Immediate Objectives
3. Activities
3.1 Develop and popularize new technologies for nonhazardous treatment and waste water treatment technologies for small-scale paper mills and printing and dyeing industries (Anxin County).
3.2 Establish demonstration projects for centralized land treatment and centralized resource use.
3.3 Establish renovation projects for central reservoir and oxidation pond.
3.4 Carry out demonstration studies:
3.5 Study water pollution control theory and methodology of water pollution related to geochemical ecological engineering.
These activities will be organized by the local government of Hebei Province.
The duration of this project will be three years.
4. Inputs
The total funding for this project is US $ 3.55 million, including US $1.81 million from domestic inputs, US $0.26 million in international grant and US $1.48 million in loan.
Budget (in million US dollars)
| External Input |
|||
| 3.1 | 0.10 | 0.20 | |
| 3.2 | 0.89 | 1.79 | |
| 3.3 | 0.59 | 1.13 | |
| 3.4 | 0.18 | 0.35 | |
| 3.5 | 0.05 | 0.08 | |
| Total | 1.81 | 3.55 |
5. Benefits
The most direct benefit to be obtained following the implementation of the project is the ability to control the effect of pollution from Baoding on Baiyangdian. Under normal conditions, the occurrence of serious accidents such as large-scale fish extermination will be minimized. With centralized resource to use techniques, centralized industrial reuse will be possible and water quality in Baiyangdian will regain the Grade 3 standard for land surface water. In addition, areas irrigated for agricultural purposes and aquatic farms will be expanded, water quality will be improved (with benefits for tourist areas), the normal function of the damaged aquatic ecosystem will be restored, and pollution-induced conflicts among cities, prefectures and counties will be eliminated to promote stability and unity.
From a long-term point of view, the improvement
of water quality accompanied by the stimulation of benign circulation in
regional ecosystems will benefit the regional economy and raise the living
standards and health of the people. In addition, Baiyangdian can serve as
a buffer, storing water coming to Beijing once the Middle Route Water Transfer
from South to North has been completed. This will guarantee the safety of
domestic water supply for the capital. The research results and applied
technology of the proposal will serve as an example for regional water pollution
control in the northern part of China.
Project Scope and Relationship to China's Agenda 21
This project seeks to further the sustainable development of the Yanqi Basin, through a strategy emphasizing wetland ecosystem improvement and recovery, Bosteng Lake water quality and its biodiversity protection. The project is based on the sustainable development and capacity building objectives of programme area 14C of China's Agenda 21, and will contribute to a number of related programme areas including conservation of land, water, energy, and biodiversity resources, and the improvement of human settlements (programme areas 12B, 15A, 16B,18A).
1 . Background
Bosteng Lake is situated in the Bayinguoleng Mongolian Antonomous Prefecture ("Bazhou") in Xinjiang, on the northern fringe of the Takelamakan desert. Kuerle, the capital of Bazhou, lies near the Lake, and China's Xinjiang oil base is situated in the area. The Bosteng Lake is also the water source supply area of the Green Corridor as well as a class one white swan nature reserve. Bosteng Lake lies in the area of the Yanqi basin, a well-Anown important agricultural region in Xinjiang. Bosteng Lake, with its 3 billion m3, of storage capacity, is undoubtedly the lifeblood of the local economy. At the same time, the level of pollution and of water quality of Bosteng Lake will be decisive in determining the viability of the Green Corridor. Therefore, preserving Bosteng Lake is essential to prevent the deterioration of the ecological environment and desertification in Bazhou.
In the 23 years from 1958 to 1981 , Bosteng Lake has shruk and the wetland around it has retreated. Moreover, water quality is steadily deteriorating. It is clear that both water quality and water quantity in Bosteng Lake have suffered serious degradation.
In the last 30 years, the water level of the Lake has dropped by 3.54 metres, the area of water reduced by 120 km2, and the water storage capacity decreased by 3 billion m3. The salinization of Bosteng Lake is also serious due to the deterioration of wetland and a great amount of farmland drainage. Industrial waste water and domestic sewage is drained directly into the Lake, resulting in an increase in the mineral content of lake water by 0.385 g/l to 1.8 g/l in the 25 years from 1958 to 1981, with a level of l.6 g/l at the present time. Thus, what was originally a fresh water lake has evolved into a slightly saline lake. The organic pollution of the lake water is also serious, with PH value reaching 8.69. The area of reed has been significantly reduced and growth of the natural community declined. The area of reed wetland has been reduced from 558.4 km2 in 1958 to 300 km2 in 1988, a reduction of about 40%. Of the remaining, a total of 80% has been affected by deterioration. Reeds yields have been reduced from 250 thousand ton/year to 60 thousand ton/year. The diversity of life-forms in the lake and on the lake-side wetland has been greatly threatened and many rare and precious wild animals have become extinct.
Some studies have been conducted on the Lake, including a study on reed resources, land use and soil conservation plans for Bazhou, research on eutrophication in Bosteng Lake (The Seventh Five-Year Plan key project), study on the water/salt balance in Yanqi basin, survey of aquatic resources in Bosteng Iake, etc.
2. Objectives
Long-term Objectives
Immediate Objectives
3. Activities
3.1 Develop techniques and formulate standards and policies for controlling the saline balance of Bosteng Lake.
3.2 Design Bosteng Lake lake-side wetland engineering projects and demonstration engineering measures.
3.3 Coordinate the development of basin exploitation and the preservation of water quality in Bosteng Lake.
3.4 Formulate Green Corridor preservation plan.
3.5 Establish the Bosteng Lake eco-environment control information system.
3.6 Train 3 - 4 persons as the key members for lake basin control, saline balance and control, and ecological engineering planning and implementation.
The implementing agency will be the National Environmental Protection Agency, and local government.
The duration of the above activities will be four years.
4. Inputs
4.1 Chinese inputs
4.2 International cooperation
4.3 Budget
The estimated budget of this proposed
project is US$ 11.12 million, including international inputs of US $3.62
million and Chinese inputs of US $7.5 million.
Budget (in million US dollars)
| Items | International Inputs |
||
| Engineering Expenses | 6.15 | 8.65 | |
| Operational expenses | 0.85 | -- | 0.85 |
| Research expenses | -- | 1.12 | |
| Survey expenses | 0.30 | -- | 0.30 |
| 0.20 | -- | 0.20 | |
| Total | 7.50 | 11.12 |
5. Benefits
Implementation of the project will restore the eco-environment of degraded reed wetland (73.2 km2) and preserve the habitats of wild animals and birds, thereby preserving wetland diversity. It will also improve the water quality of Bosteng Lake and preserve lake water resources. The mineral content of Bosteng Lake, in the light of the long-tenm objective, will be maintained at below 1 g/l. Water quality will reach the China national surface water quality standard Class II, ensuring water quality conditions necessary to promote the sustained economic growth in the region.
The project will regulate the balance of water capacity in arid areas and improve regional climate. The sale of reed, will generate substantial income, and following project completion, the annual benefit will be approximately US$ 2 million in the short-term and up to US$ 5 million in the long-term.
The Bosteng Lake basin is an area which is short of water. The protection of this lake can guarantee sustainable economic growth and the preservation of the Green Corridor.
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