Integrating Environmental Considerations into the Economic Decision-Making Process
Modalities for environmental assessments
East and Southeast AsiaChina (Shanghai) Index
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III. ENVIRONMENT MONITORING AND URBAN PLANNING

[ III-A | III-B | III-C | III-D | III-E | III-F | III-G | III-H ]

G. Urban afforestation and environment

[ G | G-1 | G-2 | G-3 | G-4]

Urban afforestation is the secret weapon for attracting investment. Green trees, a nice environment and a civilized atmosphere, for instance, played an important part in attracting foreign investment to Singapore, and provoked the economic development of this resource-lacking island country, making it one of the richer countries of Asia.

In 1988, there was only 40.85 sq km of forested land in the total area of 350.4 sq km of Shanghai and the average green coverage was only 11.7 per cent. In a per capital area of 5.8 sq m, the per capita share of public green land was only 0.96 sq m. This green coverage level placed Shanghai not only last among the major cities in the world, but also in the last third of the 48 important cities in China. It is entirely out of proportion to the desired status of Shanghai as an international metropolis. At the same time, the average green coverage of other major cities around the world is 33.33 per cent and 36.25 sq m green land per capita (table 20). 

Table 21. The green coverage of major cities of the world 

Cities

Year

Greenland per capita (m3)

Green coverage (%)

Tokyo

1980

2.37

 

Osaka

1980

3.72

 

Singapore

1980

4.00

 

Moscow

1980

22.0

35

Chicago

1978

22.8

 

New York

1978

21.6

 

Montreal

1978

11.4

 

Paris

1980

9.50

 

Canberra

1980

 

58.0

Sydney

1980

 

28.0

Stockholm

1980

68.30

26.0

Warsaw

1980

73.80

 

Sophia

1980

25.00

20.0

Rome

1986

9.4

 

London

1978

33.4

 

Although Shanghai made great progress in afforestation from the beginning of reform to 1988, with green coverage increasing from 8.2 per cent to 11.7 per cent, and the average public green land per capita increasing from 0.47 sq m to 0.96 sq m, the discharge of soot and S02 are respectively 400t and 1500t per sq km inside the city, which vastly exceeds the environmental capacity. The development of industry and the expansion of the city have systematically seized the limited green land, threatening the urban eco-environment which not only was a bad influence on economic and social development, but damaged the physical and psychological health of the citizens.

Fig49

Figure 49. The spatial variation of the annual daily concentration of sulphur dioxide in the urban area in 1994

Fig50

Figure 50. The spatial variation of the annual daily concentration of sulphur dioxide in the urban area in 1986

Fig51

Figure 51. The spatial variation of the annual daily concentration of NOx in the urban area in 1994

Fig52

Figure 52. The spatial variation of the annual daily concentration of NOx in the urban area in 1986

Fig53

Figure 53. The spatial variation of the dustfall concentration in the urban area in 1994

Fig54

Figure 54. The spatial variation of the dustfall concentration in the urban area in 1986

Functions of green plants in improving the urban eco-environment, such as preserving water and soil, adjusting the temperature and humidity of air, preventing pollution and dust, purifying air and eliminating noise are well understood. Besides, urban green space also can improve people's health, edify people's minds, attract investment and bring enormous social and economic benefits. According to investigation, there is a very noticeable relationship between the distribution of consistency of S02 and urban green space in Shanghai. The consistency of S02 increases in winter when the tree leaves fall.

In terms of the urban planning authorized by the State Council in 1986, the average public green land per capita will reach 3 sq m and the green coverage will come to 20 per cent in 2000, although this is still lower than the average national level. From an historical standpoint, this goal would appear to be very difficult to achieve. In 1988, the Shanghai Afforestation Commission Office, Shanghai Afforestation Administration Guiding Station and the Department of Geography of Shanghai Normal University cooperated on the project "Green coverage remote sensing comprehensive investigation and research in Shanghai". Because of the high precision, short circulation and reality of aviation remote sensing, they determined the current situation of Shanghai green coverage and traced the changing pattern of the last twenty years through large scale urban green coverage investigation. Then they analyzed the relationship between the green coverage and environment in Shanghai, which suggested measures and directions for future afforestation work. Their serial cartography of Shanghai's urban green coverage and the first urban afforestation database of China provide a scientific basis for the rational and sound development of Shanghai urban afforestation.

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