Integrating Environmental Considerations into the Economic Decision-Making Process
Modalities for environmental assessments
East and Southeast Asia China (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 ]

A. Environmental quality in Shanghai

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

3. Noise

(a) Ambient noise

(i) Regional ambient noise

The average equivalent sound level measurement in each district in Shanghai in 1994 showed that the day-time noise in ChangNing district is the loudest and in PuTuo the lowest, while the night-time noise in MingHang district is the loudest and in Jin'an district the lowest. Comparing average equivalent sound levels in the urban area in the last three years, the ambient noise has been reduced due to such efforts as the designation of "zones with noise below specified limits", a ban on the use of motor vehicle horns, the construction of more green belts, and the erection of acoustic celotex boards along all the viaducts.

Fig27

Figure 27. The average equivalent sound levels

(ii) High air ambient noise

In 1994, the high air ambient noise deteriorated due to noise pollution brought about by municipal construction.

Fig28

Figure 28. Comparison of ambient noise in recent years

Fig29

Figure 29. Comparison of high air ambient noise in recent years

(b) Traffic noise

A comparison of monitoring data for recent years shows that traffic noise has been alleviated to a certain extent, despite the sharply increasing traffic volume in Shanghai. Especially in 1994, the daytime traffic noise decreased by 2 db(A). The main causes of this were: (1) operation of the Inner Ring Road (2) improvement in some of the roads in the urban area. (3) trucks were only permitted at night in Zhongshfm Road. (4) in some streets, measures were introduced to improve the traffic flow, such as pedestrian passages, one-way traffic, and no left-turns. (5) installation of acoustic celotex boards along the Inner Ring Road and a prohibition on the use of vehicle horns in some areas.

The traffic noise pollution in Shanghai is assessed by the traffic noise pollution index (TNPI)*. The day-time NPI is 1.03 and night-time 1.24, which meet the D grade or E grade limits respectively. This assessment indicates that noise pollution is still severe.

Fig30

Figure 30. Comparison of traffic noise in recent years

Table 4. TNPI grade standard

Class very good good normal polluted heavily polluted
TPNI <0.9 0.9-1.0 1.0 1.0-1.07 >1.07
Grade A B C D E

(c) Noise in different functional zones

Following GB3096-93, the Ambient Noise Standard in Urban Area, the monitored noise can meet the standard limits in class 2 zones where there is a cross-section of residential, commercial, and industrial land uses. In class one zones, which are for residences and administration, and in class 3 zones for industrial use, only the night-time noise exceeds the standard. The overall trend shows that ambient noise pollution in different functional zones has been alleviated.

* Definition of traffic noise pollution index caused

TNPI =

Li: Average equivalent sound level

L: The total length of main roads where the noise is monitored

Ls: Noise standard limit which is 70 dB(A) for daytime and 55 dB(A) for nighttime

li: The length of the road i

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