Fighting against POLLUTION to Save Environment
Table 2 : Classification of air pollutants in Norway

Compound Effect on Averaging time Classification criterion
SO2   health, materials and vegetation    1 day  100 ug/m3  
   6 months  30 ug/m3
Seat   health    1 day  100 ug/m3       high limit
   6 months  40 ug/m3       high limit
   6 months  20 ug/m3       high limit
NO2   health    1 hour  200 ug/m3  
   1 day  100 ug/m3
   6 months  75 ug/m3
CO   health    1 hour  25 mg/m3
   8 hours  10 mg/m3
O3   health and vegetation    1 hour  120 ug/m3
F   vegetation and animals    1 day  1.0 ug/m3       gaseous F
   1 month  0.2 ug/m3       total F
   6 months  0.3 ug/m3       gaseous F
Dustfall   Welfare    1 month  5 g/m2  
S   Acidification    1 year  0.5 g/m2

Discussion And Conclusions
Monitoring of concentrations and effects of different air pollutants is necessary for prevention and control of air pollution. Without data on concentrations and effects, there is no possibility of studying the occurrance and distribution of air pollutants and their effects in place and time, of setting standards for the protection of man and his environment, and of checking the results of abatement measures. What we need is an alarm system in order to prevent the occurance of excessive concentrations, resulting in hazardous effects on man, other animals, plants and materials. For these purposes both physical/chemical concentration measurements along with biological effect measurements with plants are needed. The concentrations measured by physico-chemical methods are not sufficient to predict all possible of air pollutants, and indicator plants will never be able to give information about identity and concentration of all polluting agents in air. There is no question of replacing ambient air monitoring by physical/chemical methods with effect-monitoring with plants ; both should be used jointly. Ambient concentration measurements, effect intensity measurements on plants (including chemical/physical leaf analysis), and measurements of meterological parameters, may together produce the total picture of the pollution situation (Posthumus,1984).

The work discussed earlier proves that plants can be used for the purpose of air monitoring as a cheap instrument and technique is easy for adoption. The biological-effect monitoring network regularly spread all over the country can be set up in close co-operation with other air quality monitoring network. The sensitive indicator and/or accumulator plants could be used in a standardised way. The need for the formulation of a national programme on the use of bioindicators for air quality is, therefore, strongly felt.

REFERENCES
  • Boralkar, D. B., U. Mukherjee and S. B. Singh. 1986. Increase of lead concentration during IX Asian Games at New Delhi as indicated by plants. Ind. J. Air Pollu. Contr. 7(2) : 65-73.
  • Boralkar D. B. and U. Mukherjee. 1991. Use of Alfalfa plants for air quality monitoring in Delhi. Geobios. 18 (1) : 29-32.
  • Chaphekar, S. B. 1978. Biological indicators : The concept and new additions. Int. J. Ecol.Environ. Sci, 4 : 45-52.
  • Chaphekar, S. B., D. B. Boralkar and R. P. Shetye. 1980. Plants for air monitoring in industrial areas, p. 669-675. In Proc. I. S. T. E. Symp. Trop- Ecol. and Dev. Kuala Lumpur.
  • N. E. E. R. I. 1981. Air quality data of selected Indian cities. Vol. I & II. National Environmental Engineering Research Institute, Nagpur.
  • Posthumus, A. C. 1984. Monitoring levels and effects of air pollutants. P. 73-96. In Air Pollution and Plant Life. M. Treshow (Ed.), John Wiley & Sons Ltd.
  • W. H. O. 1977. Air Monitoring Programme Design for Urban and Industrial Areas ; Global Environmental Monitoring System. World Health Organisation (W.H O.) Of set Publication No. 38.


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