Fighting against POLLUTION to Save Environment

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Autoexhaust lead pollution of roadside ecosystem in Delhi:

J. Ind. Asso. Environ. Mgmt. 19, 21-27, 1992.

D. B. BORALKAR, S. K. TYAGI and S. B. SINGH
Central Pollution Control Board, 'Parivesh Bhawan' , CBD-Cum-office Complex, East Arjun Nagar,
Shahdara DELHI-110 032

Table 2: CATEGORISATION OF INTERSECTIONS BASED ON TRAFFIC DENSITY
S.N. Traffic Volume* Nos. Class Traffic Intersections
1 More than 30,000 I 08. Delhi Gate
05. Moolchand
2 25,000 to 29,000 II 04. A.I.I.M.S.
07. India Gate
3 20,000 to 24,999 III 10. Red Fort
12. Moti Nagar
09. Yamuna Bazar
06. Ashram
03. R.K. Puram
4 15,000 to 19,999 IV 02. Dhaula Kuan
01. Raja Garden
11. Zakira
5 Less than 15,000 V 13. Azadpur

*Petrol-driven Vehicles during 6 hr (Table 1)

Ambient Air Quality

The ambient air sampling and analysis for Pb, Suspended Particulate Matter (SPM), SO2 and NO2 was done as per Standard Methods.

Lead in Soil

The soil samples were collected in triplicate from top, bottom and middle portion of the pots of each species from every location. A composite sample was thus made for each species at every location. Precautions were taken to maintain uniformity in all soil sampling. Surface vegetation and debris, if any, were removed before sampling. Soil samples were dried for a minimum of 30 hr. After screening, the soil was pulverized and sieved through an 80-mesh screen. Lead content in the soil samples was determined by conventional atomic absorption Spectrophotometry.

Lead in Plants

Three plant species from six different locations were analysed in triplicate after scrubbing (leaf and shoot) and washing with water (root) for the lead content of the root, shoot and leaf using mixture of sulphuric and nitric acid for digestion. The test samples were processed on Atomic Absorption Spectrophotometer for estimation of lead. The dust deposited on leaves of different plant species was collected separately in pre-weighed beakers using a jet of double glass distilled water. The beaker was dried in 80°C oven for 24 hr, weighed and lead content of the dust in the beaker was determined.

Table 3: TRAFFIC FLOW AND AMBIENT AIR QUALITY AT SELECTED TRAFFIC INTERSECTIONS AND NPL NURSERY
S.N. Name Of Location Traffic Volume Nos. SO2 (µg/m3) NO2 (µg/m3) SPM (ng/m3) Pb (ng/m3)
1 Delhi Gate 36,923 36 49 696 193
2 India Gate 28,414 15 20 81 90
3 Red Fort 23,871 45 80 460 166
4 Ashram 18,009 30 25 382 192
5 Azadpur 15,608 40 75 818 277
6 NPL Nursery NIL 11 15 83 46

* Petrol-driven Vehicles during 6 hr (Table 1)

Plant Growth

The general growth of the plant species at six different locations was studied using the parameters: total chlorophyll, total biomass, leaf area (using LICOR 3000 Area Meter).

RESULTS AND DISCUSSION

Lead in the Roadside Ambient Air: The concentration of lead in ambient air at 13 traffic intersections was in the range 280 ng/m3 and 1,802 ng/m3 and SO2 and NO2 were mostly less than 100 µg/m3 in Jan. 1984. At the same intersections in June 1984, lead ranged between 170 ng/m3 and 926 ng/m3 while SO2 and NO2 did not exceed 100 µg/m3.

The lead in ambient air at five finally chosen traffic intersections and also at the control site within NPL Nursery was monitored once-a-month for 10 months from July 1984 to June 1985. No measurements could be conducted during November and December, 1984. Air quality monitoring was done for different periods of the time of the day, as follows:

AUTOEXHAUST LEAD

09.00 to 12.00 hr morning peak traffic hours 16.00 to 19.00 hr evening peak traffic hours 12.00 to 16.00 hr mid-day lean traffic hours 09.00 to 19.00 hr 10-hour day time traffic hours

Table 4: AMBIENT AIR LEAD CONTENT AT SIX DIFFERENT LOCATIONS*
S.N. Location Traffic Volume Class 9 am to 12 noon (3-hrly) 12 noon to 4 pm (4-hrly) 4 pm to 7 pm (3-hrly) 9 am to 7 pm (10-hrly)
1 Delhi Gate I 312 297 336 297
2 India Gate II 306 237 240 185
3 Red Fort III 353 270 436 287
4 Ashram IV 376 373 391 324
5 Azadpur V 336 328 298 252
6 NPL Nursery - 47 42 38 62

* Between July 1984 and June 1985

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