Assessment of air pollution stress on some commonly grown tree species in industrial zone of Durgapur, West Bengal, India.

The present study deals with the biochemical responses of some selected tree species with respect to increased air pollution in Durgapur industrial city in India. Areas in vicinity to industries possess very high concentrations of suspended particulate matter (571 microg/m3), SOx (132 microg/m3) and NOx (97 microg/m3) which shows significant correlations (p < 0.05) with the biochemical constituents of stressed plants. Plants growing in industrial zone exhibit a considerable decline in total chlorophyll (34.97-59.81%), soluble sugars (23.85-33.16%) and protein content (21.59-47.13%) and increase in ascorbic acid (81.87-238.53%) and proline content (123.47-284.91%). Of the studied tree species, Shorea robusta (9.78 +/- 0.095), Alstonia scholaris (8.76 +/- 0.084), Peltophorum pterocarpum (8.99 +/- 0.13) and Albizia lebbeck (7.71 +/- 0.012) were found to be more tolerant with higher Air Pollution Toblerance Index (APTI) and Tectona grandis (6.13 +/- 0.276), Lagerstroemia speciosa (7.075 +/- 0.18) and Delonix regia (6.87 +/- 0.079) were sensitive with lower APTI values. Therefore, plant species with higher APTI value, being more resistant, can be used as pollutant absorbent to reduce the pollution level and are suitable for plantations in industrial areas.

Temporal changes and depth wise variations in pit pond hydrochemistry contaminated with industrial effluents with special emphasis on metal distribution in water-sediment system.

The investigation showed pronounced temporal and vertical variations of pit lake-water chemistry contaminated with industrial effluents. An intermixing layer of few meters at a depth of 5-8 m usually separates an upper oxic epilimnion with alkaline pH from deeper sub-oxic/anoxic zone with relatively lower pH. Metal concentrations were in higher magnitude at anoxic zone in comparison to surface layer. Most of the parameters including metals showed higher concentrations during summer, while least concentrations were observed during monsoon. In shallow sediments, metals were mainly in insoluble-residual form, while redox metals were fractionated as oxihydroxide-reducible form. Geoaccumulation of metals in bottom sediments were Fe>Cr>Pb>Cu>Cd>Mn>Zn. Toxicity assessment showed that pit pond water is highly contaminated (C(d)=7.52) and moderate pollution load (PLI=2.272) in shallow sediments, with metal evaluation index (HEI) value of 11.08 and 15.91 respectively.

Metal accumulation and its effects in relation to biochemical response of vegetables irrigated with metal contaminated water and wastewater.

Agricultural application of metal contaminated water resulted in elevated concentrations of metals in irrigated soil and vegetables. Metal enrichment in irrigated soil is in the sequence of Cr>Fe>Pb>Mn>Zn>Cu>Cd. High metal translocation was observed from soil to plants with varied accumulation pattern in different species. Fe, Mn, Cu, Zn, Cr showed higher translocation to the aerial parts, while Cd, Pb exhibits their restricted mobility and concentrated in roots and stems. Hyperaccumulation of metals in vegetative parts resulted significant decrease (p<0.05) in total chlorophyll and soluble sugars, with elevated (p<0.05) protein and proline content in cultivated vegetables. Oxidative stress due to high metal concentrations significantly induced (p<0.05) the antioxidant-enzyme activity. Peroxidase (52-206%) and catalase (40-106%) activity was noticeably higher in all the examined species, while enhanced activity of ascorbate peroxidase (70-78%) was observed in pea and spinach.

Effect of wastewater irrigation on vegetables in relation to bioaccumulation of heavy metals and biochemical changes.

The present study was conducted to determine the heavy metal contamination in soil with accumulation in edible parts of plants and their subsequent changes in biochemical constituents due to wastewater irrigation. Though the wastewater contains low levels of the heavy metals (Fe, Mn, Pb, Cd, and Cr), the soil and plant samples show higher values due to accumulation. The trend of metal accumulation in wastewater-irrigated soil is in the order: Fe > Pb > Mn > Cr > Cd. Of the three species Colocasia esculentum, Brassica nigra, and Raphanus sativus that are grown, the order of total heavy metal accumulation in roots is Raphanus sativus > Colocasia esculentum, while in shoots the order is Brassica nigra > Colocasia esculentum > Raphanus sativus. The enrichment factor (EF) of the heavy metals in contaminated soil is in the sequence of Cd (3) > Mn (2.7) > Cr (1.62) > Pb (1.46) > Fe (1.44), while in plants EF varies depending upon the species and plant part. C. esculentum and R. sativus show a higher EF for Cr and Cd. All plants show a high transfer factor (TF > 1) for Cd signifying a high mobility of Cd from soil to plant whereas the TF values for Pb are very low as it is not bioavailable. Results of the biochemical parameters show decrease in total chlorophyll and total amino acid levels in plants and an increase in amounts of soluble sugars, total protein, ascorbic acid, and phenol except B. nigra for protein in plants grown in soil irrigated with wastewater as compared to control site.