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Modeling Phytoremediation of Heavy Metal Contaminated Mine Spoil Dumps

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Presentation on theme: "Modeling Phytoremediation of Heavy Metal Contaminated Mine Spoil Dumps"— Presentation transcript:

1 Modeling Phytoremediation of Heavy Metal Contaminated Mine Spoil Dumps
Parikshit Verma EIA and Sustainability Assessment – Asian EIA and Effective Tool Development Seol, Korea, June 5, 2007 National Environmental Engineering Research Institute (NEERI), Nagpur

2 Barren Manganese Mine Spoil Dump

3 After 10 years - Revegetated Manganese Mine Spoil Dump

4 Definitions / Terminology
Phytoremediation Use of plants / vegetation for in situ treatment of wastewater, contaminated soils or sediments. Some plants shows the capability to withstand relatively high concentration of chemicals without toxic effects (Hyperaccumulators). It is applied at sites with contamination of Organic Chemicals – BTEX, TNT, RDX, PCBs Nutrient – Ammonia, Phosphate, Nitrate Metal pollutants – Lead, Cadmium, Zinc, Arsenic, Chromium

5 Chemical uptake and translocation in the plant body

6 Unsaturated / Vadose zone

7 Processes that takes place in the root zone

8 Soil Water Partitioning

9 Metal Uptake by Plant Root
Michaelis and Menton Type of Reaction

10 Plant Root Growth

11 Saturated and Unsaturated Zone
Soil Water Soil Air Thin film of Water around soil particle

12 Saturated and Unsaturated Zone
Residual Moisture Saturation Moisture

13 Moisture Retention Characteristics Curve

14 Moisture flux in Unsaturated Zone
Relationship between Soil Moisture and Suction Head is called Soil Moisture Retention Characteristics (MRC)

15 Mathematical models used in the Metal Uptake model
Richards Equation Water uptake by plant root Metal uptake by plant root Root growth with time Plant root properties Moisture Retention Characteristics (MRC) Soil properties – Bulk Density, Clay content, Carbon content etc. Pedotransfer Function Soil Water Partition of pollutants Hydrodynamic Dispersion Moisture flux joining groundwater Chemical species flux joining groundwater

16 Pedotransfer Functions
Expensive and time consuming Bulk density Clay content Carbon content Particle size distribution MRC Parameters θs, θr, n, m, α f

17 Space – Time Domain of One Dimensional Transient Metal Uptake Model

18 Richard’s Equation descritized using Implicit scheme
Computational Scheme Richard’s Equation descritized using Implicit scheme

19

20 Techniques of Phytoremediation
Applicability – Other treatments are not cost effective Very large sites Low concentration of contaminants Only polishing treatment is required Where vegetation is used as final cap / site closure Limitations Limited regulatory acceptance Long duration of time for cleanup Potential contamination of fodder crop and food chain Techniques of Phytoremediation Phyto-transformation Rhizosphere Bioremediation Phyto-stabilization Phyto-extraction Rhizo-filtration

21 Why Phytoremediation Model Software ?
Design of experiments to determine the parameters of sub-surface phenomenon. Preparation of irrigation schedule for plantation on mine spoil dump. Decision on harvesting time of plants. Estimation of amount of heavy metal present in the plant.

22 NEERI PHYTOREM Model Software Demonstration


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