Parikshit Verma EIA and Sustainability Assessment – Asian EIA and Effective Tool Development Seol,...
-
Upload
alvin-lang -
Category
Documents
-
view
217 -
download
0
Transcript of Parikshit Verma EIA and Sustainability Assessment – Asian EIA and Effective Tool Development Seol,...
Parikshit Verma
EIA and Sustainability Assessment – Asian EIA and Effective Tool Development
Seol, Korea,
June 5, 2007
Modeling Phytoremediation of Heavy Metal Contaminated Mine Spoil Dumps
National Environmental Engineering Research Institute (NEERI), Nagpur
Definitions / Terminology
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
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).
Moisture Retention Characteristics Curve
0.05 0.1 0.15 0.2 0.25 0.3 0.35 0.4 0.450
0.5
1
1.5
2
2.5
3
3.5S
uctio
n he
ad,
log(
h) (
cm)
Moisture content
mn
rs
r
h
h
1
1
Moisture flux in Unsaturated Zone
Relationship between Soil Moisture and Suction Head is called Soil Moisture Retention Characteristics (MRC)
1)(z
hhkq
1)()(z
hhk
zt
hhc
1
1
1
1
mn
rsnn
h
hn
hhc
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
pww
ws SqMz
MD
zM
tM
t
)()()(
Expensive and time consuming
mn
rs
r
h
h
1
1
Pedotransfer Functions
• Bulk density• Clay content• Carbon content• Particle size distribution
fMRC Parameters
θs, θr, n, m, α
Computational Scheme
Richard’s Equation descritized using Implicit scheme
12
)(11
111
1
2
11
1111
1
z
hh
z
kk
z
hhhk
t
hhhc
ti
ti
ti
ti
ti
ti
tit
i
ti
ti
1)()(z
hhk
zt
hhc
011
111
itii
tii
tii DhChBhA
2
11
z
kA
ti
i
2
11
2
1
z
k
z
k
t
hcB
ti
ti
i
2
1
z
kC
ti
i
z
kk
t
hhcD
ti
ti
ti
i
11
1
Calculate c(h)
Ih-h'I<Calculate
k(h)
Calculate Z(r)
Calculate S(z,t)
Calculate Ai
Calculate Bi
Calculate Ci
Calculate Di
Input n,a,ksInput
n,a,s,r
Input Zmax, DAP,
DTM
Input Tp(t), (h)
Input Initial condition,
Boundary condition
Input Assume
(h')
Solution matrix Calculate (h)
Replace h' with calculated value of h
Yes
Output Suction Head
(h)
No
Water flux
Plant root uptake function
Techniques of Phytoremediation
– Phyto-transformation
– Rhizosphere Bioremediation– Phyto-stabilization– Phyto-extraction– Rhizo-filtration
Limitations – Limited regulatory acceptance
– Long duration of time for cleanup– Potential contamination of fodder crop and food chain
– 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
Applicability
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.