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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
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Parikshit Verma EIA and Sustainability Assessment – Asian EIA and Effective Tool Development Seol, Korea, June 5, 2007 Modeling Phytoremediation of Heavy.

Dec 18, 2015

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Page 1: Parikshit Verma EIA and Sustainability Assessment – Asian EIA and Effective Tool Development Seol, Korea, June 5, 2007 Modeling Phytoremediation of Heavy.

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

Page 2: Parikshit Verma EIA and Sustainability Assessment – Asian EIA and Effective Tool Development Seol, Korea, June 5, 2007 Modeling Phytoremediation of Heavy.

Barren Manganese Mine Spoil Dump

Page 3: Parikshit Verma EIA and Sustainability Assessment – Asian EIA and Effective Tool Development Seol, Korea, June 5, 2007 Modeling Phytoremediation of Heavy.

After 10 years - Revegetated Manganese Mine Spoil Dump

Page 4: Parikshit Verma EIA and Sustainability Assessment – Asian EIA and Effective Tool Development Seol, Korea, June 5, 2007 Modeling Phytoremediation of Heavy.

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).

Page 5: Parikshit Verma EIA and Sustainability Assessment – Asian EIA and Effective Tool Development Seol, Korea, June 5, 2007 Modeling Phytoremediation of Heavy.

Chemical uptake and translocation in the plant body

Page 6: Parikshit Verma EIA and Sustainability Assessment – Asian EIA and Effective Tool Development Seol, Korea, June 5, 2007 Modeling Phytoremediation of Heavy.

Unsaturated / Vadose zone

Page 7: Parikshit Verma EIA and Sustainability Assessment – Asian EIA and Effective Tool Development Seol, Korea, June 5, 2007 Modeling Phytoremediation of Heavy.

Processes that takes place in the root zone

Page 8: Parikshit Verma EIA and Sustainability Assessment – Asian EIA and Effective Tool Development Seol, Korea, June 5, 2007 Modeling Phytoremediation of Heavy.

Soil Water Partitioning

sdw MkM

Page 9: Parikshit Verma EIA and Sustainability Assessment – Asian EIA and Effective Tool Development Seol, Korea, June 5, 2007 Modeling Phytoremediation of Heavy.

Metal Uptake by Plant Root

wm

wp

MK

MIS

max

Michaelis and Menton Type of Reaction

Page 10: Parikshit Verma EIA and Sustainability Assessment – Asian EIA and Effective Tool Development Seol, Korea, June 5, 2007 Modeling Phytoremediation of Heavy.

Plant Root Growth

maxmax

12

,Z

Zh

Z

tTtzS rp

47.103.315.0 max DTM

DAPSinZZ r

Page 11: Parikshit Verma EIA and Sustainability Assessment – Asian EIA and Effective Tool Development Seol, Korea, June 5, 2007 Modeling Phytoremediation of Heavy.

Saturated and Unsaturated Zone

–Soil

–Water

–Soil

–Air

–Thin film of Water around soil particle

Page 12: Parikshit Verma EIA and Sustainability Assessment – Asian EIA and Effective Tool Development Seol, Korea, June 5, 2007 Modeling Phytoremediation of Heavy.

Saturated and Unsaturated Zone

sr

– Residual Moisture – Saturation Moisture

Page 13: Parikshit Verma EIA and Sustainability Assessment – Asian EIA and Effective Tool Development Seol, Korea, June 5, 2007 Modeling Phytoremediation of Heavy.

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

Page 14: Parikshit Verma EIA and Sustainability Assessment – Asian EIA and Effective Tool Development Seol, Korea, June 5, 2007 Modeling Phytoremediation of Heavy.

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

Page 15: Parikshit Verma EIA and Sustainability Assessment – Asian EIA and Effective Tool Development Seol, Korea, June 5, 2007 Modeling Phytoremediation of Heavy.

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

)()()(

Page 16: Parikshit Verma EIA and Sustainability Assessment – Asian EIA and Effective Tool Development Seol, Korea, June 5, 2007 Modeling Phytoremediation of Heavy.

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

Page 17: Parikshit Verma EIA and Sustainability Assessment – Asian EIA and Effective Tool Development Seol, Korea, June 5, 2007 Modeling Phytoremediation of Heavy.

Space – Time Domain of One Dimensional Transient Metal Uptake Model

Page 18: Parikshit Verma EIA and Sustainability Assessment – Asian EIA and Effective Tool Development Seol, Korea, June 5, 2007 Modeling Phytoremediation of Heavy.

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

Page 19: Parikshit Verma EIA and Sustainability Assessment – Asian EIA and Effective Tool Development Seol, Korea, June 5, 2007 Modeling Phytoremediation of Heavy.

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

Page 20: Parikshit Verma EIA and Sustainability Assessment – Asian EIA and Effective Tool Development Seol, Korea, June 5, 2007 Modeling Phytoremediation of Heavy.

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

Page 21: Parikshit Verma EIA and Sustainability Assessment – Asian EIA and Effective Tool Development Seol, Korea, June 5, 2007 Modeling Phytoremediation of Heavy.

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.

Page 22: Parikshit Verma EIA and Sustainability Assessment – Asian EIA and Effective Tool Development Seol, Korea, June 5, 2007 Modeling Phytoremediation of Heavy.

NEERI PHYTOREM Model Software Demonstration