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Phyto-Remediation for Landfill Leachate Treatment

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Phyto-Remediation for Landfill Leachate Treatment John R. Buchanan Associate Professor, University of Tennessee, Walter H. Eifert Principal Hydrologist, ELM Site Solutions, Inc.
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Page 1: Phyto-Remediation for Landfill Leachate Treatment

Phyto-Remediation for Landfill

Leachate Treatment

John R. Buchanan Associate Professor, University of Tennessee,

Walter H. Eifert Principal Hydrologist, ELM Site Solutions, Inc.

Page 2: Phyto-Remediation for Landfill Leachate Treatment

Phyto-Remediation for Landfill

Leachate Treatment • Issue

– at the end of their useful life

• modern landfills are capped

• covered with a low permeability material to

minimize infiltration of precipitation

– before the advent of modern regulations

• completed landfills may have only been covered

with soil

Page 3: Phyto-Remediation for Landfill Leachate Treatment

Infiltration

• Without a cap

– more infiltration occurs

– more water comes in contact with solid

wastes

• becomes leachate

– increases hydraulic pressure on sidewalls

• seepage and slumping

– increases the potential for deep percolation

• groundwater contamination

Page 4: Phyto-Remediation for Landfill Leachate Treatment

Leachate

• At legacy landfills

– there are several conventional options for

dealing with leachate production

• replace “cover” with a “cap”

• install a geosynthetic clay liner over landfill

• collect leachate & haul to WWTP

• install & operate a WWTP

Page 5: Phyto-Remediation for Landfill Leachate Treatment

Leachate

• Making a decision about which solution to

implement depends on

– leachate chemistry

– evaluation of the hazard

• to groundwater

• to surface water

– availability of a WWTP

– cost

Page 6: Phyto-Remediation for Landfill Leachate Treatment

Potential Alternative Solution

• Create an Evapotranspiration Cover

– use the existing soil cover to store

precipitation

– use plants to remove the moisture from the

cover

– apply leachate to the cover during high ET

conditions

Page 7: Phyto-Remediation for Landfill Leachate Treatment

A Water Balance Approach

http://regclim.coas.oregonstate.edu/wp-content/uploads/BATS_highres.png

Page 8: Phyto-Remediation for Landfill Leachate Treatment

Water Balance Approach

• Moisture holding capacity

– volume of water that can be held by the soil

before deep percolation out of the root zone

• depends on texture (sand, silt, & clay content)

– Units

• inches of water per foot of soil

• typical silty clay → about 2” of water per foot of soil

Page 9: Phyto-Remediation for Landfill Leachate Treatment

Water Balance Approach

• Soil matrix potential

– often called soil

moisture tension

– soil matrix forces pull

on the moisture

• can hold moisture

above the force of

gravity

Page 10: Phyto-Remediation for Landfill Leachate Treatment

Water Balance Approach

• Infiltration and runoff

– if precipitation rate is greater than the

infiltration rate

• then the difference becomes runoff

– when precipitation rate is less than or equal to

the infiltration rate

• then precipitation infiltrates into the soil

– infiltration rate is dynamic

• rate decreases as water moves into soil

Page 11: Phyto-Remediation for Landfill Leachate Treatment

Water Balance Approach

• Evapotranspiration rates

– governed by how much moisture the air can

hold and move away

– function of

• temperature

• relative humidity

• wind speed

• plant characteristics

Page 12: Phyto-Remediation for Landfill Leachate Treatment

Trend for ET in Tennessee

0

1

2

3

4

5

6

Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec

Inches

Month

Precipitiation Evapotranspiration

Page 13: Phyto-Remediation for Landfill Leachate Treatment

Remember

• Only about 75% of

rainfall infiltrates into

the soil

– the remainder is runoff

• There will be wetter

years (such as 2018)

• There will be drier

years (such as 2016)

Page 14: Phyto-Remediation for Landfill Leachate Treatment

As Compared to a Cap

• A compacted clay cap still has some

infiltration

– 1x10-9 to 1x10-5 cm/s

– 0.032 to 315 cm of water per year

– 0.0124 to 124 inches of water per year

• ET cover is considered a success if

infiltration is equivalent to compacted clay

cap

Page 15: Phyto-Remediation for Landfill Leachate Treatment

Lowland, Tennessee

• Former 764-ac BASF manufacturing area

– previously known as Liberty Fibers

• rayon plant, originally American Enka Company

• opened in 1948

– now a very complex site in terms of

• ownership

• stormwater management

• environmental regulations

• local politics

Page 16: Phyto-Remediation for Landfill Leachate Treatment

North Landfill

• BASF owns two landfills on this site

– the focus is on the North Landfill

– used to store

• fly ash

– approximately 90% of volume

• production wastes

• wastewater treatment sludge

• garbage generated at plant

Page 17: Phyto-Remediation for Landfill Leachate Treatment

Closure

• Disposal operations ended in 1983

– covered with 30 inches of soil

– additional 30 inches added later to limit

infiltration

– considered “closed” in 1985

• non-RCRA closure

Page 18: Phyto-Remediation for Landfill Leachate Treatment

Leachate Management

• Historically, leachate has been collected

– by a subsurface toe drain system installed

around landfill base to intercept leachate

– this drainage system connected to a gravity

line that conveyed leachate to a lift station

– then,

• gravity flow, lift station, and gravity flow to WWTP

Page 19: Phyto-Remediation for Landfill Leachate Treatment

WWTP is Nearby But Pipes are Leaky

• With all the I&I

– the flow from former

manufacturing site has

been restricted

– little of the water was

leachate from BASF

– forced BASF into a

pump & haul system

for leachate disposal

Page 20: Phyto-Remediation for Landfill Leachate Treatment

A Potential Solution

• Is to minimize leachate production

– reduce percolation through cover by storing

moisture in the cover soil

– pull moisture out of the soil using ET to

reestablish storage

• use plant material that encourage transpiration

• high leaf surface area

• open canopy

Page 21: Phyto-Remediation for Landfill Leachate Treatment

Water Balance – Morristown, TN

0

1

2

3

4

5

Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec

Inches

Month

Precipitiation Grass Reference ET

Page 22: Phyto-Remediation for Landfill Leachate Treatment

Accounting for Runoff Assuming 85% Infiltration

0

1

2

3

4

5

Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec

Inches

Month

Infiltration Grass Reference ET

Page 23: Phyto-Remediation for Landfill Leachate Treatment

Soil Moisture Balance w/Grass Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec

I 3.4 3.5 3.5 3.3 3.5 3.1 4.0 3.0 2.6 1.9 2.9 3.4

ET 0.2 0.3 1.1 2.1 3.4 4.3 4.9 4.8 3.6 2.3 1.0 0.3

Net -3.2 -3.2 -2.4 -1.2 -0.2 1.1 1.0 1.8 1.0 0.4 -1.9 -3.1

S 8.2 10.0 10.0 10.0 10.0 8.9 7.9 6.1 5.1 4.8 6.7 9.8

D 0.0 1.4 2.4 1.2 0.2 0.0 0.0 0.0 0.0 0.0 0.0 0.0

I = Infiltration

ET = Evapotranspiration

Net = ET – I

S = Moisture Storage in Soil

D = Deep Percolation

Grass Reference ET

• began year with 5” of soil moisture

• ended year with 9.8” of soil moisture

• deep percolation: 5.1”

Page 24: Phyto-Remediation for Landfill Leachate Treatment

Hybrid Poplars

• Cross between

Eastern Cottonwood

and Black Poplar

– utilizes a prolific

volume of water

– tremendous leaf

surface area available

for transpiration

– NM6 and DN34

genotypes https://www.leachate.us/poplars/

Page 25: Phyto-Remediation for Landfill Leachate Treatment

Development of the Phytoplot

• Top surface of North Landfill

– 5 acres planted with 2,400 hybrid poplar trees

• November 2017

• 10-ft by 10-ft spacing

• 435 trees per acre

– Anticipated ET rates

• Year 1 – 1.2 gpd per tree

• Year 3 – 9.8 gpd per tree

• Year 5 – >20 gpd per tree

Page 26: Phyto-Remediation for Landfill Leachate Treatment

At Maturity

• Assuming 20 gpd per tree

– 8,700 gallons per acre

– 0.32 inch per day

– Greater than the Grass Reference ET

• Estimated 217 growing-days per year

– for trees in the Ridge and Valley of East

Tennessee

– essentially March through September

Page 27: Phyto-Remediation for Landfill Leachate Treatment

Water Balance with Trees Assuming 25% Greater ET

0.0

1.0

2.0

3.0

4.0

5.0

6.0

7.0

Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec

Inches

Month

Infiltration Tree Potential ET

Page 28: Phyto-Remediation for Landfill Leachate Treatment

Water Balance w/Trees (25%) Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec

I 3.4 3.5 3.5 3.3 3.5 3.1 4.0 3.0 2.6 1.9 2.9 3.4

ET 0.2 0.3 1.3 2.7 4.2 5.4 6.1 6.0 4.5 2.3 1.0 0.3

Net -3.2 -3.2 -2.1 -0.7 0.7 2.2 2.2 3.0 1.9 0.4 -1.9 -3.1

S 8.2 10.0 10.0 10.0 9.3 7.1 4.9 2.0 0.1 -0.3 1.6 4.7

D 0.0 1.4 2.1 0.7 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0

I = Infiltration

ET = Evapotranspiration

Net = ET – I

S = Moisture Storage in Soil

D = Deep Percolation

Assuming Tree ET is 25% greater than grass ET

• began year with 5” of soil moisture

• ended year with 5” of soil moisture

• deep percolation: 4.1”

Page 29: Phyto-Remediation for Landfill Leachate Treatment

Water Balance with Trees Assuming 35% Greater ET

0.0

1.0

2.0

3.0

4.0

5.0

6.0

7.0

Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec

Inches

Month

Infiltration Tree Potential ET

Page 30: Phyto-Remediation for Landfill Leachate Treatment

Water Balance w/Trees (35%) Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec

I 3.4 3.5 3.5 3.3 3.5 3.1 4.0 3.0 2.6 1.9 2.9 3.4

ET 0.2 0.3 1.4 2.9 4.5 5.8 6.6 6.4 4.8 2.3 1.0 0.3

Net -3.2 -3.2 -2.0 -0.5 1.0 2.6 2.7 3.4 2.3 0.4 -1.9 -3.1

S 8.2 10.0 10.0 10.0 9.0 6.3 3.7 0.2 -2.0 -2.4 -0.5 2.6

D 0.0 1.4 2.0 0.5 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0

I = Infiltration

ET = Evapotranspiration

Net = ET – I

S = Moisture Storage in Soil

D = Deep Percolation

Assuming Tree ET is 35% greater than grass ET

• began year with 5” of soil moisture

• ended year with 2.6” of soil moisture

• deep percolation: 3.8”

Page 31: Phyto-Remediation for Landfill Leachate Treatment

With a 35% ET Increase

• Soil moisture storage is maximized

– deep percolation is minimized

• will always have some deep percolation

• Now have excess ET capacity

– could use it to ET leachate

• irrigate phytoplot to ensure moisture is available to

be evapotranspired

• could apply 2.4 inches per year

Page 32: Phyto-Remediation for Landfill Leachate Treatment

Leachate Production

• Leachate flows were monitored

– October 2016 to February 2017

• peak flow, 25 gpm, heavy rain event

• wet weather flow, 6.6 gpm

• dry weather flows, 1.5 gpm

• For the phyto-remediation project

– the design flow became 3.5 gpm

• or 5,040 gallons per day

• 1.8 million gallons per year

Page 33: Phyto-Remediation for Landfill Leachate Treatment

Proposed Irrigation System

• Subsurface drip

irrigation

– one row of tubing per

row of trees

– effective irrigation area

is 1.5’ to each side of

tubing

– 1.4 acres of effective

irrigation area within 5-

ac phytoplot

10-ft row spacing

wetted soil volume

Page 34: Phyto-Remediation for Landfill Leachate Treatment

Irrigation Scheduling

• Proposed irrigation system is designed so

that no leachate is recirculated through

the solid wastes

– must have sufficient soil moisture storage to

hold additional moisture until evapotranspired

– application rate is equivalent to 0.04 inch per

hour

Page 35: Phyto-Remediation for Landfill Leachate Treatment

Leachate Application

• 5,040 gallons over 1.4 acres

– is 0.13 inch of moisture

• this is the design daily leachate production

• At anticipated ET of hybrid poplar trees

– there would be days when 0.32 inch of

moisture could be applied

• which is 2.4 times the daily design leachate

production

Page 36: Phyto-Remediation for Landfill Leachate Treatment

Performance Monitoring

• Sensors

– evapotranspiration

• sap flow meters, soil moisture sensors, Rh,

temperature, rain gauge, evap pan

– leachate flow and quality

• doppler meter in collection system

• automatic sampler

– Irrigation system

• flow meters and pressure gauges

Page 37: Phyto-Remediation for Landfill Leachate Treatment

Leachate Storage

• Three 21,000-gallon

tanks

– AKA, frac tanks

– plumbed in series

– surge tanks for pump

& haul

• Pump station for

proposed irrigation

system

Page 38: Phyto-Remediation for Landfill Leachate Treatment

Leachate Quality Most Results below Reporting Limit

• nitrate 0.02 mg/L

• nitrite

• ammonia 5.42 mg/L

• TSS 9.8 mg/L

• settleable solids 0.10 mg/L

• TKN 6.21 mg/L

• BOD5

• pH 7.70

• phenolics

• arsenic

• cadmium

• cyanide 0.0077 mg/L

• chromium

• copper

• lead

• molybdenum

• nickel

• phosphorus 0.147 mg/L

• selenium

• silver

• zinc

• mercury

Page 39: Phyto-Remediation for Landfill Leachate Treatment

Dissolved Constituents

• Precipitate will occur with evaporation

– selected hybrid poplars are salt tolerant

• Wet season rainfall will flush salts through

soil profile

• Recall

– that primary goal is to minimize leachate

production

– leachate treatment is a secondary benefit

Page 40: Phyto-Remediation for Landfill Leachate Treatment

Reduced Percolation means

Reduced Leachate Production

• With grass cover

– percolation estimated to be 5.1 inch per year

• equivalent to 4x10-7 cm/s

• With trees consuming 35% more than

grass

– percolation estimated to be 3.3 inch per year

• equivalent to 3.3x10-7 cm/s

Page 41: Phyto-Remediation for Landfill Leachate Treatment

For Legacy Landfills

• An evapotranspiration cover with leachate

irrigation is a potentially less expensive

solution

– for leachate management

– hybrid poplar trees have a luxurious

consumption of moisture

• maintains the moisture holding capacity of the

cover soil

• promotes evapotranspiration instead of percolation

Page 42: Phyto-Remediation for Landfill Leachate Treatment

QUESTIONS?

Thanks for your time!!


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