Leachate`s Phytoremediation on Ft Collins` Landfill

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Leachate’s Phytoremediation at the Fort Collins Landfill

B Y : C A R L O S Q U I R O Z & A L I M E H D A W I

I N S T R U C T O R : E L I Z A B E T H P I L O N – S M I T H S

N O V E M B E R , 2 0 1 0

Photographic credit: Quiroz, 2010

Background

Photographic credit: Quiroz, 2010

Background

 Basic concepts

Landfill

Leachate

Background

 Fort Collins

Landfill

Background

Operation

Leachate

Management

Photographic credit: Quiroz, 2010

Background

 Fort Collins

Landfill

Background

Operation

Recycling

Hazardous management

Leachate

Management

Photographic credit: Quiroz, 2010

Background

 Fort Collins

Landfill

Background

Operation

Recycling

Hazardous management

Leachate

Management

Photographic credit: Quiroz, 2010

Background

 Fort Collins

Landfill

Background

Operation

Recycling

Hazardous management

Leachate

Management

Photographic credit: Quiroz, 2010

Background

 Fort Collins

Landfill

Background

Operation

Recycling

Hazardous management

Leachate

Management

Photographic credit: Quiroz, 2010

Background

 Fort Collins

Landfill

Background

Operation

Recycling

Hazardous management

Leachate

Management

Photographic credit: Quiroz, 2010

Background

 Scientific facts

• Che et al, (2006)

• Danha et al, (2006)

• El Gendy, (2008)

• Nagendran et al,

(2008)

• Jones et al, (2005)

• Justin et al, (2010)

• Kang et al, (2008)

• Zalesny et al, (2006)

• Zalesny et al, (2007)

• Using Popular Trees to Remove

Contaminants

Background

• Using Popular Trees to Remove

Contaminants

 Scientific facts

• Using

Popular Trees

Background

 Scientific facts

• (PRS)

• Passive Remediation Systems. (PRS)

Background

Scientific facts

• PRS irrigates hybrid poplar with the landfill leachate

Background

Scientific facts

Increasing of poplar trees biomass.

Objectives

Evaluate the current risk in the landfill.

Evaluate the current phytoremediation on the landfill.

Recommend suitable options to enhance the current situation.

Method

Topography, hydrogeology and heavy metals in ground water.

Heavy metals in plant tissues.

Proposals to situation.

Method

 Topography, hydrogeology and Heavy

Metals in ground water.

Source: Larimer County Landfill.

Results

Geology & hydrogeology

Source: Larimer County Landfill.

Results

Geology & hydrogeology

Source: Larimer County Landfill.

Source: Larimer County Landfill.

Results

Geology & hydrogeology

Method

 Heavy metals in plant tissues.

Photographic credit: Quiroz, 2010

Native Plants (North)

Control

Samples

(South)

Method

 Heavy metals in plant tissues.

Sunflower

Cottonwood

Smooth brome

Photographic credit: Quiroz, 2010

Method

 Heavy metals in plant tissues.

Photographic credit: Quiroz, 2010

Method

 Proposals to situation

- Buffer strip.

Remediation of groundwater through the irrigation of plants.

Licht & Isebrands (2005).

Results

Cotton Wood Smoothbrome Sunflower

Metal

Arsenic

PPM

0

Stand.

Desv

0

% Dry

Mass

0.00000

PPM

0

Stand.

Desv

0

% Dry

Mass

0

PPM

0

Stand.

Desv

0

% Dry

Mass

0.00000

Cadmium

Results

5.10

0.12

4.16

0.12

Copper

Iron

Lead

4.63

Metals in plant tissues.

2.77

5.10

1.65

0.00051

0.00001

0.00046

0.00274

0.00022

0.15

0.20

5.67

51.06

1.55

0.19

0.000015

0.47

0.30

2.51

22.16

2.27

0.00002

0.39

0.00057

45.31

0.00511

128.07

106.77

0.01281

0.00015

2.59

0.33

0.88

41.15

0.73

0.00005

0.00004

0.00453

0.00026

Magnesium 3670.60

1001.48

0.36706

2357.01

558.61

0.23570

3330.80

604.23

0.33308

North Samples

Manganese 67.69

26.67

0.00677

33.88

15.48

0.00339

15.14

6.24

0.00151

Mercury

Molybdenium

Nickel

0.44

0.37

0.13

0.69

0.83

0.19

0.00004

0.00004

0.00001

0.00

1.42

0.09

0.00

1.40

0.20

0.00000

0.00

0.00014

1.47

0.00001

0.03

0.00

2.15

0.06

0.00000

0.00015

0.00000

Sulfur

Selenium

Tellurium

Vanadium

Tungsten

Zinc

11858.60 6014.05

1.18586

4255.66

1590.24

0.42557

7092.00

2457.91

0.70920

19.22

3.31

0.00192

18.54

13.28

0.00185

20.69

4.59

0.00207

50.86

0.00

56.76

0.00

0.00509

0.00000

78.49

6.62

134.63

13.58

0.00785

0.00066

94.84

0.41

56.21

0.91

0.00948

0.00004

1.23

2.70

0.00012

119.88

216.72

0.01199

0.33

0.00

0.74

3.3111E-05 1.84

0.00

0 88.06

1.62

173.49

0.00018

0.00881

Metal

PPM

Cotton Wood

Stand.

Desv

% Dry

Mass

PPM

Smoothbrome

Stand.

Desv

% Dry

Mass

PPM

Sunflower

Stand.

Desv

% Dry

Mass

Arsenic

Cadmium

Copper

Iron

Lead

Results

0

0.32

0.00

Metals in

33.30

plant tissues.

0

0.17

0.00

0.66

4.76

1.53

0.00000

0.00003

0.00000

0.00046

0

0

0.32

8.07

0.00333

70.30

0.00017

3.97

0

0

0.45

6.12

0.00000

0

0.00000

0.25

0.00003

0.01

0.00081

41.33

0

0.09

0.01

24.77

13.46

0.00703

125.06

34.28

4.81

0.00040

2.44

2.30

0.00000

0.00003

0.00000

0.00413

0.01251

0.00024

South Samples

0.24570

2315.17

1365.92

0.23152

3009.00

427.98

0.30090

Manganese 4.45

0.00169

11.35

6.60

0.00114

6.62

1.59

0.00066

Mercury

(Control)

0.22

0.50

0.00002

3.00

3.82

0.00030

0.00

0.00

0.00000

Molybdenium

Nickel

Sulfur

Selenium

Tellurium

Vanadium

Tungsten

Zinc

1.09

1.13

0.00011

1.56

1.17

0.00016

0.20

0.42

0.00002

0.75

0.89

0.00008

0.08

0.18

0.00001

0.74

1.17

0.00007

5125.00

2651.79

0.51250

6126.73

3061.60

0.61267

10310.20 3316.54

1.03102

12.76

4.85

0.00128

23.14

14.77

0.00231

13.55

6.21

0.00135

107.43

29.04

0.01074

59.60

81.73

0.00596

33.53

43.64

0.00335

5.37

1.23

12.00

0.64

114.68

92.24

0.00054

0.00012

0.01147

0.35

0.85

2.85

0.78

1.90

6.38

0.00004

0.00

0.00009

0.55

0.00

0.81

0.00000

0.00006

0.00029

82.18

112.82

0.00822

Metal

Guideline Value

PPM*

Antimony

Arsenic

Barium

0.02

0.01

0.70

Nickel

Potassium

Selenium

Silver

Sodium

Sulfur

Tellurium

Thallium

Tin

Vanadium

Tungsten

Zinc

Beryllium

Results

Calcium

0.003

Cobalt

Current 0.05

Iron

Remediation of

Groundwater

0.01

Lead by Native

Manganese

Plants

0.40

0.001

Molybdenium 0.07

0.02

0.01

215.842

0.021

0.011

0.014

14.766

0.014

282.263

NE

0.0002

NE

0.026

149.821

0.028

0.014

742.053

NE

NE

0.013

0.1

0.029

NE

0.06

Groundwater Plant Tissue

PPM** Stand. Desv.

PPM*** Stand. Desv.

0.020

0.025

NE

0.019

0.824

0.023

0.243

0

NE

0.001

0.001

0.0004

0.0003

NE

5.104

4.162

47.934

0.008

0.005

0.015

NE

0.394

NE

45.306

16.249

128.068

0.013

2.594

41.793

3670.6

67.688

0.014

72.167

0.034

0.021

205.658

0.442

1.47

0.126

NE

20.688

NE

NE

11858.6

0.010

94.84

NE

NE

6.617

0.047

1.840

0.198

119.876

0.881

41.152

106.766

0.73

1001.48

Plant with Highest

Concentration of Metal

Cottonwood

Sunflower

Sunflower

Sunflower

Sunflower

Cottonwood

26.667

0.692

Cottonwood

Cottonwood

2.151

Smoothbrome / Sunflower

0.194

Cottonwood

4.588

6014.05

56.21

13.581

1.619

216.717

Sunflower

Cottonwood

Sunflower

Smoothbrome

Sunflower

Cottonwood

Buffer strip Area

Results

 Proposals to situation

Option 1

Solution: Buffer strip.

Plants: Cottonwood, sunflower, smoothbrome & vetiver.

Perimeter: 2.35 miles

Plantation density: 10,000 plants / ha. (Sebastian et al. 2004)

Buffer strip Area

Results

 Proposals to situation

Option 2

Solution: Buffer strip plus irrigation system to remediate polluted groundwater.

Plants: Cottonwood, sunflower, smoothbrome, vetiver.

Perimeter: 2.35 miles

Plantation density: 10,000 plants / ha. (Sebastian et al. 2004)

Irrigation: Wells located on the landfill.

Conclusions

Conclusions

Current Risk: Antimony, Arsenic,

Barium, Lead, Nickel, and Selenium are still over the guideline value.

Current Phytoremediation: Cadmium and Mercury by Cottonwood. Chromium by

Sunflower.

0.17 Acres on the north side (0.09% of area)

0.57 Acres on the south side (0.32% of area)

 Suitable Options:

Buffer strip around the landfill perimeter to prevent pollution of water resources.

Determine the groundwater flow to evaluate the feasibility of plant’s irrigation with leachate.

Conclusions

 None of the plants evaluated showed absortion of As. Thus,

Vetiver could be applied. L.T. Danh et Al (2009)

 More researches are needed to remediate antimony and barium on leachate.

 The buffer strip around the landfill could reduce the concentration of lead, nickel and selenium.

Acknowledgments

 Steve Harem, Environmental

Specialist of Larimer County Landfill.

 Colin Quinn, Post-Doc, Biology

Department

 Elizabeth Pilon – Smiths,

Professor, Biology Department.

References

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Che, D., Meagher, R.B., Heaton, A.C.P., Lima, A., Rugh, C.L. & Merkle, S.A., 2003. Blackwell publishing ltd. Expression of mercuric ion reductase in eastern cottonwood (populus deltoides) confers mercuric ion reduction and resistance. Plant Biotechnology Journal, 1, 311-319.

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References

Kim, K.-R. & Owens, G., 2010. Potential for enhanced phytoremediation of landfills using biosolids – a review. Journal of

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Lee, R.W., Jones, S.A., Kuniansky, E.L., Harvey, G., Lollar, B.S. & Slater, G.F., 2000. Phreatophyte influence on reductive dechlorination in a shallow aquifer contaminated with trichloroethene (tce). International Journal of Phytoremediation, 2

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Management, 30 (5), 856-862.

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Leachate’s Phytoremediation at the Fort Collins Landfill

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Photographic credit: Quiroz, 2010

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