+ All Categories
Home > Documents > Phytoremediation of PHC & Salt

Phytoremediation of PHC & Salt

Date post: 13-Mar-2016
Category:
Upload: pete-mosley
View: 221 times
Download: 3 times
Share this document with a friend
Description:
Dr Bruce Greenberg Phytoremediation of PHC Salt
Popular Tags:
41
Phytoremediation of petroleum and salt impacted soils: Successfully meeting generic Tier 1 standards and making green technologies work Bruce Greenberg, X-D Huang, K Gerhardt, X-M Yu , S Liddycoat, X Lu, B McCallum, G MacNeill, M Hannaberg, P Mosley, J Gurska, N Knezevich, P Gerwing and B Chubb Partners: Cenovus; ConocoPhillips; Lone Pine Resources; Baytex; TransEuro Energy; Solaction; Shell; Talisman; PennWest; Questerre Beaver River; Imperial Oil; Seaway Energy Services; MWH; SNC Lavalin; NSERC EARTHMASTER ENVIRONMENTAL STRATEGIES INC.
Transcript
Page 1: Phytoremediation of PHC & Salt

Phytoremediation of petroleum and salt impacted soils: Successfully meeting

generic Tier 1 standards and making green technologies work

Bruce Greenberg, X-D Huang, K Gerhardt, X-M Yu, S Liddycoat, X Lu, B McCallum, G MacNeill, M Hannaberg, P Mosley, J Gurska, N Knezevich, P Gerwing and B Chubb

Partners: Cenovus; ConocoPhillips; Lone Pine Resources; Baytex; TransEuro Energy; Solaction; Shell; Talisman; PennWest; Questerre Beaver River; Imperial Oil;

Seaway Energy Services; MWH; SNC Lavalin; NSERC

EARTHMASTER ENVIRONMENTAL

STRATEGIES INC.

Page 2: Phytoremediation of PHC & Salt

Outline

1.  Overview of phytoremediation

3.  Science of successful phytoremediation

4.  Examples of full scale phytoremediation at petroleum and salt impacted sites

5.  Achieving Tier 1 and Tier 2 Criteria

Page 3: Phytoremediation of PHC & Salt

Phytoremediation Processes

•  Volatilization •  Phytodegradation •  Chelation/compartment in leaves

•  Translocation: root symplast xylem

•  Chelation/compartment in roots •  Plant uptake soilroot •  Rhizosphere Processes •  Bioavailability particlewater

Rhizodegradation - PHC

Salt

Page 4: Phytoremediation of PHC & Salt

1.  Improves the quality of soil

2.  It is driven by solar energy and suitable to most regions and climates

3.  It is cost effective and technically feasible

4.  Plants provide sufficient biomass for rapid remediation; promote high rhizosphere activity

5.  Reasonable time frames - 2 to 3 years

6.  Can be used effectively at remote sites

7.  Greenhouse gas storage: 6 tonnes per ha per year

8.  Effective for remediation of PHC and salt – relevant to the energy industry

Advantages of Phytoremediation

Page 5: Phytoremediation of PHC & Salt

Development, Proof, and Full Scale Application of PGPR Enhanced Phytoremediation Systems (PEPS)

Over 12 years of research with full-scale field remediations at each stage of development and application

1.  PHC: sites in AB, BC, QC, MB, NWT and ON (2004-11)

2.  Salt: sites in SK, AB and NWT (2007-11)

Performing full scale remediations for > 5 yrs

PEPS successful at > 25 sites

Page 6: Phytoremediation of PHC & Salt

The key to phytoremediation success - Transfer of the science from the lab to the field

EARTHMASTER ENVIRONMENTAL

STRATEGIES INC.

1.  Strategies for aggressive plant growth in impacted and poor quality soils at full scale sites – PEPS Deployment by highly trained scientists

2.  Monitoring the progress of phytoremediation at each site – Following the chemistry

3.  Continuous improvement of our phytoremediation systems through scientific research

Page 7: Phytoremediation of PHC & Salt

WEBi-Earthmaster-UW partnership

EARTHMASTER ENVIRONMENTAL

STRATEGIES INC.

•  Synergistic expertise in contaminated site remediation •  Developed commercial phytoremediation

technologies (PEPS) •  12 years of research, development and full scale field

implementation •  Field proven systems •  Research to continually improve PEPS

Page 8: Phytoremediation of PHC & Salt

Edson, AB – Before treatment

Soil Impact – PHC (Diesel Invert; 85% F3)

Job # 1 – Grow plants using PEPS

Page 9: Phytoremediation of PHC & Salt

PEPS Deployment at Edson, AB

Soil Impact – PHC (Diesel Invert; 85% F3)

Mission Accomplished - excellent plant growth

Page 10: Phytoremediation of PHC & Salt

Dawson, BC – Before PEPS treatment

Soil Impact – PHC (75% F3)

Page 11: Phytoremediation of PHC & Salt

Dawson after PEPS deployment – excellent plant growth

Soil Impact – PHC (75 % F3)

Page 12: Phytoremediation of PHC & Salt

Weyburn, SK - 1: Before PEPS

Soil Impact – Salt (ECe ~ 15 dS/m)

Page 13: Phytoremediation of PHC & Salt

Weyburn, SK - 1: PEPS utilization – 1 Month

Soil Impact – Salt (ECe ~ 15 dS/m)

Page 14: Phytoremediation of PHC & Salt

Weyburn, SK - 1: PEPS utilization – 3 Months

Soil Impact – Salt (ECe ~ 15 dS/m)

Page 15: Phytoremediation of PHC & Salt

Weyburn, SK - 2: Before PEPS deployment

Soil Impact – Salt (ECe ~ 10 dS/m)

Page 16: Phytoremediation of PHC & Salt

Weyburn, SK - 2: PEPS deployment – One month

Soil Impact – Salt (ECe ~ 10 dS/m)

Page 17: Phytoremediation of PHC & Salt

Weyburn, SK - 2: PEPS deployment – 3 Months

Average NaCl in leaf tissue = 23 g/kg

Soil Impact – Salt (ECe ~ 10 dS/m)

Page 18: Phytoremediation of PHC & Salt

500 kg of salt (NaCl) off the site in the plants

That is equal to the weight of a cow!

Page 19: Phytoremediation of PHC & Salt

PGPR Enhanced Phytoremediation Systems (PEPS) Aggressive plant growth strategies leads to remediation

Physical soil treatment: Seed bed preparation

Phytoremediation: Growth of plants with PGPR

Monitoring and remediation assessment: Environmental chemistry to follow PEPS from start–to–finish

•  PGPR: Plant growth promoting rhizobacteria. •  Prevent the synthesis of stress ethylene. •  PGPR are applied to the grass seeds prior to sowing

→ NOT Bioaugmentation •  Effect depth of remediation ~ 0.5 m

Page 20: Phytoremediation of PHC & Salt

Interaction of a PGPR Containing ACC Deaminase with a Plant Seed or Root

Plant growth promoting rhizobacteria (PGPR)

Natural, non-pathogenic strains of PGPR (usually Pseudomonads)

We have isolated PGPRs from ON, AB, SK and the NWT

PGPR are applied to seeds prior to planting

Page 21: Phytoremediation of PHC & Salt

With abundant plant growth – PEPS results in PHC Remediation

•  At least twice as much plant biomass due to PGPR; root growth to 50 cm below ground level

•  Remediation monitored using CCME PHC analytical methods •  30 to 40% remediation per year with PEPS; Twice as fast as plants

without PGPR •  Rhizosphere microbes (esp. PHC degraders) elevated 10 to 100 fold

with the PEPS - microbes and plants consume PHC •  Very low 14C detected in soil microbial fatty acids – Carbon came

from PHC metabolism (PHC has no 14C) •  Very low 14C in CO2 that evolves from soil – PHC has been

mineralized to CO2 •  No PHC detected in plant tissue as it disappears from the soil •  Tier 1 criteria (and closure) have been met at several full scale sites

sites

Page 22: Phytoremediation of PHC & Salt

Phytoremediation of PHC

oil droplet

O2

oxidized PHC

A

1 µm

PHC

PHC-degrading microbes

[O] DEHYD

[O] ω-OxGenase

[O] ω-OxGenase

Cn PHC

Rhizo.

cell membrane (width C30 to C40)

Cytosol

OH

H

Cn fatty acid

B

O

OH

O

(A) Microbial aerobic PHC degradation – rhizosphere supported by plants

(B) Possible microbial oxygenation pathway of PHC to form a fatty acid

Acetate

β-oxidation

Page 23: Phytoremediation of PHC & Salt

0

0.05

0.1

0.15

0.2

0.25

0.3

0.35

1 3 5 7 9 11 13 15 17 19 21 23 25

Tota

l PH

C (%

)

Sampling points

Jun-07 Oct-07 Jun-08 Oct-08

Total 31%

average

In June 2007, 9 of 13 sampling points above Tier 1 criteria (F3 > 1300 mg/kg)

Edson, AB – PHC Remediation (2007- 08) Soil Impact – PHC (Diesel Invert; 85% F3)

Page 24: Phytoremediation of PHC & Salt

0

500

1000

1500

2000

2500

3000

3500

LTA 1 LTA 3 LTA 5 LTA 7 LTA 9 LTA 16 LTA 17 LTA 19 LTA 21 Average

F3 (m

g/kg

)

Sampling points

Series1 Series2

31%

Alberta F3 Tier 1 Criteria

• Remediation goals were met • No points over Alberta Tier 1 criteria

June 07 Oct 08

Edson, AB – PHC Remediation (2007- 08) Soil Impact – PHC (Diesel Invert; 85% F3)

1 2 3 4 5 6 7 8 9 Average

Page 25: Phytoremediation of PHC & Salt

Soil Impact – PHC

Soil sampling point

sump

5

11

8

7

6

4

3

2

12 10

1

9

35 m

2 m

2 m

6 m

6 m

6 m

6 m

6 m

6 m 3 m 20 m

4 m

15 13

16 14

2 m 2 m 2 m

3.5 m

3.5 m

3.5 m

Planted un-impacted plot

1 m

Impacted Plot

Un-impacted Plot

Swan Hills, AB – End of Season (2009 – 10)

Page 26: Phytoremediation of PHC & Salt

0

500

1000

1500

2000

2500

3000

3500

4000

4500

1 3 4 5 7 8 9 12 Average 13 16 Average

Impacted Unimpacted Control

F3 (m

g/kg

)

June 2009 October 2009 September 2010

0

500

1000

1500

2000

2500

1 3 4 5 7 8 9 12 Average 13 16 Average

Impacted Unimpacted Control

F2 (m

g/kg

)

June 2009 October 2009 September 2010

65% remediation

F2 & F3 analysis performed by Maxxam. Method used: cold shake extraction, enhanced silica-column clean-up

Alberta Tier 1 standard

55% remediation

Alberta Tier 1 standard

Swan Hills, AB – F2/F3 Results

79% remediation

64% remediation

Anomalous sample point

Page 27: Phytoremediation of PHC & Salt

Phytoremediation Cost analysis: Edson Site

•  Volume of impacted material – 460 m3 of diesel invert drilling mud was originally spread over 1.07 ha

•  1.07 ha impacted to a depth of 0.3 m or 3,210 m3 of PHC impacted material

•  The costs for the entire project was: $104,000 or $32.50/m3 •  Includes all Earthmaster, WEBi and 3rd party costs •  Costs about the same at remote sites •  Unit cost drops as volume of impacted soil increases

•  Landfilling this material would have cost $80/m3 •  2 h truck turnaround time •  Costs increase dramatically as the site becomes more remote

Page 28: Phytoremediation of PHC & Salt

Conclusions for PHC Remediation SUCCESS •  Achieved PHC remediation: 5 sites brought to closure, 11

second generation sites progressing well towards closure

PERFORMANCE PREDICTIONS FOR PEPS •  Fine grain soils - F3 from 2000 to 10,000 mg/kg

•  In 2 to 4 years, will meet Alberta Tier 1 standards •  Fine grain soils - F3 above 10,000 mg/kg

•  In 3 to 6 years, will meet Alberta Tier 1 or 2 standards •  Coarse grain soils - F3 above 3000 mg/kg

•  Phytoremediation will significantly lower F3 •  Tier 2 approach may be required

COST •  Actual cost for the Edson site (3,400 m3) was $33/m3

•  Cost to landfill (landfill 1 h from site): at least $80/m3

Page 29: Phytoremediation of PHC & Salt

PEPS use at Salt Impacted Sites

EARTHMASTER ENVIRONMENTAL

STRATEGIES INC.

Page 30: Phytoremediation of PHC & Salt

Plant responses to salinity

•  Inhibited germination •  Decreased water uptake

•  Unbalanced sodium/potassium ratios •  Inhibition of photosynthesis •  Increased reactive oxygen species (ROS) •  Increased ethylene production •  PGPR doubles biomass

Page 31: Phytoremediation of PHC & Salt

Norman Wells, NWT – End of Season (2010) Soil Impact – Salt

Page 32: Phytoremediation of PHC & Salt

Plants used: slender wheatgrass and red fescue No soil conditioning

Norman Wells, NWT – End of Season (2008) Soil Impact – Salt

Page 33: Phytoremediation of PHC & Salt

High shale area has filled in 0

1

2

3

4

5

6

7

Tzero (2008) Year 2 (2009) Yeae 3 (2010) EC

e (d

s/m

)

Plot B

Year 3 (2010)

0

1

2

3

4

5

6

Tzero (2008) Year 2 (2009) Yeae 3 (2010)

ECe

(ds/

m)

Plot C

Year 3 (2010)

Salt Remediation

Norman Wells, NWT – End of Season (2010) Soil Impact – Salt

0

3

6

9

12

15

18

T zero (2008) Year 2 (2009) Yeae 3 (2010)

ECe

(ds/

m)

Plot A

Year 3 (2010)

Mass balance proves salt uptake

Page 34: Phytoremediation of PHC & Salt

Current Research to Improve PEPS

•  Optimize the CCME PHC analytical protocol to remove interferences from biogenic organic compounds (BOC)

•  Assess soil toxicity during phytoremediation to meet Tier 2 criteria

Page 35: Phytoremediation of PHC & Salt

During Phytoremediation – Have to assay PHC without interferences from biogenic organic

compounds (BOCs)

•  Ontario MOE sampled at 180 pristine rural and old urban parkland sites

•  218 surface soil samples were selected for PHC analysis

•  Only 36 of 218 were ND for F3 (For BC: will be in both and EPHC10-19 and EPHC19-32)

•  8 samples exceeded F3 criteria •  BOCs are primarily derived from

plant material – Problem for phytoremediation

Page 36: Phytoremediation of PHC & Salt

Enhanced CCME method for removal of BOCs

  The CCME method recognizes that BOCs will interfere and leads to a erroneously high PHC data (particularly F3)

  Clean up of extracts with silica gel can be used to help remove interfering BOC

  Proper use of Si cleanup can overcome most of the problems (e.g., Method 10 in BC)

  Two methods: 1. In situ Si treatment 2. Ex situ Si Column clean-up

(Enhanced BOC clean-up)

Page 37: Phytoremediation of PHC & Salt

GC-FID analysis of PEPS soil samples with Enhanced BOC method

No clean up In situ Si gel clean-up Si gel Column clean-up

BOC Some BOC removed

Almost all BOC removed

Enhanced BOC method used in phytoremediation

Page 38: Phytoremediation of PHC & Salt

GC-MS – Shows only BOC is removed by the enhanced BOC method

Total ion scan – GC-MS Total ion scan – GC-MS

No clean-up In situ Si clean-up Enhanced BOC Method

F2/F3 F3/F4

No clean-up

In situ Si clean-up

Enhanced BOC Method

Selective ion scan – GC-MS

Ion: 137

Compounds identified: plant terpenoids and plant sterols

Page 39: Phytoremediation of PHC & Salt

Plant toxicity testing – to meet Tier 2 criteria

•  Plant Species –  Cucumber, Barley,

Northern Wheatgrass

•  Endpoints –  Percent Emergence (7d; 14/21d) –  Root and shoot length/weight

0

0.5

1

1.5

2

2.5

3

3.5

4

4.5

0 500 1000 1500 2000 2500 3000 3500 4000 4500 5000

Nor

mal

ized

Ave

rage

End

poin

t Mea

sure

men

t

Petroleum Hydrocarbon F3 Concentration (mg/kg)

Followed Environment Canada plant toxicity test protocol

Environment Canada Protocol minimum endpoint requirements for artificial soil

Cucumber Root Weight

Plant toxicity not correlated with F3 levels

Will have springtail data shortly

Page 40: Phytoremediation of PHC & Salt

•  Proven to work PHC and/or salt impacted sites. •  Remediations at all sites have been successful; > 25 sites. •  Phytoremediation costs < half the cost of landfilling. •  Liability is reduced, not transferred to a landfill. •  Cost effective at remote sites. •  Enhanced CCME BOC method – phytoremediation will meet

Tier 1 criteria. •  Tier 2 approach – will work – After PEPS brings F3 levels ≤

2500 mg/kg no plant toxicity.

Why Use Phytoremediation?

Page 41: Phytoremediation of PHC & Salt

Thank you

EARTHMASTER ENVIRONMENTAL

STRATEGIES INC.

Please visit us at the Earthmaster booth for more information


Recommended