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Fourth International Symposium on Bioremediation and Sustainable Environmental Technologies 22-25, May 2017 Miami, Florida Dhari Al-Gharabally, Aisha Al-Baroud, Hussain Al-Kandari - Kuwait Oil Company Kuwait Environmental Remediation Program (KERP): Oil Lakes Remediation in South East Kuwait Background After the Gulf war, in February 1991, Kuwait’s oil wells were damaged and set on fire, resulting in oil contamination of the land. Environment Contamination occurred from oil spreading over the land surface and penetrated the soil to varying depths forming oil lakes. This Unique Program is currently the largest environmental inland cleanup in the world. Types of Contamination The total estimated volume of contaminations is 26.1 million m 3 Contaminated Piles 12.22 Dry Oil Lakes 8.92 Wet Oil Lakes 4.56 Tarcrete 0.25 Wellhead Pits 0.116 Coastal Trenches 0.036 Dry Oil Lakes Dry contamination areas cover almost 100 km 2 of the desert, with an average depth of approximately 25 cm. The surface tar material in areas of dry soil contamination is found to contain mean TPH concentrations of about 7.3%. Underlying contaminated soil is found to contain a mean TPH concentration of 2.5% Wet Oil Lakes The distinguishing features of Oil Lakes with a surface area of over 7 km 2 include a surface layer of weathered crude, oily liquid/ sludge, sometimes covered by a thin, hardened crust. Investigations revealed that the average depth of oil contamination in the wet contaminated areas is approximately 63 cm. Sludge material has been found to contain mean TPH concentrations in excess of 19%. The underlying contaminated soil is found to contain a mean TPH concentration of 3.4% Oil Contaminated Piles Contaminated piles consolidate oil-contaminated soil and/or liquid oil into mounds. Oil-contaminated pile surface materials are found to contain mean TPH concentrations of about 4.0%. The underlying contaminated soil is found to contain a mean TPH concentration of 4.6% KERP Time Frame Total Remedial Solution The TRS will utilize soil remediation technologies together with a reduced scope for soil remediation through use of the Risk Based Approach (RBA). The remedial solutions that make up the TRS comprises of the following five key elements: 1. Risk Based Approach 2. Enhanced Bioremediation 3. Remediation Treatment Technologies 4. Sludge Disposal Via Beneficial Re-use 5. Engineered Landfills Bioremediation Technologies Option 2 “Enhanced Bioremediation” is the option to follow for remediation purpose. In-situ bioremediation and Ex-situ bioremediation are examples of bioremediation treatment methods. In-situ bioremediation is used to treat contaminated soils with low TPH level and depth up to 30. On the other hand, Ex-situ bioremediation is used to treat contaminated soils with higher TPH level and depth. Conclusion The impact of Iraq invasion in Kuwait environment is still on going. 26 million m 3 of Kuwait soil need to be remediated and sseveral technologies of bioremediation treatment methods are available in the market. Determining which treatment methods to use depends on multiple factors such as: cost, TPH target level, and soil characteristics. All of the mentioned technologies will reduce the contaminated soil TPH, which will lead to better environment conditions Bioventing (In-situ) Bioventing is a process of stimulating the natural in situ biodegradation of contaminants in soil by providing air or oxygen to existing soil microorganisms. Landfarming (Ex-situ) It is performed in the upper soil zone or in bio treatment cells. Contaminated soils, sediments, or sludge are transported to the landfarming site, incorporated into the soil surface and periodically (Figure 1). Composting (Ex-situ) The process depends on mixing the contaminated soil with organic materials, which will enhance and support the microbial growth and present.(Figure 2). Biopiles (Ex-situ) Biopiles treatment is a full-scale technology in which excavated soils are mixed with soil amendments and placed on a treatment area that includes leachate collection systems and some form of aeration (Figure 3). Figure 1 Figure 2 Figure 3 FIVE ELEMENTS OF TOTAL REMEDIAL SOLUTION (TRS) ENHANCED BIO- REMEDIATION SLUDGE RECOVERY LANDFILL RISK BASED APPROACH TREATMENT TECHNOLOGY ENABLING WORKS (PARALLEL ACTIVITIES) CUMULATIVE VOLUME - 5,000,000 10,000,000 15,000,000 20,000,000 25,000,000 30,000,000 0 1000000 2000000 3000000 4000000 5000000 6000000 7000000 2015 2016 2017 2018 2019 2020 2021 2022 2023 2024 2025 CUMULATIVE VOLUME, M3 ANNUAL VOLUME, M3 KERP - ESTIMATED SOIL VOLUME TREATED PER YEAR NK E&T SK E&T Remed I SK Remed II SK Remed III SK Remed I NK Remed II NK Sludge NK LF NK RBA Objective The objective of this poster is to demonstrate one such type of technology, known as bioremediation treatment for soil contaminated with total petroleum hydrocarbon.

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Page 1: ENABLING WORKS (PARALLEL ACTIVITIES)

Fourth International Symposium on Bioremediation and Sustainable Environmental Technologies22-25, May 2017 Miami, Florida

Dhari Al-Gharabally, Aisha Al-Baroud, Hussain Al-Kandari - Kuwait Oil Company

Kuwait Environmental Remediation Program (KERP): Oil Lakes Remediation in South East Kuwait

Background• After the Gulf war, in February 1991, Kuwait’s oil wells were damaged

and set on fire, resulting in oil contamination of the land.

• Environment Contamination occurred from oil spreading over the landsurface and penetrated the soil to varying depths forming oil lakes.

• This Unique Program is currently the largest environmental inlandcleanup in the world.

Types of Contamination• The total estimated volume of contaminations is 26.1 million m3

Contaminated Piles12.22

Dry Oil Lakes8.92

Wet Oil Lakes4.56 Tarcrete

0.25

Wellhead Pits0.116

Coastal Trenches0.036

Dry Oil Lakes• Dry contamination areas cover almost 100 km2 of the desert, with an average depth of approximately 25 cm.

The surface tar material in areas of dry soil contamination is found to contain mean TPH concentrations ofabout 7.3%. Underlying contaminated soil is found to contain a mean TPH concentration of 2.5%

Wet Oil LakesThe distinguishing features of Oil Lakes with a surface area of over 7 km2 include a surface layer of weatheredcrude, oily liquid/ sludge, sometimes covered by a thin, hardened crust. Investigations revealed that theaverage depth of oil contamination in the wet contaminated areas is approximately 63 cm. Sludge material hasbeen found to contain mean TPH concentrations in excess of 19%. The underlying contaminated soil is found tocontain a mean TPH concentration of 3.4%

Oil Contaminated PilesContaminated piles consolidate oil-contaminated soil and/or liquid oil into mounds. Oil-contaminated pilesurface materials are found to contain mean TPH concentrations of about 4.0%. The underlying contaminatedsoil is found to contain a mean TPH concentration of 4.6%

KERP Time Frame

Total Remedial Solution The TRS will utilize soil remediation technologies togetherwith a reduced scope for soil remediation through use ofthe Risk Based Approach (RBA). The remedial solutionsthat make up the TRS comprises of the following five keyelements:1. Risk Based Approach2. Enhanced Bioremediation3. Remediation Treatment Technologies4. Sludge Disposal Via Beneficial Re-use5. Engineered Landfills

Bioremediation Technologies Option 2 “Enhanced Bioremediation” is the option to follow for remediation purpose. In-situ bioremediationand Ex-situ bioremediation are examples of bioremediation treatment methods. In-situ bioremediation is usedto treat contaminated soils with low TPH level and depth up to 30. On the other hand, Ex-situ bioremediation isused to treat contaminated soils with higher TPH level and depth.

ConclusionThe impact of Iraq invasion in Kuwait environment is still on going. 26 million m3 of Kuwait soil need to beremediated and sseveral technologies of bioremediation treatment methods are available in the market.Determining which treatment methods to use depends on multiple factors such as: cost, TPH target level, andsoil characteristics. All of the mentioned technologies will reduce the contaminated soil TPH, which will lead tobetter environment conditions

Bioventing (In-situ)Bioventing is a process of stimulating the natural in situ biodegradation of contaminants in soil by providing airor oxygen to existing soil microorganisms.

Landfarming (Ex-situ)It is performed in the upper soil zone or in bio treatment cells. Contaminated soils, sediments, or sludge aretransported to the landfarming site, incorporated into the soil surface and periodically (Figure 1).

Composting (Ex-situ)The process depends on mixing the contaminated soil with organic materials, which will enhance and supportthe microbial growth and present.(Figure 2).

Biopiles (Ex-situ)Biopiles treatment is a full-scale technology in which excavated soils are mixed with soil amendments andplaced on a treatment area that includes leachate collection systems and some form of aeration (Figure 3).

Figure 1 Figure 2 Figure 3

FIVE ELEMENTS OF TOTAL REMEDIAL

SOLUTION (TRS)

ENHANCEDBIO-

REMEDIATIONSLUDGE

RECOVERY

LANDFILL

RISK BASED APPROACH

TREATMENTTECHNOLOGY

ENABLING WORKS (PARALLEL ACTIVITIES)

CUMULATIVEVOLUME

-

5,000,000

10,000,000

15,000,000

20,000,000

25,000,000

30,000,000

0

1000000

2000000

3000000

4000000

5000000

6000000

7000000

2015 2016 2017 2018 2019 2020 2021 2022 2023 2024 2025

CU

MU

LATI

VE

VO

LUM

E, M

3

AN

NU

AL

VO

LUM

E, M

3

KERP - ESTIMATED SOIL VOLUME TREATED PER YEAR

NK E&T SK E&T Remed I SK Remed II SK Remed III SK

Remed I NK Remed II NK Sludge NK LF NK RBA

Objective• The objective of this poster is to demonstrate one such type of technology,

known as bioremediation treatment for soil contaminated with totalpetroleum hydrocarbon.