Membrane Separation Technology for Water Treatment in Upstream Oil & Gas Operations
presented by James Robinson on April 20, 2016, at the "Semi-Annual Water & Wastewater Short Course: Issues, Challenges, Solutions & New Technologies" hosted by the Global Petroleum Research Institute (GPRI) at Texas A&M's Department of Petroleum Engineering.
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Membrane Separation Technology for Water Treatment in Upstream Oil & Gas Operations
1. James Robinson, 2016
Membrane Separation Technology for
Water Treatment in
Upstream Oil & Gas Operations
James Robinson, P.E.
April 20, 2016
Semi-Annual Water & Wastewater Short Course: Issues, Challenges, Solutions & New Technologies
Global Petroleum Research Institute (GPRI) - Texas A&M Department of Petroleum Engineering
2. James Robinson, 2016
James Robinson, P.E.
Experience
• Water Treatment
Engineering Advisor
• Chevron (2011-2015)
• BP (2000-2009)
• Water Management
Engineering Consultant
• Oxidane Engineering (2009-2011, 2015-present)
• Cypress Engineering (1991-2000)
Professional
• Professional Engineer
• Society of Petroleum Engineers
• Produced Water Society
Education
• B.S. in Civil Engineering (1990)
Louisiana State University
• M.S. in Engineering (1992)
Rice University
Contact
• jcr.tx@icloud.com
• (281) 384-3327
3. James Robinson, 2016
Outline
• Introduction / Overview
• Composition / Characterization
• Seawater,
• Produced Water
• Quantities
• Produced Water Disposition
• Water Treatment Process Design
• Onshore Scenarios
• Offshore Scenarios
4. James Robinson, 2016
Terms used
• PW - produced water
• BPD - barrels per day
• MF - microfiltration membrane
• NF - nanofiltration membrane
• SRM - sulfate removal membrane
• RO - reverse osmosis membrane
• TSS - total suspended solids
• TDS - total dissolved solids
• TPH - total petroleum hydrocarbons (non-soluble organics)
• TOG - total oil & grease (soluble & non-soluble organics)
• EOR - enhanced oil recovery
• ASP - alkali, surfactant, polymer (Chemical-EOR)
• IX - ion exchange (softening)
7. James Robinson, 2016
Primary Produced Water Constituents
Produced Water
Organic Inorganic
Insoluble SolubleInsoluble Soluble
Cations Anions
Monovalent Multivalent
Produced Water
Organic Inorganic
Insoluble SolubleInsoluble Soluble
Cations Anions
Monovalent Multivalent
8. James Robinson, 2016
Primary Produced Water Constituents to remove
for Produced Water Re-Injection (PWRI)
Produced Water
Organic Inorganic
Insoluble SolubleInsoluble Soluble
Cations Anions
Monovalent Multivalent
TPH TSS
MF
9. James Robinson, 2016
Primary Produced Water Constituents to remove
for Offshore Discharge
Produced Water
Organic Inorganic
Insoluble SolubleInsoluble Soluble
Cations Anions
Monovalent Multivalent
Produced Water
Organic Inorganic
Insoluble SolubleInsoluble Soluble
Cations Anions
Monovalent Multivalent
TPH
TOG
10. James Robinson, 2016
Primary Produced Water Constituents to remove
for Chemical-EOR Flood
Produced Water
Organic Inorganic
Insoluble SolubleInsoluble Soluble
Cations Anions
Monovalent Multivalent
Produced Water
Organic Inorganic
Insoluble SolubleInsoluble Soluble
Cations Anions
Monovalent Multivalent
TSSTPH
TOG
HardnessNF
MF
11. James Robinson, 2016
Primary Produced Water Constituents to remove
for Low Salinity Waterflood & Beneficial Reuse
Produced Water
Organic Inorganic
Insoluble SolubleInsoluble Soluble
Cations Anions
Monovalent Multivalent
Produced Water
Organic Inorganic
Insoluble SolubleInsoluble Soluble
Cations Anions
Monovalent Multivalent
TSSTPH
TOG
TDS
MF
RO
12. James Robinson, 2016
Quantities
• Seawater Injection
• Many offshore developments inject ~1 to 2 bbls seawater per bbl fluid (oil & water)
produced
• Typical offshore injection wells are designed to injection ~10,000 to 30,000 BPD seawater
• Several large offshore facilities inject ~500,000 BPD seawater
• Produced Water
• On average, 8 bbls water produced per bbl oil worldwide
• Some mature field are economically operated at up to 98% water cut (50 bbls water
produced / bbl oil produced)
• U.S. produced water for all oil & gas is ~21 billion bbls (882 billion gals)
(Source: Clark and Veil, 2009)
• Of that amount, flow-back water from hydraulic fracturing of unconventional wells in the
US is ~1.2 billion bbls (50 billion gals; 5.7% of all produced water)
13. James Robinson, 2016
Produced Water Disposition
• Onshore
~95% PW is re-injected into injection wells
(either water flood or disposal)
~5% PW is treated for beneficial reuse
(generally, where disposal capacity is limited or where water is scarce)
• Offshore
~85% PW is treated for discharge into the sea
(disposal overboard)
~15% PW is re-injected into injection wells
(either water flood or disposal; generally, where required by regulation)
14. James Robinson, 2016
Water Treatment Process Design
• Water Balance & Water Management Plan
• Source Water (Influent) Selection &
Water Quality Characterization
• Operational Conditions, Constraints & Priorities
• Treated Effluent Use, Disposal &
Water Quality Specifications
• Optimize Water Management (Reduce, Reuse & Recycle)
• Technology Selection
• Integration of multi-technology process (pre-treatment processes)
15. James Robinson, 2016
Water Balance & Water Management Plan
• Water Balance
• Determine Water Needs
• Identify Potential Water Sources and
Capacities
• Determine Wastewater Streams
• Identify Wastewater Disposal Options
and Capacities
• Optimize Water Management
• Identify Water Efficiency / Reduction
Opportunities
• Identify Water Reuse Opportunities
(with minimal or no water treatment)
• Identify Water Recycling Opportunities
(with significant water treatment)
• Develop a Water Management Plan:
• Meets water needs
• Has available/sustainable water
sources
• Ensures adequate wastewater disposal
capacity / reliability
• Considers timing of water needs, water
sources, wastewater streams
• Maximizes economic benefits of water
reduction, reuse & recycling
• Minimized environmental impacts on
water supplies and environments where
wastewater is disposed
16. James Robinson, 2016
Treatment Conditions, Constraints & Priorities
• Water Quality & Quantity variability
• Onshore vs Offshore
• Manned vs Un-manned
• Manually Controlled vs Remote Controlled vs Automated
• CAPEX vs OPEX
• Reliability / Redundancy
• Project life-cycle, re-deployment
17. James Robinson, 2016
Primary Options for Produced Water Disposition
• Reuse (minimal or no treatment)
• Waterflood
• Recycling (requires treatment)
• Steam Flood EOR
• Low Salinity Waterflood EOR
• Chemical-EOR Flood
• Beneficial Reuse
• Agriculture
• Irrigation
• Livestock
• Stream flow restoration
• Groundwater Aquifer restoration
• Disposal
• Deep well injection
• Surface discharge (offshore discharge)
• Evaporation
18. James Robinson, 2016
Technology Selection
• Select the most appropriate (economical / reliable /
compact) technology(s) that will achieve the
Treated Effluent Specifications, given the
Source Water Characterization and
Operational Conditions, Constraints & Priorities
• A multi-technology process is often required
(pre-treatment, etc.)
19. James Robinson, 2016
Examples of Onshore Scenarios (Generic/Hypothetical)
• Onshore Produced Water Treatment Process
(Ceramic MF & RO)
• Onshore Chemical-EOR Waterflood Process (MF & NF)
• Onshore Gas Gathering and Processing Plant
Wastewater Recycling Process (MF & RO)
20. James Robinson, 2016
Onshore Produced Water Treatment Process
(Ceramic MF & RO)
Scenario: Beneficial reuse of produced water used as alternative to water disposal in wells due to
limited water disposal capacity and reliability; Ceramic MF used as a pre-treatment for IX and RO
Influent: Produced Water (formation water plus re-produced steam)
Influent Water Characterization:
Flowrate: 50,000 BPD
TDS: 6,000 mg/L
TSS: 10 mg/L
TPH: 100 mg/L (after primary oil/water separation)
Treated Effluent Use: Discharge to Surface Wetlands
Treated Effluent Specification:
TDS: < 500 mg/L
TPH: < 1 mg/L
(additional treated effluent specification include organic compounds and metals)
Process:
Primary
Oil/Water
Separation
PW Gravity
Separation
IX WetlandsRO
Surface
Discharge
to River
Gas
Flotation
Walnut
Shell
Filter
Ceramic
MF
22. James Robinson, 2016
Onshore Chemical-EOR Waterflood Process
(Ceramic MF & NF)
Scenario: Ceramic MF used as pretreatment for IX and NF; NF used for PW softening for mixing
with ASP for injection into wells for enhanced oil production
Influents:
Produced Water (formation water)
Influent Water Characterization:
Flowrate: 50,000 BPD
TDS: 2,500 mg/L
TSS: 10 mg/L
TPH: 100 mg/L (after primary oil/water separation)
Treated Effluent Use: Produced Water Recycling for Mixing with ASP for polymer flood
Treated Effluent Specifications:
For mixing with ASP and then injection into wells:
Hardness: < 30 mg/L
TPH: < 1 mg/L (feed into NF)
TSS: < 1 mg/L
Process:
Primary
Oil/Water
Separation
PW Gravity
Separation
IX
ASP
Mixing
NF
Injection
Wells
Gas
Flotation
Walnut
Shell
Filter
Ceramic
MF
24. James Robinson, 2016
Onshore Gas Gathering and Processing Plant
Wastewater Recycling Process (MF & RO)
Scenario: Wastewater recycling is an alternative to disposal in wells due to limited well disposal capacity and reliability
Influents:
Produced Water (formation water); (oily, saline & TSS)
Utility / Process Area Water (UPA: wash water) (oily, non-saline, TSS)
IX Brine (non-oily, saline, no-TSS)
Cooling Tower Blowdown (CBD: non-oily, saline, no-TSS)
Steam Boiler Blowdown (BBD: non-oily, saline, no-TSS)
PW Water Characterization:
Flowrate: 1,900 m3/d (12,000 BPD)
TDS: 5,000 mg/L
TSS: 10 mg/L
TPH: 100 mg/L (after primary oil/water separation)
Treated Effluent Use: Produced Water Recycling for feed to Steam Boilers
Treated Effluent Specifications:
For reuse in Steam Boilers:
Hardness: < 0.5 mg/L (feed into steam boilers)
TPH: < 1 mg/L (feed into NF)
TSS: < 1 mg/L
Technology Selection:
• PW treatment with gas flotation & nutshell filtration prior to wastewater recycling process
• Concentrated brine streams (CBD, BBD, IX Brine) go to disposal wells (not sent to PW recycling process
• PW & UPA streams are combined and treated with MF & NF in wastewater recycling process
25. James Robinson, 2016
Onshore Gas Gathering and Processing Plant
Without Wastewater Recycling Process
River Water
Intake
River Water
Treatment
Water
Distribution
Network
Sour
Water
Stripper
Boiler
Water
Treatment
Cooling
Water
Towers
Steam Injection:
2000 m3/d
Boiler Blowdown:
100 m3/d
Evaporation:
1000 m3/d
Cooling Tower Blowdown: 50 m3/d
Sour Water: 100 m3/d
Utility /
Process Area
Wash-down
Water Utility/Wash-down Water;
100 m3/d
Steam
Boilers
IX Brine: 100 m3/d
Produced
Water:
2000 m3/d
Produced
Water
Treatment
Wastewater
Disposal
Wells
2100 m3/d
2200
m3/d
1050
m3/d
100
m3/d
100
m3/d
3450
m3/d
2450
m3/d
Produced Water;
2000 m3/d
26. James Robinson, 2016
Onshore Gas Gathering and Processing Plant
With Wastewater Recycling Process
River Water
Intake
River Water
Treatment
Water
Distribution
Network
Sour
Water
Stripper
Boiler
Water
Treatment
Cooling
Water
Towers
Steam Injection:
2000 m3/d
Boiler Blowdown:
100 m3/d
Evaporation:
1000 m3/d
Cooling Tower Blowdown: 50 m3/d
Sour Water: 100 m3/d
Utility /
Process Area
Wash-down
Water
Utility/Wash-down Water;
100 m3/d
Steam
Boilers
IX Brine: 20 m3/d (was 100 m3/d)
Produced
Water:
2000 m3/d
Produced
Water
Treatment
Wastewater
Disposal
Wells
MF & NF
Wastewater
Recycling
Process
Retentate
(Waste Stream):
210 m3/d
Permeate
(Recycled Water):
1890 m3/d
210 m3/d
230
m3/d
1050
m3/d
100
m3/d
100
m3/d
1480
m3/d
480
m3/d
(was
3450
m3/d)
(was
2450
m3/d)
27. James Robinson, 2016
Examples of Offshore Scenarios (Generic/Hypothetical)
• Offshore Waterflood Process (MF)
• Offshore Sulfate Removal Membrane (SRM) Process (NF)
• Offshore Low Salinity Waterflood Process (NF & RO)
• Offshore Chemical-EOR Waterflood Process (NF)
28. James Robinson, 2016
Offshore Waterflood Process (MF)
Scenario: MF used as an alternative to multi-media filters for suspended solids
removal; Seawater injection is to maintain reservoir pressure and improve oil
production
Influent: Seawater
Influent Water Characterization:
Flowrate: 100,000 BPD
TSS: 2 mg/L
Treated Effluent Use: Injection into wells for reservoir pressure maintenance
Treated Effluent Specification:
TSS: < 0.1 mg/L; max solids particle size < 10 microns
Process: Seawater
Lift Pumps
Coarse
Strainers
MF
Deaeration
Towers
Injection
Wells
29. James Robinson, 2016
Offshore Sulfate Removal Membrane (SRM)
Process (NF)
Scenario: sulfate removal membranes (SRM) used as mitigation to prevent barium
sulfate scale precipitation and/or reservoir souring; Seawater injection is to maintain
reservoir pressure and improve oil production
Influent: Seawater
Influent Water Characterization:
Flowrate: 100,000 BPD
TSS: 2 mg/L
SO4: 2,700 mg/L
Treated Effluent Use: Injection into wells for reservoir pressure maintenance
Treated Effluent Specification:
TSS: < 0.1 mg/L; max solids particle size < 10 microns
SO4: < 40 mg/L
Process: Seawater
Lift Pumps
Coarse
Strainers
MF
Deaeration
Towers
Injection
Wells
SRM
(NF)
30. James Robinson, 2016
Sulfate Removal Membranes (SRM)
• Used to mitigate scale formation:
• Where oilfield reservoir formation water contains significant amounts of barium and/or
strontium, injection of seawater can cause barium and strontium sulfate scale to be
formed.
• These scales can become deposited in production pipe internals and may also have
the effect of reducing reservoir permeability.
• Barium and strontium sulfate scales are difficult to remove since they are not easily
dissolved.
• Uses nano-filtration membranes to remove sulfates from seawater
• Reduces seawater sulfate ion concentration from around 2,700 ppm to less than 40 ppm.
• May help mitigate formation souring by limiting the action of sulfate reducing bacteria
(SRB)
33. James Robinson, 2016
Offshore Low-Salinity Waterflood Process
(NF & RO)
Scenario: A combination of NF and RO used to partially desalinate and remove sulfate from
seawater; Low-salinity seawater injection is to maintain reservoir pressure and enhance oil
production
Influent: Seawater
Influent Water Characterization:
Flowrate: 100,000 BPD
TDS: 35,000 mg/L
TSS: 2 mg/L
SO4: 2,700 mg/L
Treated Effluent Use: Injection into wells for reservoir pressure maintenance
Treated Effluent Specification:
TSS: < 0.1 mg/L; max solids particle size < 10 microns
TDS: < 4,000 mg/L
SO4: < 40 mg/L
Process:
Seawater
Lift Pumps
Coarse
Strainers
MF
Deaeration
Towers
Injection
Wells
NF
RO
34. James Robinson, 2016
Offshore Chemical-EOR Waterflood Process (NF)
Scenario: NF used to soften seawater; Softened seawater is mixed with ASP for injection to
maintain reservoir pressure and enhance oil production
Influent: Seawater
Influent Water Characterization:
Flowrate: 100,000 BPD
TDS: 35,000 mg/L
TSS: 2 mg/L
SO4: 2,700 mg/L
Treated Effluent Use: Mixing with ASP for polymer flood injection into wells for enhanced oil
production
Treated Effluent Specification:
TSS: < 0.1 mg/L; max solids particle size < 10 microns
SO4: < 40 mg/L
Hardness: < 300 mg/L
Process: Seawater
Lift Pumps
Coarse
Strainers
MF
Deaeration
Towers
ASP
Mixing
NF
Injection
Wells
35. James Robinson, 2016
Emerging Membrane Technologies
• Organo-phobic / Oleo-phobic MF (PW)
• Current MF is susceptible to fouling by suspended oil droplets in PW coating the
membrane surface. Surface repulsion of oil droplets would enable less-frequent
membrane cleaning cycles and less intensive pre-treatment for dispersed oil removal
• Subsea Seawater MF, NF & RO (on the Seafloor)
• Placement of seawater treatment processes at the location of subsea injection wells
would enable farther off-sets from host facilities thereby allowing greater areal sweep
of the reservoir, while also reducing weight and footprint on the host production
facility
• Membrane Distillation (PW & Seawater)
• Membrane Distillation (MD) is a thermally-driven separation process, in which only
vapor molecules transfer through a microporous hydrophobic membrane. The driving
force in the MD process is the vapor pressure difference induced by the temperature
difference across the hydrophobic membrane.
36. James Robinson, 2016
James Robinson, P.E.
Experience
• Water Treatment
Engineering Advisor
• Chevron (2011-2015)
• BP (2000-2009)
• Water Management
Engineering Consultant
• Oxidane Engineering (2009-2011, 2015-present)
• Cypress Engineering (1991-2000)
Professional
• Professional Engineer
• Society of Petroleum Engineers
• Produced Water Society
Education
• B.S. in Civil Engineering (1990)
Louisiana State University
• M.S. in Engineering (1992)
Rice University
Contact
• jcr.tx@icloud.com
• (281) 384-3327