7. Waste Options: Deep well injection Flashcards

1
Q

Deep Well Injection history

A

-in use since the 1950s by oil and gas for disposal of oil field brines

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2
Q

2 Reasons for injecting fluids into the subsurface formations

A

-increase pressures i oil and gas reservoirs that have been on production for some time
(P increases, production rates of Oil and Gas Increase)
-Disposal of LIQUID hazardous wastes

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3
Q

5 Classes of injection/disposal wells in Alberta

A
-based on type of fluid injected
Class IV
Class III
Class II
Class Ib
Class Ia
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4
Q

Class IV injection wells

A
  • direct injection into a reservoir (not a disposal well) –> SAGD
    eg. potable water, steam from potable water
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5
Q

Class III Injection well

A
  • injection of hydrocarbons, inert gases or other gases
  • purely used for storage of liquids in enhanced oil and gas recovery systems
  • Fluid types include solvents for enhanced oil recovery, sweet gas storage, emergency fuel supply
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6
Q

Class II injection well

A
  • injection or disposal of produced waters (mainly brines)

- brines originate from water produced during oil and gas production operations, water produced from solutions mining

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7
Q

Class Ib Injection well

A
  • disposal or produced water, specific oilfield waste streams and waste streams meeting specific criteria
  • regs provide liquids which can be disposed here
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8
Q

Class Ia Injection well

A
  • disposal of oilfield or industrial waste fluids
  • only waste to accept waste that’s not oil field waste
  • liquids must be tested prior to disposal and must meet all criteria in ERCB directive 50
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9
Q

Fluid Waste Criteria for DWI

A
  • pH between 4.5 and 12.5
  • substance doesn’t meet surface water discharge criteria
  • has a non-halogenated organic fraction of less than 10% by mass (except untreatable sand or crude oil/water emulsion, antifreeze or dehydration fluid)
  • has one or more halogenated organic compounds in a total combined concentration less than 1000 mg/kg
  • PCB concentration less than 50 mg/kg
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10
Q

Deep Well Injections regulated by:

A

ERCB directive 51, not Alberta Environment and Water

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11
Q

ERCB Regulations focus on 4 key areas

A
  • Wellbore integrity
  • Formation suitability for the disposal of fluids
  • Waste stream suitability
  • Reporting and manifesting
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12
Q

Wellbore Integrity

A
  • both initial and ongoing containment of the injected fluids in the disposal/injection zone
    • protection of ground water
    • conservation of hydrocarbons
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13
Q

Formation suitability for the disposal of fluids

A

-make sure injection/disposal zone will continue to confine the injected fluids with that single zone

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14
Q

Wellbore Design

A

must result in complete isolation of the disposal zone from all other formations and especially from useable groundwater aquifers

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15
Q

Well head

A

includes well head and casing pressure gages

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16
Q

Surface Casing

A

Must extend below all useable ground water aquifers

17
Q

Production Casing

A

Extends from surface to the base of the well

18
Q

Annulus

A

Between casing and injection tubing

19
Q

Packers

A

Isolates the annular fluids from the disposal/ injection fluids

20
Q

Wellbore Integrity is ascertained by logging/testing the well:

A
  • Prior to any fluids being injected into the disposal formation (if don’t meet this application will be denied)
  • During the life of the disposal well (ongoing monitoring to ensure hydraulic isolation of the injection/disposal zone from other zones)
21
Q

Initial logging/testing requirements include:

A
  • cement on top location logging
  • hydraulic isolation logging
  • casing integrity logging
  • initial pressure tests
22
Q

Cement top location logging

A
  • cement is used to hold the casing in place

- isolate various zones from one another

23
Q

Hydraulic isolation logging

A

-ensures isolation of disposal zone

24
Q

Casing integrity logging

A

-full length casing inspection to determine if corrosion is becoming an issue which can weaken the casing

25
Q

Initial pressure tests

A
  • test pressures up to about 7000 kPa for 15 min for all classes of wells
  • ensures no leaks will occur once injection starts
26
Q

Monitoring logging/testing requirements include (Class Ia wells):

A
  • recording of annular and injection pressures daily
  • hydraulic isolation logging every 5 years
  • formation pressure surveys yearly
  • packer isolation tests yearly
27
Q

Requirements for the disposal zone of fluids (relating to formation suitability):

A
  • porous (storage) and permeable zone (waste can flow)
    • sandstones/conglomerates
    • carbonates
    • unconsolidated sands
  • not fractured- may not be able to get hydraulic isolation
  • below useable groundwater zones
  • want formation waters to be saline
  • confined
  • deep
28
Q

Waste Stream Suitability

A

Injection fluids must be chemically compatible with both the formation fluid and the rock matrix

29
Q

Problems associated with deep well injection

A
  • Contamination of ground water aquifers if hydraulic isolation of the disposal zone is not maintained
  • Localized earthquakes because of increased subsurface pressure as fluids are injected