Geological Storage of CO 2 by Hubbert’s Force Potential and … · 2016-01-22 · Geological...

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Geological Storage of CO 2 by Hubbert’s Force Potential and Gravitational Force Potential and Gravitational Groundwater Flow Systems by K Ud W Ph D PG l P HG K. Udo Weyer, Ph.D., P .Geol., P .HG. WDA Consultants Inc. Calgary, Alberta, Canada Calgary, Alberta, Canada [email protected] 1 © 2010 K.U. Weyer

Transcript of Geological Storage of CO 2 by Hubbert’s Force Potential and … · 2016-01-22 · Geological...

Page 1: Geological Storage of CO 2 by Hubbert’s Force Potential and … · 2016-01-22 · Geological Storage of CO 2 by Hubbert’s Force Potential and GravitationalForce Potential and

Geological Storage of CO2 by Hubbert’s Force Potential and GravitationalForce Potential and Gravitational

Groundwater Flow Systems

by

K Ud W Ph D P G l P HGK. Udo Weyer, Ph.D., P.Geol., P.HG.WDA Consultants Inc.

Calgary, Alberta, CanadaCalgary, Alberta, [email protected]

1 © 2010 K.U. Weyer

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Purposep

• Show that pressure gradients are not the driving forces for subsurface flow of groundwater and all other fluids.

• Show how gravitational groundwater flow affects theShow how gravitational groundwater flow affects the long term geological storage and subsurface migration of CO2 and other fluids to the surface.

© 2010, K. U. Weyer2

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Common misconceptions in the treatmentCommon misconceptions in the treatment of subsurface fluid flow

• Water is incompressible • Fluid flow is driven by pressure gradients• Saltwater separates and sinks to the bottom of the system

because of its higher density• Aquitards ‘confine’ fluid movement to aquifers• More water flows in aquifers than aquitards• Recharge to artesian aquifers occurs only in outcrops• Underground ‘buoyancy forces’ are always directed vertically• Underground buoyancy forces are always directed vertically

upwards

© 2010, K. U. Weyer3

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Arrangement of presentationArrangement of presentation• Driving Forces for Fluid Flow in the Subsurface• ‘Buoyancy Forces’ = Pressure Potential Forces• Groundwater Flow SystemsGroundwater Flow Systems• Upward-Discharging Salt Water and Brine• Crystal Geyser, Utah: Natural discharge of CO2 into a River • Downward-Directed Pressure Potential Forces: ‘Buoyancy Reversal’• Trapping of CO2 under Conditions of ‘Buoyancy Reversal’ and its

Maintenance

© 2010, K. U. Weyer4

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Driving Forces for FluidDriving Forces for Fluid Flow in the Subsurface

© 2010, K. U. Weyer5

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Continuum Mechanics Reservoir Engineering

(Muskat, 1937: velocity potential)

versus

Force PotentialOil Exploration and Regional Groundwater Flow

(Hubbert, 1940, 1953, 1957)

© 2010, K. U. Weyer6

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Muskat’s Velocity Potential ΦMuskat, 1937: Φ = energy / unit volume; dimension [L2T-1]Muskat, 1937: Φ energy / unit volume; dimension [L T ]

Φ = k/μ (p - ρgz)Φ k/μ (p ρgz)

Muskat, 1937, integrated the gravity as a vertical body force within the equation for velocity potential, making the equation unsuitable for 2D and 3D flow fields inthe equation unsuitable for 2D and 3D flow fields in anisotropic media.

© 2010, K. U. Weyer7

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Muskat’s [1937] non-physical approach Muskat s [1937] non physical approach to fluid flow in the subsurface

volumetric = intrinsic dynamic ● pressureflow vector permeability viscosity gradientp y y g

[Muskat, 1937, The Flow of Homogeneous Fluids Through Porous Media]formerly known as “The Bible” of reservoir engineering

This is not a valid expression of Darcy’s equation.

© 2010, K. U. Weyer8

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Darcy’s Law [1856]

flow = area ● hydraulic ● head conductivity difference

© 2010, K. U. Weyer9

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Pressure gradients are not the motor f ti f fl id i th b ffor motion of fluids in the subsurface

978

afte

r Wey

er, 1

9

© 2010, K. U. Weyer10

Water flows with and against the pressure gradients.

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Sand model of groundwater flow

© 2010, K. U. Weyer11

Sand model of groundwater flow

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Demonstration of groundwater flow through geologic cross-section

© 2010, K. U. Weyer12

g g g gFor animation on the web see: http://www.wda-consultants.com/sm-03.htm

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S h ti f t fl t ti h d bSchematic of water flow penetrating hydrocarbon (or CO2) accumulations and caprock

U d Fl D d Fl

A d h l b d i i bl b i h d b

Upward Flow Downward Flow

A sandstone-shale boundary is an impermeable barrier to hydrocarbons or CO2 trapped in the sandstone, but is not an impermeable barrier to the passage of water in either direction (see Hubbert, 1953, p.1975-1979).

13© 2010, K. U. Weyer

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Offshore hydrocarbon seepsOffshore hydrocarbon seeps are used in the exploration for offshore hydrocarbon fields, much the same way as theymuch the same way as they used to be applied in the early days of onshore hydrocarbon explorationexploration.

The assumption that h d b fi ld fhydrocarbon fields are safe areas for CO2 storage is therefore not a priori correct, b t d t b ibut needs to be proven in each particular case.

© 2010, K. U. Weyer14

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Ch f i k t d diti ithi iChanges of sink towards source conditions within a reservoir during petroleum production, EOR and subsequent CCS

© 2010, K. U. Weyer15

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Continuum Mechanics vs. Force Potential

Continuum Mechanics Force Potential

Oil Industry: Reservoir Engineering

Source: Muskat, 1937

Oil Industry: Exploration GeologistsGeneral: Groundwater Flow Systems

Source: Hubbert, 1940,1953,1957,1969Source: Muskat, 1937

p = energy / unit volume [ML-1T-2]

hydraulic forces: grad p

, , , ,

Φ = energy / unit mass [L2T-2]

hydraulic forces: grad Φ

area considered: reservoirs only area considered: all rocks from groundwater table to selected depth,including reservoirs

The methods of Hubbert’s Force Potential should be applied to Carbon Sequestration

16© 2010, K. U. Weyer

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Application of Hubbert’s Force Potential to Groundwater Flow

Potential = Energy / Mass [L2T-2]

forces = -grad Φ

Hubbert, 1940: Theory of groundwater motionHubbert, 1953: Entrapment of petroleum under hydrodynamic conditions

17 © 2010, K. U. Weyer

, p p y yHubbert, 1957: Darcy’s law and the field equations of the flow of underground fluids

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Hubbert’s [1940] Schematic Diagram ofHubbert s [1940] Schematic Diagram of Gravitational Groundwater Flow

1940

afte

r Hub

bert,

1

© 2010, K. U. Weyer18

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Under natural conditions, the fresh water energy field of hydraulic potentials

determines the state of energy for all fluidsdetermines the state of energy for all fluids in the subsurface [Hubbert, 1953], for

groundwater, salt water, oil, gas, and CO2g g 2

19© 2010, K. U. Weyer

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Vectoral addition of hydraulic forces

after Weyer, 1978

The direction of the total hydraulic force is fundamentally different

© 2010, K. U. Weyer20

from the direction of the pressure potential force

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The Princeton model on leaking abandoned wells in Albertaabandoned wells in Alberta

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• The model is based on pressure and the assumption of hydrostatic conditions. Potentials (energy/mass) and gravitational forces are thereby not taken into account

• Forces are: “pressure drive and buoyancy” [Scherer et al., 2005, p.828]

fro B W

© 2010, K. U. Weyer21

p y y [ p ]• Gravitational groundwater flow systems are not incorporated

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Mathematical models by IPCC, 2005: restricted to capillary and buoyancy forcescapillary and buoyancy forces

05IP

CC

, 200

The above models ignore gravitational groundwater flow systems, and, by their caption, misrepresent b f d ibl l ill f Si f d l t i di t d

© 2010, K. U. Weyer22

buoyancy forces and possibly also capillary forces. Size of model area not indicated.

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‘Buoyancy Forces’ =Buoyancy Forces Pressure Potential Forces

© 2010, K. U. Weyer23

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Hydraulic forces (grad Φ) under hydrostatic and hydrodynamic conditions

There is no principle difference between hydrostatic and hydrodynamic forces

hydrostatic and hydrodynamic conditions

hydrostatic and hydrodynamic forces. Hydrostatic conditions (A) are a special hydrodynamic condition wherein the pressure potential gradient is equal in size

h i i l f b i i i hto the gravitational force, but pointing in the opposite direction. Hence, the hydraulic forces Φ are equal to 0 and the water does not flow.not flow.

Under hydrodynamic conditions (B), the water flows and the fresh water pressure potential gradient is either not pointing in

after Hubbert, 1953: Entrapment of Petroleum Under Hydrodynamic Conditions, Fig. 4

p g p gopposition to the gravitational gradient g, or is of different magnitude.

© 2010, K. U. Weyer24

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Schematic derivation of pressure potential forces (‘buoyancy forces’) for oil, gas, and salt water

under hydrostatic conditions• Submerged salt water, fresh water, oil and gas show

different pressure potential gradients as shown in the diagramdiagram

• The salt water has a greater density than fresh water and sinks vertically downwards

• Submerged fresh water does not move up or downwards in a hydrostatic fresh water fieldy

• Oil and gas have lower density than fresh water and float vertically upwards

• The combined force vectors on right side of the diagram combine the pressure potential forces of fresh water oil and gas They are all directedfresh water, oil, and gas. They are all directed vertically upwards because the fresh water pressure potential force is directed vertically upwards. The direction of the fresh water pressure potential force determines the direction of the pressure potential forces for oil and gas. That is the reason why oil andforces for oil and gas. That is the reason why oil and gas float vertically upwards under hydrostatic conditions.

• Exactly the same happens under hydrodynamic conditions, except that the direction of the fresh water pressure potential force usually takes a

© 2010, K. U. Weyer25

water pressure potential force usually takes a non-vertical direction in space.

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Comparison of the direction of pressure potential forces (‘buoyancy forces’) under hydrostatic and hydrodynamic conditions

• The hydrostatic part of the diagram shows the pressure potential vectors to be directed vertically-upwards while the hydrodynamic part of the diagram shows a non-vertical direction of pressure potential vectors for all fluids: fresh water, salt water, oil, and gas.

• The direction of any so called ‘buoyancy force’• The direction of any so-called buoyancy force is determined by the direction of the pressure potential force of fresh water which, under hydrodynamic conditions, may point in any direction in space.

• Division of the water pressure potential force• Division of the water pressure potential force by the density of the ‘buoyant’ fluid determines the size of its pressure potential force.

• The flow direction of the ‘buoyant’ fluid is determined by vectoral addition of the ‘buoyant’ pressure potential force and thebuoyant’ pressure potential force and the gravitational force as shown in the next slide.

© 2010, K. U. Weyer26

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Determination of flow directions for all fluids in the subsurface• The pressure potentials of fresh water

determine the pressure potentials for all other fluids (oil, gas, CO2, salt water) within the ubiquitous energy field created by fresh groundwatergroundwater

• The lower densities of oil and gas cause stronger pressure potential forces to maintain, within the freshwater field, the same energy status for the less dense fluids. gyThe pressure potential force of water is divided by the densities for oil and gas.

• Vectoral addition in turn leads to significantly differing flow directions within the same energy field as shown.

• Liquid CO2 has a density similar to that of oil at about 0.85 g/cm3.

• Salt water gradients were not shown in the

H bb t 1953 E t t f P t l U d

diagram by Hubbert. Slide 39 shows that ocean-type salt water has almost the same flow direction as fresh water.

© 2010, K. U. Weyer

Hubbert, 1953: Entrapment of Petroleum Under Hydrodynamic Conditions

27

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Comparison of hydrostatic and hydrodynamic conditions in subsurface fluid flowconditions in subsurface fluid flow.

Ф : hydraulic potentiald Ф h d li f

© 2010, K. U. Weyer28

grad  Ф : hydraulic force

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Groundwater Flow SystemsGroundwater Flow Systems

© 2010, K. U. Weyer29

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Tóth’s [1962] analytical calculation of groundwater flow systems in a cross-section with homogeneous and isotropic lithology

Tóth, 1962

Total elevation gain is approximately 150 m over about 6 km; the amplitude of hills is approximately 15 m; penetration depth of local groundwater flow systems is up to 900 m, intermediate groundwater flow system about 2400 m, and regional groundwater flow system over 3000 m (lower border limited by model depth)system over 3000 m (lower border limited by model depth).

© 2010, K. U. Weyer30

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Effect of buried higher-permeable layer upon groundwater flow pattern and location of recharge and discharge areasp g g

[1]

[2]

after Freeze and Witherspoon, 1967

Under natural conditions, twice as much water can flow within the aquitard (downward and upward flow)

© 2010, K. U. Weyer31

, q ( p )as compared to the aquifer (lateral flow). (See case [2].)

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Schematic diagram of groundwater flow with aquitard over buried aquiferq

ft W 1996

Twice as much groundwater flows through the aquitard (vertically downwards and upwards) as through the aquifer (laterally). The head distribution in the aquifer is a replica of the topography. In recharge areas the potential in the aquifer is lower than that at the groundwater table, in discharge areas the potential in

f

after Weyer, 1996

© 2010, K. U. Weyer32

the buried aquifer is higher than that at the groundwater table.

32

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Plan view of groundwater flow systems penetrating an aquitard

1969

Alb

inet

& C

otte

z,

Recharge and discharge areas are outlined by differences in hydraulic heads (water levels) in piezometers. Subtracting head values in the aquifer from those at the groundwater table. Negative values indicate areas of upward flow through aquitard and discharge. They are

afte

r

g p g q g yhatched and shown in yellow.

© 2010, K. U. Weyer33

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Erroneous assumptions about regional groundwater flow 1

H bb t 1953 E t t f P t l U d H d d i C ditiHubbert, 1953: Entrapment of Petroleum Under Hydrodynamic Conditions

Hubbert restricted flow to the aquifer. Knowledge about groundwater flow systems penetrating aquitards only became available more than a decade later (Freeze and Witherspoon, 1966, 1967).

© 2010, K. U. Weyer34

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Erroneous assumptions about regional groundwater flow 2p g g

Aft IPCC S i l R t C b Di id C t d St 2005 Fi 5 25After IPCC Special Report on Carbon Dioxide Capture and Storage, 2005, Figure 5.25

IPCC, 2005 missed Tóth’s (1962) paradigm shift, and the associated groundwater flow through aquitards, about forty years after its publication. It also refers to the outdated concept of up-dip migration.

© 2010, K. U. Weyer35

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Upward-Discharging Salt Water and BrineUpward Discharging Salt Water and Brine

© 2010, K. U. Weyer36

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Case 1: Münchehagen landfill [SAD], Germany

Digital Elevation Model [DEM]

yer,

1996

afte

r Wey

The DEM shows the position of the cross-section A-B, the Rehburg Hills, the landfill (SAD), borehole

© 2010, K. U. Weyer37

226, and the river Ils. The size of the DEM is about 22 km (E-W) by about 18 km (N-S).

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Discharge of saline water at the Ils river (natural discharge) and at the Münchehagen landfill site (pumping-induced coning).

er L

üdek

e, 1

987

afte

Investigators at the site discovered what they called a “coning effect” for salt water of ocean-type salinity. They did not realize that the connection to the Ils river was natural discharge of saline water and the flow

© 2010, K. U. Weyer38

towards the landfill was pumping-induced discharge. Note location of borehole 226 in inset.

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2D-vertical model of groundwater flow directions in cross-section A-B in the Münchehagen landfill area

er, 1

996

afte

r Wey

e

Geologic cross-section taken from 1:25,000 geologic maps. Calculated groundwater flow directions

© 2010, K. U. Weyer39

Geologic cross section taken from 1:25,000 geologic maps. Calculated groundwater flow directions were based on the groundwater table (following topography) and estimated permeability contrasts.

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Cross-section A-B showing flow lines calculated by 2D-vertical mathematical model2D vertical mathematical model

• SAD = Münchehagen landfill• Laterally-compressed flow lines y

as returned by model calculation; vertical exaggeration 30:1

• One of the two upward flow lines of saline water enters the river Ils di l Th hdirectly. The other passes beneath the SAD landfill at 50 m depth below ground.

• Due to higher permeable layer, lateral flow of shallow and deeplateral flow of shallow and deep flowlines converge towards river Ils.

salt water fresh water

© 2010, K. U. Weyer40

after Weyer, 1996

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Occurrence of saline water in borehole 226 at a depth of about 50 b l d50 m below ground. • Conductivity and salinity of the saline water

is about that of ocean water.• Upward flow of saline water to about 50 m• Upward flow of saline water to about 50 m

depth due to higher permeable layer abovethat depth (see permeability distribution indiagram: 1.3 x 10-6 m/s vs 6.8 x 10-7 m/s).

• Due to this higher-permeable layer, lateralg p y ,flow of shallow and deep flow linesconverge and flow towards the river Ils.

• Water levels in diagram indicate downwardflow in local flow system with fresh waterand upward flow in the regional saline flowsystem.

• The occurrence of salt water is coincidental.in the sense that a very similar flow pattern

ld ith f h t l F

[Gronemeier et al 1990 Fig 7]

would emerge with fresh water only. Forexplanations, see the next slide.

© 2010, K. U. Weyer41

[Gronemeier et al, 1990, Fig.7]

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Why is fresh water modeling suited to determine the flow lines of saline seawater?determine the flow lines of saline seawater?

• Freshwater determines the field of the potential in the subsurface (see slide 17).

• With a density of 1.03 g/cm3, the vectoral pressure potential force [(grad p)/ρs] for this ocean-type saline water is very similar in magnitude to that of fresh y ggroundwater with a density of 1.00 g/cm3 and has the same direction.

• Thus, the flow directions are very similar for ocean-, ytype saline groundwater and fresh groundwater.

• This has been verified by the occurrence of saline water at a depth of about 50 m below ground inwater at a depth of about 50 m below ground in borehole 226 and in the model results (see slide 37).

© 2010, K. U. Weyer42

after Weyer, 1996

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Case 2: Upward discharge ofUpward discharge of saturated brine near Salt River, NWT, Canada

• Saturated [~350 g/l; density 1 3 / 3] b i di h i~1.3 g/cm3] brine discharging

upwards beside a creek• Salt deposit is caused by

precipitation of salt not byprecipitation of salt not byevaporation of brine.

© 2010, K. U. Weyer43

picture: K.U.Weyer, 1977

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Case 3: Southern shore of Great Slave Lake, NWT, Canada

© 2010, K. U. Weyer44

Open borehole discharging saline waterpicture: K.U.Weyer, 1977

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© 2010, K. U. Weyer45

- locations of salt water and brine discharge [cases 2 + 3]

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Crystal Geyser Green River UtahCrystal Geyser, Green River, Utah

Field example of natural discharge of CO2 by deep seated regional groundwater flow systems

© 2010, K. U. Weyer46

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Crystal Geyser on the bank of the Green River, Utah

© 2010, K. U. Weyer47

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Crystal Geyser erupting

© 2010, K. U. Weyer48

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Demonstration of deep groundwater flow with dissolved CO2entering a surface water body from underneath

© 2010, K. U. Weyer49

entering a surface water body from underneath.

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Downward-Directed Pressure Potential Forces:

‘Buoyancy Reversal’

© 2010, K. U. Weyer50

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Directions ofDirections of gravitational and pressure potential forces at ‘Buoyancyforces at Buoyancy Reversal’

grad Φ

ρ1

- g

- grad p

= hydraulic force

= gravitational force

= pressure potential forceρ g p p p

M difi d ft W 1978

© 2010, K. U. Weyer51

Modified after Weyer, 1978

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Field example: Swan Hills area, AlbertaK. U. Weyer, 20060208

© 2010, K. U. Weyer52

Field example: Swan Hills area, Alberta

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Digital Elevation Model [DEM] of the Swan Hills area, Alberta, one of the places where ‘Buoyancy Reversal’ was measured in the field

The geologic cross-section A-A’ is marked as a red line. At the sites A,B, and C the occurrence of

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e geo og c c oss sec o s a ed as a ed e e s es , , a d C e occu e ce o‘Buoyancy Reversal’ was determined to occur within the Clearwater-Wilrich aquitard.

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Geologic cross-section A-A’.

Substantial limestone and dolomite aquifers occur beneath the Clearwater-Wilrich Aquitard [the layer with field-measured ‘Buoyancy Reversal’]. The regional groundwater flow systems penetrate through the Clearwater-Wilrich Aquitard into deeper aquifers and, under natural conditions, move towards the

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t e C ea ate c qu ta d to deepe aqu e s a d, u de atu a co d t o s, o e to a ds t eregional discharge area, the Athabasca River valley.

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‘Buoyancy y yReversal’ atDEM Site A

‘Buoyancy Reversal’ within the Clearwaterwithin the Clearwater-Wilrich Aquitard

Hitchon et al, 1989

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Trapping of CO2 under Conditions of ‘Buoyancy Reversal’ and its Maintenance

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Trapping of CO2 under conditions of ‘Buoyancy Reversal’

Schematic pressure-depth relationship at (1) a natural occurrence of Buoyancy Reversal, and subsequent pressure pattern during (2) oil production, (3) carbon sequestration, and (4) mitigation of Buoyancy Reversal through pumping water from beneath the CO2 layer

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2(or other sources) and injecting it above the caprock

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Conclusion

Subsurface fresh water force fields determine the flow direction for fresh water, salt water, oil, gas, and CO2. , , , g , 2Therefore, knowledge of gravitational systems of groundwater flow is imperative for understanding the long-term movement of oil gas and CO in thelong-term movement of oil, gas, and CO2 in the subsurface as well as the monitoring and maintenance of injected CO2 .

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THE END

K. Udo Weyer, [email protected] , y @

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