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College Station June, 2002
Texas A&M University
Design and History Matching of Waterflood/Miscible CO2
Flood Model of a Mature Field: The Wellman Unit, West Texas
Chair of Advisory Committee: Dr. David SchechterCommittee Members: Dr. Duane McVay and Dr. Luc Ikelle
byJose Rojas
Master of Science Candidate
College Station June, 2002
Texas A&M University
Content
• Research Objectives• Review of Geology• Historical Reservoir Performance• OOIP and Water Influx (Material Balance)• Simulation Model • Model Calibration – History Matching• Results: Primary Depletion
Waterflooding CO2 Injection • Conclusions and Recommendations
College Station June, 2002
Texas A&M University
Objectives
Revise and integrate data from the reservoir description todevelop a full field, three-dimensional black oil simulationmodel to reproduce via history matching, the historical performance of the reservoir under primary, secondary and tertiary stages of depletion
Secondly, develop a calibrated model that can be used to evaluate, design and plan future reservoir management decisions.
College Station June, 2002
Texas A&M University
Wellman Field
Midland
Horseshoe Atoll
Review Of Geology
Location
•Terry county, TX, along the Horseshoe Atoll reef complex that developed in North Midland during Pennsylvanian and early Permian time
College Station June, 2002
Texas A&M University Review Of Geology
Field is considered geologically unique, because it comprises twotypes of reef construction
Pennsylvanian Cisco Reef Permian Wolfcamp Reef
• Built in deep clear water• Large mound shape structure• Strong depositional dip• Water bearing
• Built in shallow muddy(turbid) water• Encroaching shales at the flank• Smaller cone-shape structure• Oil bearing
College Station June, 2002
Texas A&M University
• Wolfcamp deposited on top of the prominent Cisco Reef• Curved layers at the bottom, more horizontal in upper structure
Review Of Geology
Reef on Reef Depositional Model
• Structural Northeast – southwest cross section reveals the cone shaped structure
Top of Wolfcamp
Spraberry Sand
College Station June, 2002
Texas A&M University Review Of Geology
Structural Setting
• Oval shaped covering a productive area of 2100 acres
• Two local highs (dual, cone-shaped anticlinal structure)
Isopach Structure Map
Lithology
• Secondary Porosity to diagenesis- Intercrystalline- Vugular- Natural Fractures
• Carbonate reservoir (skeletal marine organisms)
NNN
College Station June, 2002
Texas A&M University Historical Reservoir Performance
Primary Depletion (1950 – 1979)
1) 1950-53 oil rate peaked 6 MSTBD
2) 1954 allowable restrictions oil rate reduced to 3, then 1.7 MSTBD
3) 1966 oil rate peaked 8 MSTBD
4) 1976-79 produced below Pb until reached minimum 1,050 psig
Pb at 1,248 PSI
1
2
3
4
5) 1976-79 GOR did not increase secondary gas cap formed. H2O cut: from 10 to 25%
5
Cum. Oil: 41.8 MMSTBRF: 34.6%
College Station June, 2002
Texas A&M University
Waterflooding (1979 – 1983)
Cum. Oil: 23.9 MMSTB
Sec. RF: 19.5%
H2O Inj
CO2 Inj
OWOC
H2O Inj
CO2 Inj
OWOC
H2O Inj
OWOC
1979 - four flank H2O injectors re-pressurize (MMP), re-dissolve part of the gas, displace oil upward
Waterflooding
• Pressure increased from 1,050 to 1,600 psig prior CO2 (1983) • Oil rate increased to 9 MSTBD
• Water cut from 25 to 40% GOR aprox. constant
• Water cut controlled by plug downs.
Historical Reservoir Performance
College Station June, 2002
Texas A&M University
H2O Inj
CO2 Inj
OWOC
H2O Inj
CO2 Inj
OWOC
H2O Inj
CO2 Inj
OWOC
1983-89 - Three crestal injectors to displace oil downward and reduce Sor
CO2 Injection (1983 – 1995)
• 1984-89, CO2 Inj. From 5 to 15 MMCFD.
• 1985, break water cut from 40 to 85%. (ESP’s, leaks, corrosion)
• GOR peaked to 3000 SCF/STB (mostly CO2)
• Pressure from 1600 to 2,300 peaked at 2,500 psig in 1994.
PrimaryDepletion
CO2
Injection
Waterflooding
Cum. Oil: 6.3 MMSTB
Ter. RF: 5.4%
Historical Reservoir Performance
College Station June, 2002
Texas A&M University
Bottom Water Drive
Original Reservoir Conditions
Sec. GasCap
Prod Prod
Bottom Water Drive
Before Waterflooding (1979)
Prod Prod
WIW WIW
Bottom Water Drive
Waterflooding (Before CO 2 Flood),1983
CO2 ICO2 I
WIWWIW
Prod Prod
Waterflood and CO2 Injection (1995)
Bottom Water Drive
Bottom Water Drive
Original Reservoir Conditions
Bottom Water Drive
Original Reservoir Conditions
Sec. GasCap
Prod Prod
Bottom Water Drive
Before Waterflooding (1979)
Prod Prod
WIW WIW
Bottom Water Drive
Waterflooding (Before CO 2 Flood),1983
CO2 ICO2 I
WIWWIW
Prod Prod
Waterflood and CO2 Injection (1995)
Bottom Water Drive
CO2 ICO2 I
WIWWIW
Prod Prod
Waterflood and CO2 Injection (1995)
Bottom Water Drive
WIWWIW
Prod Prod
Waterflood and CO2 Injection (1995)
Bottom Water Drive
Bottom Water Drive
Original Reservoir Conditions
Bottom Water Drive
Original Reservoir Conditions
Sec. GasCap
Prod Prod
Bottom Water Drive
Before Waterflooding (1979)
Prod Prod
WIW WIW
Bottom Water Drive
Waterflooding (Before CO 2 Flood),1983
CO2 ICO2 I
WIWWIW
Prod Prod
Waterflood and CO2 Injection (1995)
Bottom Water Drive
CO2 ICO2 I
WIWWIW
Prod Prod
Waterflood and CO2 Injection (1995)
Bottom Water Drive
WIWWIW
Prod Prod
Waterflood and CO2 Injection (1995)
Bottom Water Drive
Bottom Water Drive
Original Reservoir Conditions
Bottom Water Drive
Original Reservoir Conditions
Sec. GasCap
Prod Prod
Bottom Water Drive
Before Waterflooding (1979)
Prod Prod
WIW WIW
Bottom Water Drive
Waterflooding (Before CO 2 Flood),1983
CO2 ICO2 I
WIWWIW
Prod Prod
Waterflood and CO2 Injection (1995)
Bottom Water Drive
WIWWIW
Prod Prod
Waterflood and CO2 Injection (1995)
Bottom Water Drive
CO2 ICO2 I
WIWWIW
Prod Prod
Waterflood and CO2 Injection (1995)
Bottom Water Drive
WIWWIW
Prod Prod
Waterflood and CO2 Injection (1995)
Bottom Water Drive
Chronological Stages of Depletion
College Station June, 2002
Texas A&M University
OOIP and Water Influx Material Balance
Straight line Material Balance for Reservoir Without Gas Cap, m=0
0
10
20
30
40
50
60
0 0.05 0.1 0.15 0.2
Delta Bt, Rb/stb
Qp
, MM
ST
B
Qp Vs Delta Bt
Straight line Material Balance for Reservoir Without Gas Cap, m=0
0
10
20
30
40
50
60
0 0.05 0.1 0.15 0.2
Delta Bt, Rb/stb
Qp
, MM
ST
B
Qp Vs Delta Bt
N
Expected
Real
Straight line Material Balance for Reservoir Without Gas Cap, m=0
0
10
20
30
40
50
60
0 0.05 0.1 0.15 0.2
Delta Bt, Rb/stb
Qp
, MM
ST
B
Qp Vs Delta Bt
Straight line Material Balance for Reservoir Without Gas Cap, m=0
0
10
20
30
40
50
60
0 0.05 0.1 0.15 0.2
Delta Bt, Rb/stb
Qp
, MM
ST
B
Qp Vs Delta Bt
N
Expected
Real
• Lack of linearity
• Not Volumetric
• Most likely producing under influence of an aquifer
• Validate existence and influence of external energy (aquifer)• Use performance data and fluid properties prior waterflooding
Havlena and Odeh
College Station June, 2002
Texas A&M University
• Estimate and validate previous OOIP assessments
• Estimate water influx rate prior waterflooding
OOIP and Water Influx Material Balance
Hurst and Van Everdigen
Results
• OOIP (N) aprox 125 MMSTB• We10: approximately 8.0 MMRB
Final Aquifer Properties
H, Feet 68
K, md 25
, Fraction 0.9
Ro/Re 2
Ro, Feet 3000
Angle (f=1) 360
College Station June, 2002
Texas A&M University Simulation Model
H2O Inj
CO2 Inj
OWOC
H2O Inj
CO2 Inj
OWOC
H2O Inj
CO2 Inj
OWOC
Grid System
• Use of flexible grids: corner point, non - orthogonal geometry.
• K, direction subdivided in 23 layers based on porosity correlations (geological description)
• 27 x 27 gridblocks I,J direction
Full field, 3-D black oil simulation“Imex” – CMG
• Total 16,767 gridblocks
College Station June, 2002
Texas A&M University Simulation Model
3D – Structure Development
College Station June, 2002
Texas A&M University
Simulation Model Input Data
Production data
• Over 45 years of monthly cumulative oil, gas and water production from 47 wells was converted into daily rate schedules for simulation
• Model initially constrained by oil rates and water/CO2 injection rates
Pressure data
• Pressure measurements reveal good communication within the reservoir• Use of BHP corrected and averaged to a common mid-perforation• Static BHP seemed to be representative of the average reservoir pressure
0
500
1,000
1,500
2,000
2,500
3,000
3,500
4,000
4,500
A-49 M-53 J-57 A-61 S-65 O-69 D-73 J-78 F-82 M-86 M-90 J-94
Time, years
Bo
tto
m H
ole
Pre
ssu
re
(BH
P),
P
si
Unit 1-1 Unit 2-1 Unit 2-3 Unit 3-3 Unit 4-1 Unit 4-2
Unit 4-3 Unit 4-4 Unit 4-5 Un it 4-6 Unit 4-7 Unit 5-1
Unit 5-2 Unit 5-3 Unit 5-4 Unit 5-5 Unit 6-1 Unit 6-2
Unit 7-1 Unit 7-2 Unit 8-3 Unit 8-5 Unit 8-6 Unit 8-7A
Individual Static Bottom Hole Pressure
College Station June, 2002
Texas A&M University
• Use of isopach maps resulted from geological and petrophysical study in 1994
• Geological and stratigraphic correlation (Core vs Log data)• Quantify major rock properties• Lateral and areal continuity
Isopach Maps
• 60 geological contoured maps from gross thickness, porosity and NTGR were digitized
• Interpolation between contour allows model to be populated
Gross Thickness Porosity Net to Gross Ratio
Simulation Model Input Data
College Station June, 2002
Texas A&M University
Permeability
• Use previous estimates from correlations between open-hole logs and core measurements
K = 10^(0.167 * Core porosity – 0.537)
Simulation Model Input Data
Swc, aprox 20% for Ф = 8.5%Swc, aprox 20% for Ф = 8.5%
College Station June, 2002
Texas A&M University
Simulation Model Input Data
Fluid Properties
• Use PVT properties contained in previous lab and reservoir studies
• Bubble point: 1248 – 1300 psig• Rs, 400-500 SCF/STB• Oil Gravity, 43 API• OFVF, 1.30 RB/STB• Oil Viscosity, 0.4 cp• Black oil fluid type
Relative Permeability
• Special core analysis for core well No. 7-6 included measurements on only two samples with a low non-representative permeability
• Use functions derived from Honarpour’s correlation (past studies)
Initial Oil - Water Relative Permeability
00.10.2
0.30.40.50.60.7
0.80.9
1
0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8
Water saturation (Sw),fraction
Rela
tive
Perm
eabi
lity,
frac
tion
Krow
Krw
Initial Gas - Oil Relative Permeability
0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0.8
0.9
1
0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8
Gas saturation (Sg) fractionR
elat
ive
Per
mea
bili
ty, f
ract
ion Krg
Krog
Initial Oil-Water and Gas Relative Permeability
College Station June, 2002
Texas A&M University
Simulation Model Input Data
Capillary Pressure Data
• Only 4 samples, K > 1 md (Special core analysis)
Leverett's- J Function Vs. Water Saturation
0
1,000
2,000
3,000
4,000
5,000
6,000
7,000
8,000
0 10 20 30 40 50 60 70 80 90 100
Water saturation (Sw), percentage
J-
Fu
ncti
on
CC-76 H, K=18 md CC-77 H,K=161 md
CC-79 H,K= 9.07 md CC-86 H,K= 18 md
• Shape suggests lack of capillary transition zone
• Data normalized by Leverett J-function
• Good vertical communication capillary effect “not significant”
College Station June, 2002
Texas A&M University Model Calibration – History Matching
Objective: Validate the model adjusting the reservoir description until dynamic model match the historical production and pressures
• Weight and rank properties by level of uncertainty (quality, source, amount, availability of data)
Historical Responses to be Matched
• Fieldwide average reservoir pressure• Fieldwide production rates• Fieldwide GOR and Water cut• Arrival times• Individual responses (lesser degree)
Reservoir and Aquifer Parameters Level of Uncertainty
Aquifer Transmissibility, kh 9
Aquifer Storage, Φhct 9
Reservoir Transmissibility, kh 9
Reservoir permeability distribution, k 7
Chronological well completions 7
Oil-water and gas relative permeability, kr 6
Reservoir oil and gas properties 5
Mixing parameters 5
Capillary pressure functions, pc 4
Reservoir porosity and thickness 3
Structural definitions 3
Rock compressibility 2
Water– Oil – Contacts 2
Tuning uncertain propertiesinfluencing the solution
Sensitivity analysis simulation runs
Via
College Station June, 2002
Texas A&M University Results: Primary Depletion
• No aquifer modeled • Poor pressure response
First simulation runs
• Need of external energy “recognized”
College Station June, 2002
Texas A&M University Results: Primary Depletion
• Carter and Tracy “Analytic”
• MB case too strong (top)
• Aquifer size (Ф,h), trans. (K,h)
• Reference datum adjusted
• Influx 20% greater, best case
• Fetkovich, “Analytical Aquifer”
• First years not matched
• Radius ratio, K and Ф
Preliminary runs Aquifer Calibration
College Station June, 2002
Texas A&M University Results: Primary Depletion
Preliminary runs
• Water arrival time and cumulative did not match• Highest corresponds to MB• Poorest corresponds “no aquifer”
• Poorest corresponds “no aquifer”• Best pressure match “sharp gas increase”
• Secondary gas cap formed
Need for improvement was recognized !
College Station June, 2002
Texas A&M University Results: Primary Depletion
Most Uncertain Parameters influencing Production of Fluids
Model Calibration
Vertical TransmissibilityAquifer/reservoir• vertical arrays
Aquifer Properties• , h,k
Relative PermeabilityFunctions
• end points, shape, crit. sat
Re-interpretationCompletion intervals
• Plug-downs• GOR, water cut
cutoff
“K.H” TermProd / Inj Index
Uniform Mod.Fluid PVT
Local Absolute (K)Lesser degree
College Station June, 2002
Texas A&M University Results: Primary Depletion
Diagnosis
College Station June, 2002
Texas A&M University Results: Primary Depletion
Final Results
College Station June, 2002
Texas A&M University
Case OOIP (STB) Thesis
OOIP Ref. 2
OOIP Ref. 5
R.F (%)
Thesis
R.F (%)
Ref.2
OWOC Increase
(FT) Thesis
OWOC Increase
(FT) Ref.2
March_19_29 122.6 126 121.5 34.6 33.2 208 220
Testeardat 122.6 126 121.5 34.6 33.2 208 220
Jose_6 122.6 126 121.5 30.8 33.2 208 220
March_19_8 121.3 126 121.5 34.6 33.2 208 220
March_19_35 122.0 126 121.5 34.6 33.2 208 220
Results: Primary DepletionFinal Results
College Station June, 2002
Texas A&M UniversityResults: Waterflooding
H2O Inj
OWOC
H2O Inj
OWOC
• 4 producers converted to water injectors (1979)
• Injection below and above OWOC @ - 6,680 ft
• Located at the flank forming a perimeter belt
• Model primarily constrained by historical injection rate schedule
Injector Location
College Station June, 2002
Texas A&M UniversityResults: Waterflooding
Initial runs
• Green, one of the best cases from primary depletion match
• Blue, same with water injectors
• Pressure continued declining
• Adjustment “KH” term of the injectivity index to match constraint • Injection rate and volumes matched
Adjustment
• In spite of injecting the correct volume of water reservoir pressure continued declining
• Water and gas exceeded historical data (H2O: 47%)
Fluid production needsto be controlled !
Most Uncertain Parameters influencing Production of Fluids
Model Calibration
Vertical TransmissibilityAquifer/reservoir• vertical arrays
Aquifer Properties• , h,k
Relative PermeabilityFunctions
• end points, shape, crit. sat
Re-interpretationCompletion intervals
• Plug-downs• GOR, water cut
cutoff
“K.H” TermProd / Inj Index
Uniform Mod.Fluid PVT
Local Absolute (K)Lesser degree
College Station June, 2002
Texas A&M University Diagnosis
Results: Waterflooding
Model Pressure MapVoidage Replacement Ratio
College Station June, 2002
Texas A&M University Model Calibration for Final Pressure Match
Results: Waterflooding
Numerical aquifer
College Station June, 2002
Texas A&M University
Results: Waterflooding
Model fluid match
College Station June, 2002
Texas A&M UniversityResults: Waterflooding
WOC Movement
(a)
(b)
(c)
1950
1979
1983
208 ft
210 ft
College Station June, 2002
Texas A&M UniversityResults: CO2 Injection
H2O Inj
CO2 Inj
OWOC
H2O Inj
CO2 Inj
OWOC
H2O Inj
CO2 Inj
OWOC
Miscible Displacement
• Modification of the black oil sim.
• Pseudo-miscible option with no chase gas
• Based on the “Todd and Long- staff” theory
Highlights
• Modifies physical properties and flow characteristics of the miscible fluids
• Requires definition of new param.
• CO2 PVT prop., MMP, ωo(P)
College Station June, 2002
Texas A&M UniversityResults: CO2 Injection
Initial runs
• Abnormal increase in reservoir pressure • VRR greater than 1, correlates with sharp pressure increase• VRR decreased (1992) correlating with decrease in pressure
What is happening ?
College Station June, 2002
Texas A&M UniversityResults: CO2 Injection
Water Rate Solvent Rate
• Model is not able to reproduce rapid water rate increase (1986) • In 1986, insufficient water and solvent production results in a dramatic increase in reservoir pressure
Initial runs
College Station June, 2002
Texas A&M University
Most Uncertain Parameters influencing Production of Fluids
Model Calibration
Vertical TransmissibilityAquifer/reservoir• vertical arrays
• local refinements• Kv / Kh > 1
Aquifer Properties• , h,k
Relative PermeabilityFunctions
• end points, shape, crit. Sat• New set for middle reef
Account for ESP’s
Re-interpretationCompletion intervals
• Plug-downs• Include wells high
on the struct.
“K.H” TermProd / Inj Index
Uniform Mod.Fluid PVT
Local Absolute (K)Lesser degree
Results: CO2 Injection
Negative SkinStimulations - Acidizing
Kv areal distribution 2nd Relative permeability region
College Station June, 2002
Texas A&M University Diagnosis / adjustmentsResults: CO2 Injection
• Identification of abnormal individual performance
• Fluid saturation distribution
• Adjustment completion intervals
College Station June, 2002
Texas A&M UniversityResults: CO2 Injection
• Good pressure match “primary”. Lost during waterflooding, poor at CO2 Inj.
• Excess of H20 (waterflooding)
• Overall insufficient water and solvent production (tertiary), causing over- pressurization.
• Unsuccessful match after extensive model calibration
• Matching fluid production more accurately is required!
Sensitivity runs
College Station June, 2002
Texas A&M UniversityResults: CO2 Injection
Final match
• Daily oil rate primary constraint expanded to daily total liquid rate (oil + water)
• Match is preserved (primary, H2O Inj.)
• Water and H2O breakthrough matched
• Oil match sacrificed to match pressure
College Station June, 2002
Texas A&M UniversityResults: CO2 Injection
Final match
College Station June, 2002
Texas A&M University
Bottom Water Drive
Original Reservoir Conditions
Sec. GasCap
Prod Prod
Bottom Water Drive
Before Waterflooding (1979)
Prod Prod
WIW WIW
Bottom Water Drive
Waterflooding (Before CO 2 Flood),1983
CO2 ICO2 I
WIWWIW
Prod Prod
Waterflood and CO2 Injection (1995)
Bottom Water Drive
Bottom Water Drive
Original Reservoir Conditions
Bottom Water Drive
Original Reservoir Conditions
Sec. GasCap
Prod Prod
Bottom Water Drive
Before Waterflooding (1979)
Prod Prod
WIW WIW
Bottom Water Drive
Waterflooding (Before CO 2 Flood),1983
CO2 ICO2 I
WIWWIW
Prod Prod
Waterflood and CO2 Injection (1995)
Bottom Water Drive
CO2 ICO2 I
WIWWIW
Prod Prod
Waterflood and CO2 Injection (1995)
Bottom Water Drive
WIWWIW
Prod Prod
Waterflood and CO2 Injection (1995)
Bottom Water Drive
Bottom Water Drive
Original Reservoir Conditions
Bottom Water Drive
Original Reservoir Conditions
Sec. GasCap
Prod Prod
Bottom Water Drive
Before Waterflooding (1979)
Prod Prod
WIW WIW
Bottom Water Drive
Waterflooding (Before CO 2 Flood),1983
CO2 ICO2 I
WIWWIW
Prod Prod
Waterflood and CO2 Injection (1995)
Bottom Water Drive
CO2 ICO2 I
WIWWIW
Prod Prod
Waterflood and CO2 Injection (1995)
Bottom Water Drive
WIWWIW
Prod Prod
Waterflood and CO2 Injection (1995)
Bottom Water Drive
Bottom Water Drive
Original Reservoir Conditions
Bottom Water Drive
Original Reservoir Conditions
Sec. GasCap
Prod Prod
Bottom Water Drive
Before Waterflooding (1979)
Prod Prod
WIW WIW
Bottom Water Drive
Waterflooding (Before CO 2 Flood),1983
CO2 ICO2 I
WIWWIW
Prod Prod
Waterflood and CO2 Injection (1995)
Bottom Water Drive
WIWWIW
Prod Prod
Waterflood and CO2 Injection (1995)
Bottom Water Drive
CO2 ICO2 I
WIWWIW
Prod Prod
Waterflood and CO2 Injection (1995)
Bottom Water Drive
WIWWIW
Prod Prod
Waterflood and CO2 Injection (1995)
Bottom Water Drive
Chronological Stages of Depletion
College Station June, 2002
Texas A&M University
College Station June, 2002
Texas A&M University Conclusions
1. Original fluids in place (according to simulation): Oil: 127.1 MMSTB Water: 139.0 MMSTB Gas: 54.3 BSCF Model OOIP, proved to be in close agreement not only with past
estimations but also with the analytical solution of the material balance technique previously presented.
2. Cumulative water influx (8 MSTB) was estimated from application of the material balance theory and correlates quite well with water influx obtained in the “best case” being 8.5 MMSTB (first 10 years).
3. The natural aquifer greatly influenced production of fluids and consequentially, the predicted average reservoir pressure.
4. The initial set of aquifer parameters was derived analytically by the Hurst and Van Everdigen theory and finally tuned by sensitivity analysis
College Station June, 2002
Texas A&M University
5. The Carter and Tracy (analytic) method resulted as the best alternative to model the Cisco aquifer over the Fetkovich (analytic) and the numerical aquifer method.
Conclusions Cont….
6. The Cisco aquifer provided energy and supplied water that encroached uniformly advancing the WOC 208 ft (prior to waterflooding) and an
additional 210 feet (prior to CO2 injection) being in excellent agreement with field observations.
7. The use of a flexible grid system, honored the characteristic structureof the cone-shaped double anticline. The distorted grid blocks
allowed a good representation of Wellman Unit geological features.
8. Historical water production and breakthrough times were identified as one of the most difficult parameters to match and one that greatly
influenced the behavior of the predicted reservoir pressure response.
College Station June, 2002
Texas A&M University Conclusions Cont….
• A complete pressure match was achieved through primary depletion, waterflooding and CO2 injection, however the match on liquid production was compromised in order to tune the final pressure match.
• The results of this work provide the foundation for future research into this hydraulically complicated reservoir
College Station June, 2002
Texas A&M University Recommendations for Future Work….
• More research is recommended on the geology of the field with the aim of simplifying the total number of gridblocks, specifically the number of layers (23) by the use of some of the upscaling methods in the literature.
• Consider the use of pseudo-functions during simplification of the existing model to increase the accuracy when modeling the production of fluids.
• Place additional effort to update the current model by incorporating production and injection data from 1995 to the present time, thereby it can be used to assist future reservoir management decisions.
College Station June, 2002
Texas A&M University