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POLYMER FLOODING IN WILMINGTON OIL FIELD, RANGER ZONE, FAULT BLOCK V. by Robert Crowder SHALLOW AQUIFERS AND SURFACE CASING REQUIREMENTS FOR WILMINGTON AND BELMONT OFFSHORE OIL FIELDS. by Larry Olson CALIFORNIA DEPARTMENT OF CONSERVATION Division of Oil & Gas Publication No. TR22 I I

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Page 1: POLYMER FLOODING IN WILMINGTON OIL FIELD, … · polymer flooding in wilmington oil field, ranger zone, fault block v. by robert crowder shallow aquifers and surface casing requirements

POLYMER FLOODING INWILMINGTON OIL FIELD, RANGER

ZONE, FAULT BLOCK V.by Robert Crowder

SHALLOW AQUIFERS ANDSURFACE CASING REQUIREMENTS

FOR WILMINGTON ANDBELMONT OFFSHORE OIL FIELDS.

by Larry Olson

CALIFORNIA DEPARTMENT OF CONSERVATION

Division of Oil & Gas

Publication No. TR22

I I

Page 2: POLYMER FLOODING IN WILMINGTON OIL FIELD, … · polymer flooding in wilmington oil field, ranger zone, fault block v. by robert crowder shallow aquifers and surface casing requirements

POLYMER FLOODING IN WILMINGTONOIL FIELD, RANGER ZONE, FAULT BLOCK V.

by Robert Crowder

SHALLOW AQUIFERS AND SURFACECASING REQUIREMENTS FOR WILMINGTON

AND BELMONT OFFSHORE OIL FIELDS.by Larry Olson

A pubtica tion of the

California Division of Oil & Gas

sacramento1978

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ABOUT THE AUTHORS

Robert Crowder is an Oil and Gas Engineer withthe California Division of Oil and Gas at Long Beach.He earned a Bachelor of Science degree in Petro­leum Engineering from the University of SouthernCalifornia.

Bob worked as a Reservoir Engineer for WesternGulf Oil Corporation before joining the division in 1949.He is a California registered geologist.

Larry Olson is an Oil and Gas Engineer withthe California Division of Oil and Gas at LongBeach. He received a Bachelor of SCIence degree ingeology from the University of Southern California.Prior to his state service, he was employed byWood-Gallahan 01/ Company, United GeophysicalCorporation, and Lane-Wells Company (now DresserAtlas Corporation).

In 1965, Larry was appointed to the positIon of Engi­neering Geologist with the Department of Water Re­sources where he specialized in groundwater studies.He joined the Division of all and Gas in 1970. Larry isa California registered geologist.

ii

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CONTENTS

SECTION A - POLYMER FLOODING IN WILMINGTON OIL FIELD, RANGER ZONE,FAULT BLOCK V.

POLYMER FLOODING 1WILMINGTON OIL FIELD 1

Ranger Zone 2Fault Block V 2

POLYMER FLOODING IN FAULT BLOCK V 5Waterflooding 5Polymer Flooding _ 5

Early Performance 5Well Stimulation 5Final Results 5

CONCLUSIONS 7SELECTED REFERENCES 8

- -~ -~ ~----_. - - --- - -- - . '~-.~•• -........ - :.-t- •• .-. ~- --_ ...._. -_. r- ••• - - •

SECTION B - ,ALLOW619U!EER§ AN§ sUBEAgE CASING REaUIREMEN~ FOR• ILMINGT NAND BELM NT OFFSHORE Oil FIELDS.

PURPOSE 11STUDY AREA , 11,GBQUNDWAT~R LOCATION 11GROUNDWATE~ OUA~ 11HYDROLOGIC UNITS ANP SHALLOW AQUIFE8§ 11

, GaspurAqwler 13• 200-Foot Sand Hvdroloqic Unit 14• 4OD-Foot Gravel Hydrologic Unit 14• Silverado Hydrologic Unit 14• Pico HYdrologic Um1 15

BASE OF F8~~H~ 15JOp OF FRE ~ 15DOMINGUEZ GAP BARRIER PROJECT 15

8g~gr~,~~~~ ..~~.~~~~.~~.~':~~ .. ::::::::::::::::::::::::::::::::::::::::::~; .SELECTED REFERENCES 21

iii

Page 5: POLYMER FLOODING IN WILMINGTON OIL FIELD, … · polymer flooding in wilmington oil field, ranger zone, fault block v. by robert crowder shallow aquifers and surface casing requirements

Figure 3.Figure 4.Figure 5.Figure 6.

ILLUSTRATIONS

SECTION A - POLYMER FLOODING IN WILMINGTON OIL FIELD, RANGER ZONE,FAULT BLOCK V.

FIGURES

Figure 1. Wilmington oil field 2Figure 2. Onshore and offshore segments, Fault Block V 3Figure 3. Cross section A-B, Fault Block V .4Figure 4. Injection and production graph 5Figure 5. Polymer flood production graph 6Figure 6. Polymer flood graph 6

TABLES

Table 1. Reservoir data and fluid properties 2

SECTION B - SHALLOW AQUIFERS ANP SURFACe CASING ReqUIREMENTS FORWILMINGTON AND BELMONT OFFSHORE OIL FIELDS.

FIGURES

Figure 1. Study area: Wilmington oil field. onshore andoffshore areas, and Belmont Offshore oil field 12

Figure 2. Typical electric log for study area. Water salinityvalues for each aquifer 14Cross section A-B 16

~QotQY~ ~ ~~~ ~~~ ~b..~i~' 18

i~~Ji~iit~iis=c~~;~~;~ 19on the ase 0 e Irs competen formation 20

TABLES

Table 1. Series, formation, thickness; and lithology of hydrologic~n}~e study !iJea 13

Table 2. cr' eria for water guali1¥ 14.k

- --" ... .--. - . . - .-~-'. ----.--.- --. .• ."'f' _. '':.. '. -~., f ....- •

IV

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SHALLOW AQUIFERS AND SURFACE CASINGREQUIREMENTS FOR WILMINGTON

AND BELMONT OFFSHORE OIL FIELDSa

by L. J. Olson

PURPOSE

Vast. available quantities of fresh groundwater.partially stored within Wilmington and Belmont Off­shore fields. played a vital role in the development ofthe Los Angeles area. Today. these groundwater sup­plies remain critically important.

This study is intended to add data to groundwaterprote~tio~ programs for Los Angeles and environs byinvestigating shallow aquifers inside the study areaand addressing surface casing requirements for oiland gas wells drilled in the onshore portion of Wil·mington oil field. In the study area. the shallow aqui­fers and the uppermost and lowermost horizons offresh groundwater were identified and delineatedand the first competent formation suitable for cement~ing surface casing was mapped.

STUDY AREA

The report study area includes onshore and off­shore portions of Wilmington oil field. Belmont Off­shore oil field. and an area slightly northeast of thesefields (Fig. 1).

Wilmington oil field produces more oil than anyother oil field in California. Furthermore. the water­flood repressuring operation conducted in the field isthe largest of its type in the world. The field is southof Los Angeles. located in the Long Beach-Los Ange­les Harbor area. Proved acreage consists of 6.980acres onshore and 6.025 acres offshore. Belmont Off­shore field. with 760 proved acres. is the southeaster­ly extension of Wilmington oil field.

GROUNDWATER LOCATION

Fresh groundwater in the study area is contained

aManuscript submitted November 1977.

within the upper 2.000 feet of sediments that are con­fined laterally between the structural uplift of thePalos Verdes Hills and the Newport-Inglewood faultzone. Figure 3. a cross section through part of thestudy area. shows the relative positions of the variousshallow hydrologic units and aquifers. Cross sectionlocations are also shown on Figures 4,5. and 6. Table1 lists the series. formation. thickness. and lithology ofeach hydrologic unit in the study area.

GROUNDWATER QUALITY

Study area groundwater quality was determinedthrough the use of electric logs. An electric log resis­tivity reading of30 ohm-meters or more in the shal­low aquifers was considered to indicate fresh water.The assumption was made after comparing resistivityreadings on electric logs to known formation water­quality information available from chemical analysesin certain wells.

To approximate groundwater salinities. the resis­tivity of the formation fluid was calculated from thespontaneous potential curve on the electric log. Fig­ure 2 is a typical electric log showing salinity valuesof water in each aquifer.

Based on the California Department of Water Re­sources (DWR) criteria. groundwater evaluated inthis study was considered fresh when it containedless than 3.000 parts-per-million (ppm) in totaldissolved solids (TDS) (Table 2).

HYDROLOGIC UNITS ANDSHALLOW AQUIFERS

Hydrologic units are comprised of intervals of wa­ter-bearing sediments containing interbedded aqui­fers and aquicludes. Aquifers are permeablesediments that consist mainly of sand and gravel.Most aquicludes are composed of impermeable sedi-

Page 7: POLYMER FLOODING IN WILMINGTON OIL FIELD, … · polymer flooding in wilmington oil field, ranger zone, fault block v. by robert crowder shallow aquifers and surface casing requirements

0'I"I

SCALE IN IJIlES

w<!>'s

"~--

Study area: Wilmington oil field. onshore and offshore areas. and Belmont Offshore oil field,Figure 1.

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Table 1. Series. formation. thickness. and lithology of hydrologic units in the study area.5

,8

ThicknessFormation Hydrologic (feet)

Series and member (groundwater)Avg. Max.

Lithologyunit

Gravel. gravelly sand.River channel Gaspur Aquifer 70 110 cobbles. overlain by clayey

Holocene gravels silt and sand.

{unconformity}Sand. medium to coarse.

Q; unnamed 200-foot sand 150 250variable thickness: clay:

0. interbedded silt. fine sand:0.::> gravel lenses.

- I---{ unconformity)Sand. coarse. uniform.

CD 400-foot gravel 150 300highly permeable; minor

Pleistocene '6 gravel bed; overlain by silt:-0 clay.E-0 San Pedro

-(unconformity)'-

c CD Sand. coarse. thick-bedded.I~

0. 250 3500. highly permeable:Silverado ::>jCD gradational to fine. silty

I~~Q; sand. or silt. southward:~ 150 250 blue clay.52I (unconformity)

Sand. fine to medium.

I Ithick-bedded. silty.

Pico 500 700 interbedded with silty clay1'- i and shale: moderately

I ~I "P,CO" permeable: marine.BASE OF FRESH WATER

PiioceneShale. gray-green.

200 300 saturated with brackishwater.

- f--(unconformity)Sandstone. greenish-gray.

Q; poorly consolidated.~ "Repetto" 1.000 - marine; interbedded ."..<"52 siltstone and shale. Oil

bearing.

Sands:cne. g'ay a:-1d brown.

i rnar;r-:e; ;nter~edded vVI:hPuente [4.000 i - j'OG8i:',{ ....... eil-,:"'d:....:,'6~eC

jsdts;:C'i~ a:-:d sha:e 0·;

i bear'~g.; ,

Miocene !

Nodula- i S~a:€. r·ard, dense:

shale 900 - I s, :scor:e 'r\)ith Inteioedded, sandswne Oil bearing.

Monterey I,,

! I

!Schistj SChist conglomerate and

II 25 I -congl. breccia. Oil bearing.

CretaceousCatalina Schist - -

or older Schist. hard. well-indurated.

ments. largely clay.Hydrologic units in the study area are named after

locally named aquifers within each unit: 2eo-footsand. 400-foot gravel. Silverado. and Pico. The Gas­pur Aquifer is sufficiently uniform and consistentso that only the aquifer portion of the hydro­logic unit is discussed below and shown on Figure2 and Table 1.

Gaspur Aquifer

The Gaspur Aquifer consists of sand and graveldeposited in the Los Angeles River Channel. The Gas-

SHALLOW AQUIFERS AND SURFACE CASING REQUIREMENTS

pur transects the study area and lies roughly betweenthe easterly limits of the Los Angeles River Channelon the east and'Henry Ford Avenue on the west.The top and bottom of the Gaspur Aquifer are ap­proximately 80 and 180 feet below sea level. respec­tively. The type section of this aquifer is described byZielbauer. et al. 8

Fresh water in the aquifer has been degradedto about 15.000 ppm by seawater intrusion and bythe percolation of oilfield brines and other indus­trial waste waters disposed of In surfacesumps. concentration ponds. and disposal pits. espe-

~ Superior figures refer to a list of references at the end of this report.

13

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'Drinking water usually contains less than 1.000 ppm in TD5.

Table 2. DWR criteria for water quality.

20Q-Foot Sand Hydrologic Unit

Figure 2. Typica! electric log fOf study area. Water saklityvalues for each aauifer.

The 400-foot gravel hydrologic unit extendsthroughout the study area. The unit consists of ma­rine and continental deposits of uniform. coarsesands and gravels from 50- to 75-feet in thickness andof interbedded clay. The top and bottom of the unitare located at depths of approximately 200 feet and500 feet below sea level. respectively.

The 400-foot gravel is an important source of freshgroundwater (1.000 ppm) at the northerly margins ofthe study area because of the high yield (200-to­2,100 gallons per minute) obtained from wells pro­ducing from aquifers in this unit. However. the qualityof water in this unit has been degraded throughoutthe southerly portion of the area (20.000 ppm), eitherfrom seawater intrusion and local industrial wastes orfrom native saline water 8 Native saline water degra­dation is thought to result from connate brines trap­ped in the less-permeable portions of the freshwateraquifers. The connate brines are released and de­grade the fresh water as pressure differentials are al­tered and/or landward groundwater gradientsestablished.

unit merges with. and is in hydraulic continuity withthe Gaspur Aquifer in areas where the Los AngelesRiver trench became incised in the 20o-foot sand( Fig. 3 ). Three-to-four sand beds and alternating.clay beds comprise the 200-foot sand. The top andbottom of the 200-foot sand unit are generally foundat depths of 25 and 200 feet below sea level. respec­tively.

The quality of the groundwater in the 200-foot sandhas been degraded to about 15.000 ppm throughoutmuch of the study area. most likely by seawater intru­sion and by local industrial waste water. 8 However,fresh water can be found in this unit along the north­ern margins of the study area as well as in all the otherhydrologic units and aquifers.

40Q-Foot Gravel Hydrologic Unit

Silverado Hydrologic Unit

The Silverado hydrologic unit is composed of twomajor aquifers that are easily definable and are locallyseparated by a clay. or clayey silt, about 50 feet thick.Both the upper and lower Silverado Aquifers consistof sands and gravels that grade southward into apredominance of silts. clayey silts. and blue clays.Permeability becomes so severely reduced thataquifer portions of the Silverado hydrologic unitno longer exist in these areas. The top and bot­tom of the Silverado unit are approximately 600feet and 1,100 feet belOW sea level, respectively.The type section of tr-"s unit ;s described in referenceNO.1

The Srlve acio unit is the principal freshwatersource orr of tne study area.There is no evidenceOf seaVvater .rTusion; however. the determination ofwater Qua;:" i'om electric logs in the southern por­tions of the studY area is greatly impaired due toincreased clay content within the aquifers. The qual-

Excellent to goodGood to injuriousInjurious to unsatisfactory

o to 1,0001,000 to 3,000

3,000 and over

The 200-foot sand hydrologic unit extends through­out the study area, except where it was eroded entire­ly and Gaspur Aquifer sediments redeposited. The

Parts Per Million (ppm)of

Total Dissolved Solids (TDS) Irrigation Water Quality'or Chemical Constituents

cially during the early development of the Wilming­ton and Long Beach oil fields.s Subsequently. thedegraded Gaspur water has been useful only to theoil industry as a source of waterflood injection waterfor deeper oil zones.

Today. the water is usable only for some industrialpurposes. s For this reason. protection of fresh waterin the Gaspur Aquifer is not considered as importantas protection of higher-quality. deeper groundwa­ters.

ISERIES

APPROXIMATE

ITYPICAL

HYDROLOGIC TDS IN PPM OF ELECTRICFORMATION UNITS FORMATION WATER LOG

I~.OUJ('.ENE AIVEA CHANNel GASPUR '~.(X't.1 IIGRAvELS AQUIFER( LOCAlLY ME~G!:C A-"t-:. )

~ /'0../' ,N1RiJOED a..... SE.;.W,:.T!;'" ,, ~ J UNNAMED ~FOOT

~1\

SAND

20.000 l Ii4~FOOT (LOCALLY INTRUDED)

5GRAVEL BY SEAWATER

-- :00

~BASE OF FIRST

- --OOMPETeNT-FORMATi6N----wC)0 SAN1-Ul PEDRO ;>Wo. 8"- <

~~~O\S 700

ffi~&~

"'00

~~~~ws 1,700.Ja~

700

PICO'500"PIca"

a:Ii'"-:J

------- __!~-f~~~~~___

3.000

~a: >-\!i "REPETIO" -- 30.000 r'<=- .?'X(,

S 1.1! ,~, I

14 CALIFORNIA DIVISION OF OIL AND GAS

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ity of local water is apparently better in the upperSilverado Aquifer (700 ppm) than in the lower (1,700ppm), as indicated in Figure 2.

Pica Hydrologic Unit

The Pico freshwater hydrologic unit. which is thedeepest. is present uniformly throughout the area.Although fresh water is not usually produced fromthe unit because of the depth, the fresh water shouldnevertheless be protected for future use. The Picaunit consists of alternating fine sands, silts and clays.or shales The top of the aquifer is found about 1.200feet belo\-'! sea level, and the base of freshwater sandsis about 1,700 feet below sea level within this aquifer.The quality of water In the Pico unit is generally verygood (700 po ), however. the quality becomes tran­sitionall poo er with depth near the base of freshwater (3.OC<J PD },

BASE OF FRESH WATER

e Dese of fres water in the study area coincides. '8 ~se of the deepest. uniformly deposited,

fre a.er 8q iter In the Pico hydrologic unit. Thebase I; es water IS a prominent feature on electricI ar s (~. w as the K marker in the northwester-ly s ' f ilrrll gton field. Stratigraphically,t ,e tBse c:' '-es" water !S found in the "Pica"Fo'i1"1-<i:: (F Q 2J,

Fi_l e.:l. :: ,r _::or'OlFS drawn on the base of freshwater : s_';....~s!edy portion of Figure 4 extendsno - eas1en "r-:, ,he Belmont Offshore field andincludes pc~ 0' ~""e Sea! Beach oil field.

OP OF FRESH WATER

Conto rs o~ ere top of fresh water areshown 0 F' e 5 can lOurs are shown wherefresh water e -' .... olisly 'rOTl the groundsurface do," n '-' :"'6 oaS€ ill "esh water in the north­erly portio ,$ '~...,~ 2'~c - .. e e- contours areshown were "e:::- ;-'::~-,-"'5~e' S '_'6',a rD. salinewater I, t e SO:...:--er- DC-: c~:

Saline ",'a:e-' -=~'! -_"E$'"' ::--~-'owa-e'sdue ,0

DOMINGUEZ GAP BARRIER PROJECT

In February 1971. a recharge project known as theDominguez Gap Barrier Project was begun by the LosAngeles County Flood Control District to halt seawa­ter intrusion into shallow aquifers. The alignment ofinjection wells for this project is shown on Figure

SHALLOW AOUIFERS AND SURFACE CASING REOUIREMENTS

5. Currently, Colorado River water is being injected atthe rate of 212,000 barrels per day into 29 injectionwells. The water is being injected into the mergedGaspur Aquifer and 200-foot sand at the rate of ap­proximately 108,000 barrels per day and into the 400­foot gravel at about 104.000 barrels per day.

The extraction of water by oil operators for water­flood operations from these shallow aquifers on theseaward side of the barrier is thought to be beneficialto the barrier project as water levels must be higherat the barrier than on the seaward side for the barrierto be effective. To date, the project has been only mod­erately successful.

SURFACE CASING REQUIREMENTS

At a depth suitable for pressure control. surfacecasing must be cemented into reasonably consolida­ted or competent strata to provide anchorage forblowout prevention equipment. In the study area. aseries of poorly consolidated sands and gravels ex­tends from just below the surface to a depth of about500 feet on the onshore portion. This series is under­lain throughout most of the field by a sandy claystonethat is at a suitable depth and sufficiently compactedand impermeable to be considered a competent rockunit in which to cement surface casing.

A typical electric log of the study area shows theshallow sand and gravel aquifers and this competentbed (Fig. 2). Figure 6 shows contours drawn on thebase of the competent bed; therefore. the contourscan be used to determine the depth at which surfacecasing will be cemented,

Surface casing requirements on the offshore drIll­ing islands in Wilmington and Belmont Offshorefields were established as the result of a pr;or 'nvesti­gation and are shown on Figure 6.

CONCLUSIOI\JS

Fresh groundwater in most oil fields is subject or,!,to degradation by poorer-quality waters migratingfrom below the base of fresh water. In portiofls of the\/Ili'mlngton and Belmont Offshore oil fields. freshgroundwater is subject also to degradation by poore­quality waters migrating from above the fresh wate

The first competent formation suitable for the an­chorage of surface casing in Wilmington oil field a,jBelmont Offshore oil field can be adequately deFne­ated with the use of electric logs,

ACKNOWLEDGMENTS

The author thanks Dennis Allen and Mel W, ~-::'the Long Beach Department of Oil Proper:~s ':­helpful commentary during the preparation 0' --cO -2­

port.

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CHAMPLIN PETROLEUM CO. CHAMPLIN PETROl.EUM CO. CHAMPLIN PETROLEUM CO.UP 271 A UP 314-RB !. "'-"8

A=-~" ""n--------l'r---------------~ELr------------'~'r:------------~-----~--------- ~---~--- L _~~~~~ ~__~~__~ GASPUR t AOUIFER

200-FOOT SANO HYOROLOGIC "'-' UNIT ~

~~~~~~ t400-F'OOT GRAVEL

HYDROLOGIC ~UNIT

)

FllESH WATER AQUIFERS

Figure 3. Cross section .A:-B. Wilmington oil field.

16 CALIFORNIA DIVISION OF OIL AND GAS

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TO 5720

SURFACE CASING REQUIREMENTS

Pl,.IOCENE

Pl,.IOCENE:

JOO

200

<Xl

300 GOO 900 l200 1500 l800

I4MlZONTAl SCALE IN FEET

17