university report on effectiveness of glensol as oil remediation additive

24
Evaluation of GEOR 1 as an Additive for Enhanced Oil Recovery Prepared by: Professor Andrew Hurst Dr Stephen Bowden Dept Geology and Petroleum Geology, University of Aberdeen, Aberdeen Scotland 06 July 2009

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A research report by the University of Aberdeen on the GLENSOL Oil Remediation Additive - Evaluation of GEOR 1 as an Additive for Enhanced Oil Recovery

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Page 1: University Report on Effectiveness of GLENSOL as Oil Remediation Additive

Evaluation of GEOR 1 as

an Additive for Enhanced

Oil Recovery

Prepared by: Professor Andrew Hurst Dr Stephen Bowden Dept Geology and Petroleum Geology, University of Aberdeen, Aberdeen Scotland 06 July 2009

Page 2: University Report on Effectiveness of GLENSOL as Oil Remediation Additive

Evaluation of GEOR 1 for EOR

1

Page Summary 2 Introduction 6 Experimental Method 10 Results

Recovery Efficiency 13Fractional Flow analysis 17Notes on Areal Sweep efficiency 21

Conclusion 23

Abbreviations cp; centipoises

EOR; Enhanced oil Recovery

GEOR 1; Glensol mixture used for experiments

HO; heavy oil

M; mobility ratio

Page 3: University Report on Effectiveness of GLENSOL as Oil Remediation Additive

Evaluation of GEOR 1 for EOR

2

Summary Water flooding with GEOR 1 significantly enhances recovery of heavy oil. The

presence of a low concentration (5 parts per million) increases the amount of oil

recovered and reduces watercut. Relative to flooding with coldwater (20 deg C)

or hotwater (>85 °C) flooding with GEOR 1 brings forward production of heavy

oil.

A single GEOR 1 additive is effective for both saltwater and freshwater. Many

surfactants and emulsifying agents achieve very high levels of oil recovery but

GEOR 1’s efficiency at low concentrations and in both salt- and freshwater set it

apart. These two distinguishing features suggest the potential to succeed in the

field where other chemical methods of enhanced oil recovery have failed.

Previous chemical methods of enhanced oil recovery have depended on

laboratory studies to adjust and optimise surfactant solutions prior to field

application. GEOR 1’s efficiency at low concentrations combined with its

improved economic efficiency would help to mitigate the marginal nature of

chemical EOR methods: e.g. surfactant loss would be less significant

economically and should increasing the concentration of GEOR 1 to improve

recovery be necessary this need not significantly impact project-margins.

Results for preliminary coreflood experiments are summarised in Table 1.1 and

1.2. During all experiments a flood with coldwater (20 deg C) was performed to

drive a ~10000 cp heavy oil from a beadpack (the primary oil recovery phase).

Subsequent to this an EOR method is applied (flooding with GEOR 1or hotwater

or an extended flood with coldwater). The EOR phase was extended by flooding

with an equal pore volume. For both cold- and saltwater, enhanced oil recovery

by flooding with GEOR 1 greatly increased oil recovery and reduced watercut

relative to continued flooding with coldwater. Increases in oil recovery and

reductions in watercut achieved by GEOR 1 compare favourably or exceeded

those of hot water.

Page 4: University Report on Effectiveness of GLENSOL as Oil Remediation Additive

Evaluation of GEOR 1 for EOR

3

Images of the beadpack before and after flooding with GEOR 1 in Table 1.1 and

1.2 show the recovery of oil from bypassed regions. Relative to other methods

GEOR 1 appeared efficient at accessing zones of bypassed oil. GEOR 1 was

originally developed to remove heavy oil residues to remediate contaminated

land and clean surfaces. In this application GEOR 1 acts rapidly, penetrating

asphaltic deposits to clean oil from surfaces. This ability appears to transfer to a

dynamic environment at the laboratory-scale, and would be crucial at the field

scale if it improved the access of an EOR fluid to oil bypassed by the initial water

flood.

Page 5: University Report on Effectiveness of GLENSOL as Oil Remediation Additive

Evaluation of GEOR 1 for EOR

4

Table 1 Summary of results

Oil Recovered†

Watercut during EOR‡

Prim

ary

EOR

Exte

nded

% EOR

††

Low

est

Ave

rage

Red

uctio

n

Image before EOR phase

‡‡

Image after EOR phase

Freshwater

GEOR 1 5 μL/L

33

27

70

67

93

90

37 (55)

40 (60)

64

60

67

67

-10

-15

Coldwater

27

27

37

43 55

10 (30)

16 (37)

80

85

82

85

+ 5

+11

Hotwater >70 ºC 80 – 85 ºC

27

40

46

13

16

65

64

85

78

-28

-28

Hotwater 85 ºC

63 – 36 (57)

55 71 -38 -10

Page 6: University Report on Effectiveness of GLENSOL as Oil Remediation Additive

Evaluation of GEOR 1 for EOR

5

Table 1 Continued

Oil Recovered†

Watercut during EOR‡

Prim

ary

EOR

Exte

nded

%

EOR ††

Low

est

Ave

rage

Red

uctio

n

Image before EOR phase‡‡

Image after EOR phase

Saltwater

GEOR 1 5 μL/L

35 72 83 37 (54)

40 51 -31

Coldwater

40 50 10 (20)

50 66 +27

†Oil Recovered = the % of oil initially in place recovered. Primary recovery = % recovered after waterdrive; EOR = % recovered after equal volume of water to primary phase used to implement EOR technique; Extended = % recovered after extension of EOR phase. Approximately equal pore volumes used for each experiment. †† % EOR = % of oil initially in place recovered by first EOR technique, number in brackets is % enchantment in oil recovery. ‡ Water cut during EOR . Note that for extended flooding there is no reduction, hence this number is positive. ‡‡ Water is entering from the top of the page and oil exiting from wells at the bottom. Coloured lines identify regions of different shading, where shading is being used as a proxy for oil saturation. Blue is highest saturation and yellow lowest.

Page 7: University Report on Effectiveness of GLENSOL as Oil Remediation Additive

Evaluation of GEOR 1 for EOR

6

1.1 Introduction, aims and objectives Experiments were designed and conducted to test under laboratory conditions

whether there is evidence that GEOR 1, a chemical additive, has the potential to

enhance the direct recovery of heavy oil from reservoir rocks. The background for

the experimental work is a history of successful applications of GEOR 1 to

dispersal of heavy-oil pollution, remediation of oil-contaminated sand and

cleaning and unblocking of oil transport infrastructure (pipelines and storage

tanks). The success of these downstream applications coupled with their cost

effectiveness and environmental friendliness encouraged Glensol, the

manufacturers of GEOR 1, to evaluate possible use of the additive to enhance oil

recovery from natural reservoir rocks. GEOR 1 was successfully tested by

Glensol as an extraction method for mined and quarried tar and oil sands. If

significant improvement in heavy-oil recovery is possible by using a chemical

additive it opens the way for step changes in the recovery of heavy oil both in

terms of recovery efficiency and cost per barrel of oil recovered.

The aim of this study is use simple laboratory experiments to verify that a low

concentration of GEOR 1 added to water can enhance the recovery of heavy oil

from reservoirs. Recovering heavy oil from the subsurface in a dynamic

environment is very different to extracting bitumen from sand at the surface.

Therefore specific objectives are required to benchmark any enhancement in

recovery observed for GEOR 1 compared to extended flooding with coldwater

and hotwater, with particular attention being paid to factors unique to flow through

porous media. These factors are the rate of oil recovery relative to chosen

benchmarks, and how much water is produced along with a given volume of oil.

Additional objectives were to observe the behaviour of GEOR 1 in both salt and

freshwater systems and differentiate GEOR 1 from previous methods of

chemical-enhanced oil recovery.

Specific questions to answer are:

Page 8: University Report on Effectiveness of GLENSOL as Oil Remediation Additive

Evaluation of GEOR 1 for EOR

7

• Can GEOR 1 enhance oil recovery?

• Is GEOR 1 stable and effective in both fresh and salt water?

• How efficient is GEOR 1 in comparison to alternative methods of EOR?

• How does GEOR 1 improve upon other chemical methods of EOR?

Positive outcomes for the experiments above provide a basis for planning and

designing field tests of GEOR 1 in conventional heavy-oil reservoirs. The

experiments are designed to give oil-field operators a clear indication of the likely

benefit of using GEOR 1 in a commercial context.

Page 9: University Report on Effectiveness of GLENSOL as Oil Remediation Additive

Evaluation of GEOR 1 for EOR

8

1.2 Previous chemical EOR Although there is a considerable literature on chemicals that enhance oil recovery

there have been few successful commercial projects. General textbooks on

reservoir engineering tend to characterise chemical methods of enhanced oil

recovery as being economically marginal and technically complex, although

rarely for a common reason.

Foremost is that the cost of the surfactants can be expensive relative to the value

of any increase in oil recovery. This is further compounded by the possible loss of

surfactants to the reservoir formation during floods. Furthermore in many field

situations it has been difficult to bring the injected water containing EOR-

chemicals into contact with bypassed oil – the injected water containing EOR

chemicals simply flows around regions that contain residual oil.

Technical problems are caused the sensitivity of surfactant properties?? to

differing reservoir formation water chemistry and mineralogy, which necessitate a

design stage to specifically tailor a combination of surfactants and their co-

surfactants for particular reservoir characteristics. A miscalculation or false

assumption about reservoir rock and fluid properties at an early design stage has

the potential to cause failure for a chemical EOR project at the field scale.

Therefore in addition to the costs of implementing a field-scale EOR project a

considerable investment is also necessary at the design stage, thus a chemical

EOR project is inherently risky, may take along time to bring to fruition and even

longer to pay back a financial investment.

The chemical composition of GEOR 1 is confidential and thus it is hard to place

within the schemes typically used to characterise chemical EOR techniques.

Previous characterisations of EOR treatments similar to GEOR 1 include low and

high concentration surfactant floods, techniques that form surfactants using

chemicals already present in the oil (alkali flooding) and those that use

Page 10: University Report on Effectiveness of GLENSOL as Oil Remediation Additive

Evaluation of GEOR 1 for EOR

9

microbially produced biosurfactants. Although GEOR 1 is used at low

concentrations, and forms water in oil micro emulsions, the producers of GEOR 1

believe that GEOR 1 does not fit easily within any currently used classification.

Page 11: University Report on Effectiveness of GLENSOL as Oil Remediation Additive

Evaluation of GEOR 1 for EOR

10

2.0 Experimental method A microfluidic beadpack was adapted to allow the preliminary evaluation of water

flooding with GEOR 1 as a method of enhanced oil recovery for heavy oil. During

experiments the bead-pack was flooded with heavy oil and to promote the aging

of the system to an oil-wet state it was warmed at 30 ºC. The device was cooled

to room temperature before use. Two or more phases of recovery were used.

The first phase comprised primary recovery by water drive. During this stage

coldwater (20 ºC) was used. Second and subsequent phases comprised flooding

by one of three techniques; 1) coldwater (20 ºC), 2) hotwater between 70 to 85

ºC or 3) water with a 5 μL/L (5 ppm) concentration of GEOR 1. The beadpack

was videoed during the experiments and still-images were point-counted to

measure water saturation and the volume of fluids exiting the bead pack. The

methodology is summarised in figure 2.1. Table 1 lists the experiments

performed for the evaluation of GEOR 1 as a heavy oil recovery additive and the

details of additional experiments whose results are presented here for evaluation

purposes.

Table 2.1 Experiments used for report Water type EOR method Other details Freshwater GEOR 1 5 μL/L concentration

GEOR 1 duplicate Coldwater comparison Hotwater comparison experiments at 70, 80 and 85 ºC

Saltwater GEOR 1 5 μL/L concentration Coldwater comparison

Heavy Oil and Water The oil used is from Siljian (Sweden) and has an asphaltene + resin content of 36

%, an API value of 18 o/ ~10 000 cp. Tap water (TDS < 500 mg/L) was used for

freshwater floods and seawater for saltwater floods (TDS ~ 35 000 mg/L). The

same stock solution of GEOR 1 was used to make up saltwater and freshwater

Page 12: University Report on Effectiveness of GLENSOL as Oil Remediation Additive

Evaluation of GEOR 1 for EOR

11

solutions of 5 ppm concentration. GEOR 1 was not explicitly tailored or adapted

for the heavy oil and bead pack used in this study.

1) Channel with bead trap

2) Channel packed with beads

3) Oil flown into channel

4) Water flown into channel

5) Volume of oil and water in draining wells counted

800 μm

6) Before and after images of gravel pack analysed

1) Channel with bead trap

2) Channel packed with beads

3) Oil flown into channel

4) Water flown into channel

5) Volume of oil and water in draining wells counted

μm

6) Before and after images of gravel pack analysed

Bead diameter/ Grain size: 22 μmPorosity: ~ 46 %

~ 48 μm

1) Channel with bead trap

2) Channel packed with beads

3) Oil flown into channel

4) Water flown into channel

5) Volume of oil and water in draining wells counted

800 μm

6) Before and after images of gravel pack analysed

1) Channel with bead trap

2) Channel packed with beads

3) Oil flown into channel

4) Water flown into channel

5) Volume of oil and water in draining wells counted

μm

6) Before and after images of gravel pack analysed

Bead diameter/ Grain size: 22 μmPorosity: ~ 46 %

~ 48 μm

1) Channel with bead trap

2) Channel packed with beads

3) Oil flown into channel

4) Water flown into channel

5) Volume of oil and water in draining wells counted

800 μm

6) Before and after images of gravel pack analysed

1) Channel with bead trap

2) Channel packed with beads

3) Oil flown into channel

4) Water flown into channel

5) Volume of oil and water in draining wells counted

μm

6) Before and after images of gravel pack analysed

Bead diameter/ Grain size: 22 μmPorosity: ~ 46 %

~ 48 μm

Bead diameter/ Grain size: 22 μmPorosity: ~ 46 %

~ 48 μm

Figure 2.1 Photo graphs of device, and device before and after heavy oil is emplaced. Schematic diagram of method, showing different stages of an experiment.

Page 13: University Report on Effectiveness of GLENSOL as Oil Remediation Additive

Evaluation of GEOR 1 for EOR

12

Further details The device used in this study is not a micromodel but a micro-scale beadpack.

The key difference between the two techniques is that the beadpack creates true

3D tortuousity. The sodalime glass-beads used for experiments are a high

sphericity 22 micrometer diameter particle-size standard. Beads were introduced

through a channel 500 micrometers in breadth and ~46 micrometers in depth

until a pack of suitable length accumulated behind a gap filter. A picture of the

device and an image of the channel packed with beads is shown in figure 2.2.

Prior to use the pack was flushed with the water appropriate to the experiment

and the oil flown in to the pack at high flow rates/pressures. Prior to each

experiment the device was warmed to 30 oC to promote the adhering of oil onto

the beads to create an oil wet system.

During experiments the beadpack and the draining wells were videoed. Image

stills were point-counted to obtain water saturation and fractional watercut. When

measuring fractional water-cut, blocked-wells were excluded from calculation of

the parameter.

The device was fabricated at the James Watt-Nano Centre at the University of

Glasgow in cooperation with Professor Jonathan Cooper, experiments were

performed at the Dept of Geology and Petroleum, University of Aberdeen.

Page 14: University Report on Effectiveness of GLENSOL as Oil Remediation Additive

Evaluation of GEOR 1 for EOR

13

3.1 Heavy oil production using different EOR techniques Fluid flow during experiments was driven by the circulation of water with the data

collected including the volume of water injected into the device, the percentage of

water in the beadpack and the percentage of water exiting through the draining

wells1. These three measurements represent the time taken to recover a given

quantity of oil, the amount of oil recovered out of the total available and the

proportion of oil recovered relative to water.

The amount of oil produced per volume of injected water is plotted in figures 3.1.

and 3.2. Extended phases of recovery are denoted by dashed lines, but the

following discussion refers to the first phase of enhanced oil recovery. Relative to

flooding with hotwater and coldwater, flooding with GEOR 1 brought forward

production significantly. This is illustrated in figures 3.1.and 3.2 by GEOR 1

attaining its maximum displacement of oil for the circulation of lower pore

volumes in comparison to the hot- and coldwater experiments. Although the

overall volume of oil displaced is similar for both hotwater and GEOR 1, the key

difference is that GEOR 1 attains this far more rapidly (a Welge displacement

efficiency calculation suggests that to recover 70 % of the oil initially in place

more than 50 pore volumes of cold-freshwater would have to be circulated).

Fractional water-cut is a measure of the proportion of water produced relative to

oil. Because of the viscous and asphaltic nature of the heavy oil used during the

experiments water is significantly more mobile than oil during the primary water-

flooding. This is particularly notable for the cold-freshwater experiment where the

watercut was very high from an early stage in the experiment (figure 3.3). This

continued during extended flooding with cold-freshwater. In contrast coldwater

flooding with GEOR 1 added significantly reduced or suppressed the fractional

water-cut.

1 The higher the amount of water in the bead pack the greater the amount of oil displaced and recovered. Similarly; either water or oil is exiting the device so the greater the percentage of water exiting the device the lesser the percentage of oil recovered.

Page 15: University Report on Effectiveness of GLENSOL as Oil Remediation Additive

Evaluation of GEOR 1 for EOR

14

Wat

er s

atur

atio

n

5 ppm GlensolP

rimar

y R

ecov

ery

Hot water 75 to 80 ºC

Hot water 85+ ºC

Cold water

0

0.2

0.4

0.6

0.8

1

50

Pore volume injected subsequent to water break through

0 5 10 15 20 25 30 35 40 45

5 ppm Glensol

Cold water

0

0.2

0.4

0.6

0.8

1W

ater

sat

urat

ion

5 ppm GlensolP

rimar

y R

ecov

ery

Hot water 75 to 80 ºC

Hot water 85+ ºC

Cold water

0

0.2

0.4

0.6

0.8

1

50

Pore volume injected subsequent to water break through

0 5 10 15 20 25 30 35 40 45

5 ppm Glensol

Cold water

0

0.2

0.4

0.6

0.8

1

Figures 3.1 and 3.2. Graphs illustrating the recovery of oil by displacement with water. All unfilled symbols e.g. □, ○ etc refer to data for primary recovery phases. Shades symbols: ■▲ = data obtained for Glensol; ● = data obtained for cold water; + = data for hot water experiments. Dashed lines show extended flooding with Glensol.

Page 16: University Report on Effectiveness of GLENSOL as Oil Remediation Additive

Evaluation of GEOR 1 for EOR

15

Making a comparison between the hotwater and GEOR 1 flood experiment is a

little more complicated due to differential changes in volume in the oil phase

brought about by the two EOR techniques. It is likely that the overall reduction in

water-cut brought about by GEOR 1 is at least equitable to that of the hotwater

method if not greater. The minimal water-cut values attained by both techniques

are about 60 % for the freshwater/heavy oil system (figure 3.3.).

The saltwater/heavy oil system exhibited higher recoveries of the oil in place. The

presence of saltwater changes how heavy oil interacts with solid surfaces

(lowering the contact angle between the oil and water phases on wetting

surfaces). For an oil-wet system the decrease in contact angle or wetting

preference in saltwater can increase the mobility of the oil phase causing it to be

more easily mobilised than in a freshwater/heavy oil system. The effect of this

change in wetting preference can be seen by comparing figure 3.1 and 3.2,

where considerably more oil is mobilised during flooding with saltwater than with

freshwater.

The behaviour of GEOR 1 in a saltwater system is important in two respects: 1)

does GEOR 1 have an effect above that of using cold-saltwater alone and 2) is

GEOR 1 stable in both a fresh and saltwater environment? Firstly; flooding with

GEOR 1 in a saltwater system brought forward production significantly and

recovered more oil than cold-saltwater alone, but most notably it reduced water-

cut by about 40 % (figure 3.4). Secondly, the same GEOR 1 batch enhanced oil

recovery in both freshwater and saltwater/ heavy oil systems. This is highly

significant because it broadens the scope of applicability for GEOR 1-flooding as

an EOR-technique. Previous surfactant flood and EOR techniques that utilised

micellar solutions have been highly sensitive to formation water chemistry

requiring a pre-flush to condition formations or the tailoring of surfactants for

specific formation water chemistries. For both salt- and freshwater a GEOR 1

flood recovered 70 % of the oil in place.

Page 17: University Report on Effectiveness of GLENSOL as Oil Remediation Additive

Evaluation of GEOR 1 for EOR

16

5 ppm Glensol

Hot water 75 to 80 ºC

Hot water 85+ ºC

Frac

tiona

l wat

er c

ut

50

Pore volume injected subsequent to water break through

0 5 10 15 20 25 30 35 40 450

0.2

0.4

0.6

0.8

1

0

0.2

0.4

0.6

0.8

1

5 ppm Glensol

Hot water 75 to 80 ºC

Hot water 85+ ºC

Frac

tiona

l wat

er c

ut

50

Pore volume injected subsequent to water break through

0 5 10 15 20 25 30 35 40 450

0.2

0.4

0.6

0.8

1

0

0.2

0.4

0.6

0.8

1

Figure 3.3 and 3.4. Graph of the fraction of water exiting the device. All unfilled symbols e.g. □, ○ etc refer to data for primary recovery phases. Shades symbols: ■▲ = data obtained for Glensol; ● = data obtained for cold water; + = data for hot water experiments. Dashed lines show extended flooding with Glensol.

Page 18: University Report on Effectiveness of GLENSOL as Oil Remediation Additive

Evaluation of GEOR 1 for EOR

17

3.2 Further analysis Analysis of fractional flow curves provides a means to predict how water flooding

could operate at a bigger scale and also helps to characterise processes and

mechanisms that are enhancing oil recovery during a GEOR 1 flood.

The simplest estimate of water flood efficiency is the mobility ratio, a parameter

that balances the viscous forces of one fluid phase against another; a mobility

ratio less than 1 characterises an efficient water flood regime and a ratio much

greater than 1 is an inefficient water flood. The mobility ratio estimated for the

cold-freshwater experiment is approximately 500 following water breakthrough.

0

20

40

60

80

100

frac

tiona

l wat

er c

ut %

0

20

40

60

80

100

0 0.2 0.4 0.6 0.8 1Water saturation

Wct

%

M =

25

M =

2.5

M =

0.2

5M >

499

Primary Recovery Extended water flood

Sea water

Fresh water

0 0.2 0.4 0.6 0.8 1

Water saturation

0

20

40

60

80

100

frac

tiona

l wat

er c

ut %

0

20

40

60

80

100

0 0.2 0.4 0.6 0.8 1Water saturation

Wct

%

M =

25

M =

2.5

M =

0.2

5M >

499

0

20

40

60

80

100

0 0.2 0.4 0.6 0.8 1Water saturation

Wct

%

M =

25

M =

2.5

M =

0.2

5M >

499

Primary Recovery Extended water flood

Sea water

Fresh water

0 0.2 0.4 0.6 0.8 1

Water saturation Figure 3.5. Fractional flow behaviour of beadpack. ○● = data for primary and advanced stages of cold-freshwater flood (solid blue line); ∆▲ = data for primary and advanced stages of cold-saltwater flood (dashed blue line). Inset shows behaviour for idealised mobility ratios. Wct % = fractional water cut and M = mobility ratio.

Page 19: University Report on Effectiveness of GLENSOL as Oil Remediation Additive

Evaluation of GEOR 1 for EOR

18

The fractional water-flow behaviour for the coldwater experiments are shown in

figure 3.5. After a small amount of heavy oil has been produced (water has

displaced oil from the beadpack thus increasing water saturation), water-cut

values are high. For comparative purposes fractional water-cut curves are also

shown for idealised systems with lower mobility ratios. Comparison of these

systems to the one used for experiments highlights the difficulty of producing

heavy oil: if a watercut of 80 % represented the operating limit for a given field,

then production of a heavy oil deposit with the characteristics of the micro-

beadpack would have to cease after production of less than 10 % of the movable

oil in place. For the lowest mobility ratio illustrated, with a low viscosity oil this

would be about 50 % of the oil in place.

0

20

40

60

80

100

0 0.2 0.4 0.6 0.8 1Water saturation

70 oC80 oC85 oC

0

20

40

60

80

100

0 0.2 0.4 0.6 0.8 1Water saturation

Wct

%

Wat

er w

etOil

wet

frac

tiona

l wat

er c

ut %

0

20

40

60

80

100

0 0.2 0.4 0.6 0.8 1Water saturation

70 oC70 oC80 oC80 oC85 oC85 oC

0

20

40

60

80

100

0 0.2 0.4 0.6 0.8 1Water saturation

Wct

%

Wat

er w

etOil

wet

0

20

40

60

80

100

0 0.2 0.4 0.6 0.8 1Water saturation

Wct

%

Wat

er w

etOil

wet

0

20

40

60

80

100

0 0.2 0.4 0.6 0.8 1Water saturation

Wct

%

Wat

er w

etOil

wet

frac

tiona

l wat

er c

ut %

Figure 3.6. Fractional flow behaviour during thermal EOR, note wetability inversion at highest temperature. Blue line from figure 3.5. Redlines = thermal EOR data.. × = data for hot water at 70 oC, + = 80 oC and ○ = data for 85o C.

Page 20: University Report on Effectiveness of GLENSOL as Oil Remediation Additive

Evaluation of GEOR 1 for EOR

19

Figure 3.6 presents the results for the thermal EOR experiments. An initial a drop

in oil viscosity for temperatures in the 70 to 80 oC range increases recovery

marginally, but at temperatures greater than 85 oC a completely different

fractional flow behaviour results. The concave upwards graph is characteristic of

the fractional flow behaviour observed for low viscosity water-wet systems and

describes a situation where increased oil recovery is accompanied by relatively

minor increases in fractional water-cut.

0

20

40

60

80

100

0 0.2 0.4 0.6 0.8 1Water saturation

Fresh water Glensol

Sea water Glensol

frac

tiona

l wat

er c

ut %

0

20

40

60

80

100

0 0.2 0.4 0.6 0.8 1Water saturation

Fresh water Glensol

Sea water Glensol

frac

tiona

l wat

er c

ut %

Figure 3.7. Fractional flow behavior under Glensol flood.▲∆ & ●○ = data for 1st and 2nd stages of EOR with Glensol in freshwater. = 1st and 2nd stages of EOR with Glensol in saltwater. From figure 3.7 it is clear that flooding with GEOR 1 improves the fractional flow

regime; arrival of the GEOR 1 flood-front at the end of the beadpack is marked by

a reduction in water-cut as an oil bank is mobilised and moved through the

beadpack. This effect is most pronounced for the saltwater experiment. However

Page 21: University Report on Effectiveness of GLENSOL as Oil Remediation Additive

Evaluation of GEOR 1 for EOR

20

late stage extended flooding with GEOR 1 in saltwater is characterised by an

increasing water-cut, but the shape and gradient of the line on figure 3.7 does

not suggest a change in wettability as was observed for the thermal method.

Although the extended floods using GEOR 1 in freshwater do not water-out

during the duration of the experiment, eventually this would occur.

Flooding with a low concentration of GEOR 1 may increase recovery via a range

of mechanisms:

1) An increase in heavy oil mobility caused by strong and rapid surfacting

action; GEOR 1 has been shown (by Glensol) to act rapidly on asphalt

associated with tar-sands and pipe-line precipitated asphaltenes where it

rapidly penetrates through oil residues to reach the oil-surface interface.

Results presented here suggest that the same effect occurs in a dynamic

environment. This gives GEOR 1 not only access to residual oil, but

access to heavy asphaltic oil in marginally tighter regions of the beadpack

that would be difficult to mobilise using water alone.

2) The formation of water in oil microemulsions with reduced oil viscosity.

Microemulsions have a much reduced viscosity and swell to form a

continuous mobile oil phase. This process is most evident for the saltwater

experiments and is expressed as a notable decrease in water-cut and an

increase in recovery.

3) If GEOR 1 viscosifies water it may also increase overall recovery by

stabilising the flood-front and being better able to mobilise oil. This would

aid sweep efficiency and increase overall recovery.

Page 22: University Report on Effectiveness of GLENSOL as Oil Remediation Additive

Evaluation of GEOR 1 for EOR

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3.3 Areal Sweep Efficiency

Uns

wep

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1 mm

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Figure 3.8. Images showing increased areal sweep efficiency of Glensol flood at small scale. Top images show beadpacks after primary waterflood. Bottom images show photographs of pack after 1st EOR stage. Coloured overlays show outlines of unswept regions after primary flooding. After the coldwater flood areas outlined in blue still contain black oil. After Glensol flood the areas outlined in blue are better swept.

Field-scale areal sweep efficiency is a function of geological heterogeneity and

cannot be assessed at the scale of the experiments reported here. However

regions of bypassed oil did develop during most experiments. This is evident in

most experiments after the initial waterflood stage (see Table 1.1 and 1.2).

GEOR 1-floods are notably effective at accessing oil within these regions. This

can be further illustrated by overlaying the outlines of regions of bypassed oil

(shown as blue lines) onto to the bead pack after the application of the EOR

method (figure 3.8). After an extended waterflood many dark patches of oil

remain within blue lines as cold water can not easily shift the heavy oil in these

regions. This is not the case after flooding with GEOR 1 where the areas

enclosed by blue lines, although large, contain few patches of dark oil. GEOR 1

has somehow managed to access regions initially inaccessible to the water

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Evaluation of GEOR 1 for EOR

22

phase. A thermal method would be expected to mobilise heavy oil in such

regions by the conduction of heat, which does not depend on mass transfer to

lower viscosity. A chemical EOR method requires physical contact with the by-

passed or residual oil to mobilise it. The mobilisation of heavy oil in these regions

by GEOR 1 is therefore notable and attests to the rapid and deep surfacting

action of GEOR 1.

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Evaluation of GEOR 1 for EOR

23

4.0 Conclusion The presence of very low concentrations of GEOR 1 in injected water

significantly enhances the recovery of heavy oil during waterflood. Heavy oil

production is brought forward relative to coldwater flooding with fresh and saline

water with high recoveries obtained more rapidly when flooding with GEOR 1

than with hotwater or coldwater benchmarks. The positive affect of GEOR 1 in

both fresh and saltwater highlights its robustness as an additive.

To the best of our knowledge GEOR 1 has unique properties as a chemical

additive as it is efficient and effective in salt- and freshwater when used at low

concentrations sets it apart from previous chemical methods of enhanced oil

recovery. GEOR 1 is cost effective and not designed to be recovered for

reinjection thus mitigating an important element of economic risk in EOR projects.

For example, where loss of surfactant by adsorption onto reservoir surfaces is

encountered during surfactant flooding this could feasibly be mitigated by

increasing the concentration of GEOR 1 in the injected water as the GEOR 1

itself is not an unreasonable cost increment or environmentally sensitive in an

EOR project. Because the GEOR 1 additive can be used in a variety of reservoir

formation water chemistries it should be possible to simplify programes of

additive treatment in field applications. This potentially reduces the costs and

risks typical of previous chemical methods of enhanced oil recovery which

required extensive design and compatibility studies.

The experimental results far exceeded our expectations for GEOR 1 and more

importantly demonstrated that the additive out-performs cold- and hot-water

floods in fresh- and salt-water. Our bead-pack experiments are a simplification of

natural reservoir conditions however, they provide an important insight into the

utility of GEOR 1, which encourages us to recommend designing an immediate

field trial.