Analysis of Bhadra River Surface Water during Rainy Seasontheijes
Water samples were collected from Bhadra river along four different significant points and analyzed various temperature correlated parameters during the period rainy season 5th july, 2014 to 22nd august, 2014 using standard method. Water samples were collected from about10 cm depth with three replications from each station during low tides and high tides of the day. The study was conducted to know the present status of the water quality of the Bhadra river and the change of water quality parameters with the change of temperature. The study is significant due to huge practice of aquaculture at the adjacent area using the river water. The other significant feature is the connection of the river with sundarbans river system. This study involves the determination of some physical and chemical parameters which are mainly temperature correlated such as pH, transparency, salinity, electrical conductivity (EC), total alkalinity, total acidity, dissolved oxygen (DO) and dissolved free carbon dioxide of the surface water at four locations. The mean of parameters of different stations were temperature 290C; pH 7.68; transparency 10.88 cm, salinity 3.18 ppt, electrical conductivity (EC) 4.78 mS/cm, total alkalinity 103.91 mg/L, total acidity 8.4 mg/L, dissolve oxygen(DO) 5.1 mg/L, dissolve free carbon dioxide 3.89 mg/L. According to the results the parameters found less deviation from the standard water quality for aquatic habitat of river water
Analysis of Bhadra River Surface Water during Rainy Seasontheijes
Water samples were collected from Bhadra river along four different significant points and analyzed various temperature correlated parameters during the period rainy season 5th july, 2014 to 22nd august, 2014 using standard method. Water samples were collected from about10 cm depth with three replications from each station during low tides and high tides of the day. The study was conducted to know the present status of the water quality of the Bhadra river and the change of water quality parameters with the change of temperature. The study is significant due to huge practice of aquaculture at the adjacent area using the river water. The other significant feature is the connection of the river with sundarbans river system. This study involves the determination of some physical and chemical parameters which are mainly temperature correlated such as pH, transparency, salinity, electrical conductivity (EC), total alkalinity, total acidity, dissolved oxygen (DO) and dissolved free carbon dioxide of the surface water at four locations. The mean of parameters of different stations were temperature 290C; pH 7.68; transparency 10.88 cm, salinity 3.18 ppt, electrical conductivity (EC) 4.78 mS/cm, total alkalinity 103.91 mg/L, total acidity 8.4 mg/L, dissolve oxygen(DO) 5.1 mg/L, dissolve free carbon dioxide 3.89 mg/L. According to the results the parameters found less deviation from the standard water quality for aquatic habitat of river water
Use of hydraulic phenomena in enhancement of dissolved oxygen concentrationeSAT Journals
Abstract
The dissolved oxygen (DO) content of water bodies is an indicator of water quality and hence a measure of ability of water to sustain aquatic life. Hydraulic phenomena such as hydraulic drops and hydraulic jumps can increase the amount of DO in the water by creating turbulent conditions. The main reason for this oxygen transfer is the air entrainment into the flow through large number of air bubbles that helps in air-water transfer. The present study investigates the effect of different weir types and hydraulic jump on their aeration efficiency. Two types of weirs namely rectangular and triangular weirs were used in the study. Also, the hydraulic jump was studied as an aeration agent. From the experimental results, it was found that the triangular weir provides greater aeration efficiency of 0.1948 as compared with rectangular weir that had aeration efficiency of 0.1012. On the other hand, the hydraulic jump showed aeration efficiency of 0.14285. As the weirs are more efficient than hydraulic jump, they are most applicable in the field. Also, weir structures are less expensive when compared with the structural arrangement required for the formation of hydraulic jump.
Keywords: Dissolved oxygen, Aeration efficiency, Weir, Hydraulic jump
An overview of the U.S. healthcare industry hiring outlook for device, medtech, and diagnostic companies grappling with increased regulation, the 2.3% device tax, ACA provisions, and a candidate-driven market.
Lettre aux amis de Calcutta - avril 2010guest65ebe9
Voici une petite lettre avec quelques nouvelles de Howrah South Point en Inde. Lors de nos soirées annuelles le 11 juin à Couvet et le 25 juin à Renens, nous aurons la joie de vous donner des informations plus détaillées.
Use of hydraulic phenomena in enhancement of dissolved oxygen concentrationeSAT Journals
Abstract
The dissolved oxygen (DO) content of water bodies is an indicator of water quality and hence a measure of ability of water to sustain aquatic life. Hydraulic phenomena such as hydraulic drops and hydraulic jumps can increase the amount of DO in the water by creating turbulent conditions. The main reason for this oxygen transfer is the air entrainment into the flow through large number of air bubbles that helps in air-water transfer. The present study investigates the effect of different weir types and hydraulic jump on their aeration efficiency. Two types of weirs namely rectangular and triangular weirs were used in the study. Also, the hydraulic jump was studied as an aeration agent. From the experimental results, it was found that the triangular weir provides greater aeration efficiency of 0.1948 as compared with rectangular weir that had aeration efficiency of 0.1012. On the other hand, the hydraulic jump showed aeration efficiency of 0.14285. As the weirs are more efficient than hydraulic jump, they are most applicable in the field. Also, weir structures are less expensive when compared with the structural arrangement required for the formation of hydraulic jump.
Keywords: Dissolved oxygen, Aeration efficiency, Weir, Hydraulic jump
An overview of the U.S. healthcare industry hiring outlook for device, medtech, and diagnostic companies grappling with increased regulation, the 2.3% device tax, ACA provisions, and a candidate-driven market.
Lettre aux amis de Calcutta - avril 2010guest65ebe9
Voici une petite lettre avec quelques nouvelles de Howrah South Point en Inde. Lors de nos soirées annuelles le 11 juin à Couvet et le 25 juin à Renens, nous aurons la joie de vous donner des informations plus détaillées.
The concentration of the distributors vs. production fragmentation has created an imbalance in market power, and is at the origin of strains in the food chain. This weak bargaining position of food production produces serious socioeconomic consequences that may affect the maintenance of food production quality. The question is how to build a supply chain that provides sustainable added value to all participants that interact therein.
Produced water reinjection (PWRI) is one of the most usual ways of produced water reuse in mature fields with high water cut.
The relationship between water quality and injectivity decline in wells is well known and it is particularly important in mature
fields, such as Barrancas, an old field located in Mendoza –Argentina, with more than 40 years of water injection. In this
reservoir significant injectivity losses were recorded when fresh water was replaced by produced water in the 90´s.
Formation Damage mechanism is mainly caused by external cake. Particles are principally, iron sulfide, calcium carbonate,
and oil droplets.
Determination of Effect Bentonite and Additives On Drilling FluidsIRJESJOURNAL
Abstract :- Drilling fluids Play a vital role in hole Cleaning suspension of cuttings, prevent caving, and ensure the tightness of the well wall. Moreover they also help in cooling and lubricating the drilling tool, transfer the hydraulic power and carry information about the nature of the drilled formation by raising the cuttings from the bottom to the surface, using a simple mixture of water and clays, to complex mixtures of various specific organic and inorganic products as additives. These additives improve fluid rheological properties and filtration capability, allowing bits to penetrate heterogeneous geological formations The mud used in this work is barite and bentonites at different samples to know the difference in their specific gravity, viscosity, surface tension, and pH of the samples when chemical additives are added.
The article is devoted to the problem of limiting water inflow in a production well.
The authors consider the main features of the reservoir, which contribute to
premature flooding. This paper presents the basic classification of plugging selective
compositions, outlines the advantages and disadvantages of each type. Gel composed
of carboxymethylcellulose, chromium acetate and copper sulfate was developed for
water production restriction. An alternative way was offered to determine the optimal
concentrations of plugging compositions on the change of the total porosity and x-ray
density measured in the x-ray tomograph. Dynamics of the effective viscosity on the
magnitude of the gap, simulating the fracture was obtained – the viscosity decreases
logarithmically. Filtration experiments confirmed the selective properties of the gelforming
composition
Scale Formation problems in Oil & Gas Industry : Its reduction procedures by ...Sachin Nambiar
This paper is a literature review on methods to control scale formation using various chemicals; and its economic feasibility in the petroleum industry.
IRJET- Effect of Sea Water and Strength of Concrete
Petroleum Science and Technology 2015
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Analysis of Low Salinity Waterflooding in
Bastrykskoye Field
V. Ahmetgareev
a
, A. Zeinijahromi
b
, A. Badalyan
b
, R. Khisamov
a
& P.
Bedrikovetsky
b
a
TATNIPINEFT Research Centre, Bugulma, Tatarstan, Russia
b
Australian School of Petroleum, The University of Adelaide,
Adelaide, Australia
Published online: 16 Mar 2015.
To cite this article: V. Ahmetgareev, A. Zeinijahromi, A. Badalyan, R. Khisamov & P. Bedrikovetsky
(2015) Analysis of Low Salinity Waterflooding in Bastrykskoye Field, Petroleum Science and
Technology, 33:5, 561-570, DOI: 10.1080/10916466.2014.997390
To link to this article: http://dx.doi.org/10.1080/10916466.2014.997390
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Downloadedby[VadimAhmetgareev]at12:2718March2015
3. Petroleum Science and Technology, 33:561–570, 2015
Copyright C Taylor & Francis Group, LLC
ISSN: 1091-6466 print / 1532-2459 online
DOI: 10.1080/10916466.2014.997390
Analysis of Low Salinity Waterflooding in Bastrykskoye Field
V. Ahmetgareev,1
A. Zeinijahromi,2
A. Badalyan,2
R. Khisamov,1
and P. Bedrikovetsky2
1
TATNIPINEFT Research Centre, Bugulma, Tatarstan, Russia
2
Australian School of Petroleum, The University of Adelaide, Adelaide, Australia
Low salinity waterflooding is presently one of the most promising enhanced oil recovery (EOR) methods.
Wettability alteration and residual oil decrease are the most important EOR mechanisms of low salinity
waterflooding. However, the mobility control EOR due to fines migration, induced by low salinity water,
and the consequent flux diversion is also an important feature of the smart waterflooding. We analyze
the limited available field data from 10 years of low salinity water injection in Bastrykskoye field.
The mathematical model for fines-assisted waterflooding is used for history matching resulting in good
agreement between the field and modeling data. The model is used to compare recovery factor for
two scenarios of low salinity water injection and formation (normal) water injection. Low incremental
recovery and low decrease in the amount of produced water during the development of Bastrykskoye field
is explained by the production of significant amount of the reservoir water before the commencement of
low salinity water injection.
Keywords: field data, low salinity waterflood, fines-assisted waterflooding, history matching, fines
migration
1. INTRODUCTION
Low salinity waterflooding is a recently developed enhanced oil recovery (EOR) technique that
improves mostly microscopic displacement efficiency by alternating the rock wettability, making
it more water wet. The detailed analysis of microscopic physics mechanisms of low salinity wa-
terflooding can be found in reviews by Morrow and Buckley (2011) and Sheng (2014). Recent
studies of low salinity waterflooding have largely focused on the effects of water compositions on
wettability, capillary pressure, relative permeability, and residual oil saturation (Tang and Morrow,
1999; Berg et al., 2010). Morrow and Buckley suggest also that the formation of lamellae and
emulsions, stabilized by fines, their migration, and straining, may result in mobility control and
deep reservoir flow diversion. Tang and Morrow (1999) and Fogden et al. (2011) suggested another
mechanism of oil-wet and mixed-wet fines detachment by advancing water-oil capillary menisci; the
resulting straining may also decrease the water relative permeability and increase oil recovery. These
effects appear to be separate phenomena from the fines lifted by low salinity water and plugging of
water-filled pores, but may occur simultaneously with fines migration. Hussain et al. (2013) aimed
to confirm the above effects of the water phase permeability reduction during high and low salinity
waterflooding in oil-saturated rock. It was concluded that the water-wet particles have been removed
Address correspondence to A. Zeinijahromi, The University of Adelaide, Adelaide, Australia. E-mail: ajahromi@asp.s
adelaide.edu.au
Color versions of one or more of the figures in the article can be found online at www.tandfonline.com/lpet.
561
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4. 562 V. AHMETGAREEV ET AL.
from the rock by moving low salinity water, resulting in decrease in relative permeability for wa-
ter and in increase in fractional flow for oil. The conclusions agree with the above mechanisms
proposed by Sarkar and Sharma (1990). In order to separate these effects, the injections leading
to fines lifting and permeability decline are called in the current work the fines-assisted water-
flooding.
The available literature on laboratory studies and mathematical modeling of low salinity wa-
terflooding highly exceeds that on field trials. Several limited field applications show significant
recovery of residual oil (Seccombe et al., 2010). However, the North Sea pilot, where the screening
criteria for low salinity waterflood have been met, did not exhibit an incremental recovery (Skret-
tingland et al., 2010). The lack of information on real field applications of smart waterflooding is a
serious restriction for large scale application of the technology in oil industry.
2. DESCRIPTION OF LOW SALINITY WATERFLOODING IN THE FIELD
Map of the Bastrykskoye field is shown in Figure 1. Purple circles correspond to 18 injectors double-
color circles correspond to 36 producers. The circle sizes are proportional to accumulated injection
and liquid volume produced. Bastrykskoye field consists of two isolated sandstone reservoirs with
almost no hydrodynamic interaction between. Average thickness of the upper Tula layer is 4 m,
thickness of the impermeable clay layer in between is 6 m and the lower Bobrik thickness is 10 m.
Figure 2 shows three cross sections that are shown in the map in Figure 1. Lower Bobrik layer
has lower permeability than upper Tula layer. Pressure depletion started in 1982 followed by low
salinity water injection started in 1988. Figure 3 shows that the significant amount of water has
already been produced at the moment of waterflood commencement in 1988. Field mean water cut
reached the value 0.48 on January 1, 2014. The injectors are located below water-oil contact. Partial
pressure maintenance with oil and water production occurred during 1982–1988. Full pressure
maintenance occurred during low salinity water injection during 1988–2014. Figure 1 shows oil
saturation averaged over the production thickness. The saturation field is obtained from 3 days’
reservoir simulation after matching the production and injection history up to January 1, 2014.
Water cut in production wells gradually decreases from the position of initial oil-water contact up to
the central part of the anticlinal field. One can also see that oil saturation increases from peripheral
areas, where the injectors are located, towards the central part of the field.
The main properties of fluids and rocks are given in Table 1. The initial pressure is above the
bubble point pressure; there is no initial gas cap. The primary energy for the primary production
is provided by adjacent aquifer. Table 2 shows the formation and injected water compositions,
respectively. Extremely high formation water salinity is defined by sodium chlorite concentration
that highly exceeds those for other salts, while magnesium and calcium salts dominate in injected
water. Thus, intensive ion exchange is expected during the displacement of formation water by
injected water.
Permeability distribution of different layers can be seen in three cross sections in Figure 2.
The positions of three cross-sections are shown in Figure 1. The reservoir has minor-to-average
heterogeneity. The multiple horizontal sub-layers are combined into two layers. The upper Tula
layer has high permeability. However, the lateral correlation of sublayers is lower than that in the
lower Bobrik layer.
Water injection into aquifers yields better sweep and displacement than that in the oil zone, as the
displacement of oil by water is going on by the plane moving upwards water-oil contact. Slope of
the peripheral zones near the initial water-oil contact also increases the recovery during bottom-up
waterflooding, as gravity decelerates water and accelerates the oil. This explains high displacement
efficiency (see Table 1).
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5. LOW SALINITY WATERFLOODING IN BASTRYKSKOYE FIELD 563
FIGURE 1 Well placing in Bastrykskoye field with map of oil saturation.
3. RESERVOIR SIMULATION
The mathematical model for low-salinity waterflooding, where the incremental recovery is caused
by the capillary phenomena and wettability alteration with the consequent decrease in residual oil
saturation is similar to that of the chemical EOR (Lake, 1989). The basic equations include mass
balances for oil, water and some ions. The equations for equilibrium ion exchange and sorption on
clays give the ion sorption isotherms. The relative phase permeability and capillary pressure are
ion-concentration-dependent.
If the incremental oil recovery is caused by lifting of attached fines, their migration and strain-
ing in thin pore throats, the model is similar to those of mobility control EOR. In the present
study the comparison between the fines-assisted and normal waterflooding is performed for the
field conditions. Therefore, the mathematical model for low salinity waterflood with changing rel-
ative phase permeability and accounting for fines mobilization and straining, yielding permeability
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6. 564 V. AHMETGAREEV ET AL.
FIGURE 2 Permeability of Tula and Bobrik layers in three cross sections of the field: (a) cross section position I;
(b) cross section II; (c) position of the cross section III; (d) scale for permeability in mD, with perforation intervals
in red.
reduction in water swept areas, is used (see Zeinijahromi et al., 2013). The basic equations are
mapped on the system of equations for polymer flooding, allowing modeling of the above pro-
cesses with low salinity water injection using polymer option of black-oil model. Here we apply
the reservoir simulation software Tempest (Roxar, Houston, TX) for modeling of low salinity
and normal waterflooding. The tracer option in Tempest is equivalent to polymer option with-
out adsorption, where relative permeability depends on tracer (salt) concentration, which fits to
the previously mentioned model for low salinity waterflooding. The tuning parameters are pseudo
(at the reservoir scale) phase permeability for oil and formation water, and the reduction factor
to obtain the phase permeability for low salinity water from the phase permeability for normal
water.
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7. LOW SALINITY WATERFLOODING IN BASTRYKSKOYE FIELD 565
FIGURE 3 History matching of Low Sal Waterflooding: accumulated oil production, accumulated water produc-
tion, and accumulated water injection.
TABLE 1
Properties of Rocks and Fluids in Bastrykskoye Field
Layer
Characteristic Tula Bobrik
Reservoir top depth, m −916.8 −927
Reservoir type porous porous
Formation thickness, m 24.4 10.3
Net pay thickness, m 2.1 3.6
Relative thickness of sandstone layers 0.81 0.62
Initial oil saturation 0.83 0.86
Reservoir temperature, ◦С 25 25
Initial reservoir pressure, MPa 11.4 11.6
Bubble point pressure, MPa 1.15 4
GOR, m3/ton 6.07 14.2
Oil density under reservoir conditions, kg/m3 848.8 851.5
Oil density under surface conditions, kg/m3 864.7 878.3
Oil viscosity under reservoir conditions, mPa·sec 12.6 6.83
Formation volume factor 1.03 1.064
Water density under reservoir conditions, kg/m3 1171.5 1171.5
Water viscosity under reservoir conditions, mPa·sec 1.75 1.75
Specific-productivity index, m3/(day·MPa·m) 3.11 3.11
Displacement efficiency obtained from corefloods 0.652 0.663
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8. 566 V. AHMETGAREEV ET AL.
TABLE 2
Composition of Formation and Injected Water in Bastrykskoye Field
MW g/mol Conc. mol/L Conc. mg/L Conc. g/L Conc. % (w/w)
Formation Water
NaCl 58.439 3.26534 190823.3 190.8233 79.71
MgCl2 95.205 0.12336 11744.2 11.7442 4.91
MgSO4 120.367 0.00625 751.8 0.7518 0.31
CaCl2 110.978 0.32437 35997.7 35.9977 15.04
NaHCO3 84.006 0.00090 75.7 0.0757 0.03
Ionic strength 4.63 mol/L
Fresh Lake Water Injected
NaCl 58.439 0.00034 20.1 0.0201 2.37
MgCl2 95.205 0.00029 28.1 0.0281 3.31
MgSO4 120.367 0.00115 137.8 0.1378 16.25
CaCl2 110.978 0.00250 276.9 0.2769 32.64
NaHCO3 84.006 0.00459 385.5 0.3855 45.44
Ionic strength 1.027 mol/L
Figure 3 presents the production and injection history along with the modeling data.
The coreflood results presented in laboratory studies by Zeinijahromi et al. (2014) and Hussain
et al. (2013) show that changing formation water to injected fresh water yields significant decrease
in relative permeability for water under residual oil saturation krwor while residual oil saturation,
connate water saturation and relative permeability for oil under connate water are almost the same.
The fivefold decrease of krwor (reduction factor) that is used in this study is the same as that
obtained in laboratory studies by Zeinijahromi et al. (2014) and Hussain et al. (2013).
Let us describe the tuning procedure. The Corey form of pseudo relative permeability for each
of two reservoirs is assumed. The pseudo relative permeability kr depends on saturation (s) and
salinity (γ ): krj = krj(s,γ ), j = W,O. Following the coreflood results, it is assumed that pseudo
relative permeability for oil is independent of salinity. Residual oil saturation and power for oil are
also independent of salinity. The value of end point relative permeability krwor for injected salinity
(γ = 0) is assumed to be five times lower than that for formation water (γ = 1).
The Corey parameters are obtained by tuning the curves of cumulative oil and water production.
The form of tuned pseudo relative permeability is shown in Figure 4a for Tula layer and in Figure
4b for Bobrik layer.
The obtained Corey parameters for oil-formation water are shown in the tables below Figures
4a and 4b. The Corey powers are lower than one. It determines the convex forms of pseudo phase
permeability, which is typical for those as obtained at the reservoir scale.
Figure 3 exhibits a good match between the field history and the modeling data after the history
matching.
4. COMPARISON BETWEEN NORMAL AND LOW SALINITY WATERFLOODS
Incremental recovery with low salinity waterflooding is achieved by changing the injected water
composition if compared with the formation water. During the injection of formation water, which
in reality does not happen in industry, no ionic exchange or fines detachment due to alteration
of electrostatic force occur. Therefore, we define formation water injection as a basic waterflood
option, which is referred to as normal waterflooding. All options of water injection with different
composition are compared with the normal waterflooding.
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9. LOW SALINITY WATERFLOODING IN BASTRYKSKOYE FIELD 567
FIGURE 4 Pseudo relative permeability.
Figure 5a shows the comparison for water cut and recovery factor between the normal and low
salinity waterflooding. The incremental recovery factor due to injection of low salinity water is
1.1% only. Injection of low salinity water results in reduction of amount of produced water by 1.7%
only.
A comparative study is performed for a five-spot pattern in a two layer cake reservoir with similar
heterogeneity to Bastrykskoye field as described in Zeinijahromi et al. (2013). The results of low
salinity water injection in two-layer 5-spot pattern with size 200 × 200 m during 1,400 days (four
years) are presented in Figure 5b. The layer properties, including pseudo phase permeability are the
same as that in Tula and Bobrik layers (Figure 4). Low salinity of injected water causes fivefold
decrease in relative permeability for water. The incremental recovery factor is 8.7% that agrees
with the results reported in Zeinijahromi et al. (2013). A higher incremental recovery obtained
from five-spot pattern if compared with injection into WOC in Bastrykskoye field is majorly due to
commencement of low salinity water injection from start of production.
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10. 568 V. AHMETGAREEV ET AL.
FIGURE 5 Comparison between injections of low salinity and high salinity waters for (a) conditions of Bastryk-
skoye field, (b) two-layer cake reservoir (with Bastrykskoye field’s characteristics).
5. SUMMARY AND DISCUSSIONS
The objective of the present work is preliminary analysis of low salinity waterflooding in the
Bastrykskoye oil field and its comparison with the normal waterflooding. It is assumed that low
salinity waterflooding causes fines migration and induced permeability damage in the swept areas,
resulting in deep reservoir flux diversion.
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11. LOW SALINITY WATERFLOODING IN BASTRYKSKOYE FIELD 569
The tuned pseudo relative permeability has typical convex form, which is typical for up scaled
relative permeabilities at the reservoir length scale. The fivefold decrease of relative permeability
for water due to salinity decrease is typical for sandstone reservoir cores (see Hussein et al.,
2013).
The tuned reservoir model shows very little recovery increment and small reduction in produced
water for low salinity fines-assisted waterflooding if compared with injection of formation water.
However, these effects for injection into five-spot pattern are significant. The previously mentioned
phenomena must be explained.
Significant amount of water has been produced before the injection in Bastrykskoye field (i.e., the
injected water displaces the oil under high water saturation). The water cut map shows that the sweep
by the low salinity water is minimal due to water injection into the aquifer, almost no low salinity
water was produced (Figure 1). The central part of the reservoir is poorly swept by the injected
water. Oil is directly displaced by high salinity formation water, injected water lags significantly
behind. The main reason has been previously mentioned as to why the incremental recovery factor
with low salinity waterflooding is not high.
Sweep efficiency for water injection into aquifer is higher than that with the injection into oil zone.
The discussed fines-assisted low salinity waterflood mostly affects the sweep, which is already high.
This is another reason why low salinity fines-assisted waterflood does not exhibit high incremental
recovery in the case under consideration.
However, the model for low salinity waterflood accounts for fines migration and consequent
decrease of relative permeability for water (i.e., the effects of wettability change and residual oil sat-
uration decreasing) are ignored. Accounting for decrease in relative permeability for oil and decrease
in oil residual can bring additional incremental recovery if compared with the normal waterflooding.
This study is supposed to be performed after the laboratory coreflooding and determining the relative
phase permeability for formation and injected waters.
Both effects of sweep and of better displacement coefficient can affect only the boundary wells.
The central part of the reservoir will be affected at the later stage, when the boundary wells are
watered out and abandoned, and central wells will produce injected water.
The problem whether in general the incremental recovery with low salinity waterflood in both
chemical EOR and mobility-improvement modes during the injection into aquifer is low, may be a
subject of additional investigation.
Only very limited information from the field is available; hence, significant amount of addi-
tional investigations (coreflooding, SEM, XRD) must be performed for detailed analysis of the
Bastrykskoye field case.
Despite some studies reported alternation of oil properties during low salinity water injection
(Lager et al., 2008); no information of alterations of oil properties has been reported during LS water
injection and oil production in Basrtykskoye field.
6. CONCLUSIONS
Oil and water production data for low salinity waterflooding in Bastrykskoye oilfield can be matched
by the fines-assisted-waterflood model (tracer model in Roxar) with high accuracy.
Low salinity water injection under the conditions of Bastrykskoye field results in low incre-
mental recovery and low decrease in the produced water if compared with waterflooding by
formation water under fivefold decrease in relative permeability for water due to induced fines
migration.
The phenomenon is explained by high flooding of the reservoir before commencement of low
salinity water injection, by high salinity water. Another explanation is low salinity water injection
into aquifer causes lower incremental recovery than that with the injection into oil-zone.
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12. 570 V. AHMETGAREEV ET AL.
REFERENCES
Berg, S., Cense, A. W., Jansen, E., and Bakker, K. (2010). Direct experimental evidence of wettability modification by low
salinity. Petrophysics 52:314–322.
Fogden, A., Kumar, M., Morrow, N. R., and Buckley, J. S. (2011). Mobilization of fine particles during flooding of sandstones
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