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Nmegbu Int. Journal of Engineering Research and Applications www.ijera.com
ISSN : 2248-9622, Vol. 4, Issue 6( Version 3), June 2014, pp.165-169
www.ijera.com 165|P a g e
Model for The Diffusionof Biogenic Gases In Heterogeneous
Reservoirs Undergoing Transient Flow
Nmegbu, Chukwuma Godwin Jacob *
*(Department of Petroleum Engineering, Rivers State University of Science and Technology, Nigeria)
ABSTRACT
Microbially enhanced petroleum reservoirs confirms a recovery of about 30-40 % residual oil, with an integral
composition of wide range of oil recovery mechanisms including wettability alteration by biosurfactant
production, selective plugging of highly permeable channels by biopolymer production, creating fluid flow
channels in carbonate reservoirs by rock dissolution attributed to bioacid formation, and a range of other
exploitable recovery techniques. This study presents an investigation of biogenic gas produced in-situ and its
concentration profile across the reservoir. An increasing concentration trend in the grids was observed and these
increments were owed to the fact that diffusion of the biogenic occurred. It was also observed that after 40days
of Desulfovibro injection, the produced CO2 across the reservoir was tending towards being even in values of
concentration, implying that diffusion rate was approaching a zero value. Also, the distorting effect of reservoir
heterogeneity on biogenic gas concentration profile was also resolved by adopting the method of averaging for
permeability and porosity in the reservoir.
Keywords–Biogenic gases, Concentration, Heterogeneity, Microbes
I. INTRODUCTION
Microbial enhance oil recovery is an aspect of
biotechnology that utilizes the potentials of some
microbes injected into petroleum reservoirs for
certain oil recovery mechanisms. These mechanisms
attempt to overcome the some obstacles in efficient
oil recovery such as the low permeability, high
viscosity of the residual crude oil, and high oil-water
interfacial tensions that may result in high capillary
forces retaining the oil in the reservoir rock, etc.
[1].MEOR involves the use of specific bacteria
capable of producing useful metabolites in-situ such
as gases, acids, surfactants, solvents and polymers in
order that their presence will aid further reduction of
residual oil left in the reservoir after secondary
recovery[1], [2]. Webb in 1998 outlined the
production of biogenic gases creates a free gas phase
that can account for incremental oil recovery in
MEOR processes either by reduction of the oil
viscosity by solution of the gas in the oil, or by re-
pressurization of the reservoir through gas cap
formation, causing displacement from trapped
capillaries and enhancing mobilization of the oil to
the producing wells [3], [4]. The most important gas-
producing microbes include; Clostridium,
Desulfovibrio, Pseudomonas, and some methanogen.
The composition of the biogenic gas from
bacteriametabolism can include carbon dioxide,
hydrogen, methane and nitrogen [5], [6], [7]. This
study not only aims at investigating the concentration
profile of produced biogenic gases, but also tends to
investigate the effects of reservoir heterogeneity on
biogenic gas distribution across the reservoir. The
knowledge of biogenic gas concentration profiles in
heterogeneous reservoirs are of great importance
when accounting for the overall recovery efficiency
of the MEOR process either by solution gas drive or
gas-cap formation.[2], [8].
II. METHODOLOGY
2.1 Microbial choice
An anaerobic microbe was selected for this
investigation. Its morphology confirms its ability to
produce bioacids and biogases with a higher
production of the later. Desulfovibrio having an
excellent transport mechanism, tolerable pH range
and extremely low decay rate in subsurface
conditions proves the suitable microbe for this study.
The biogenic gas produced was assumed to be
Carbon dioxide (CO2) after microbial utilization of
the residual hydrocarbon.
2.2 Biogenic gas concentration and diffusion
account.
Assuming that the rate at which microbes act on the
oil is = microbial injection rate
and
Microbial injection rate = biogenic gas production
rate (1)
We can say that the governing
statement above automatically tends to neglect
microbial retention time.
We Recall that the volume of biogenic gases
produced = gas generated in pore volume of the
reservoir, PV. (2)
Where
RESEARCH ARTICLE OPEN ACCESS
Nmegbu Int. Journal of Engineering Research and Applications www.ijera.com
ISSN : 2248-9622, Vol. 4, Issue 6( Version 3), June 2014, pp.165-169
www.ijera.com 166|P a g e
PV= Ah 𝜙(1-Sor) (3)
A = area of the reservoir (ft2
)
H is the height of the reservoir (ft)
ϕis the average porosity of the heterogeneous
reservoir
The rate at which these biogenic gases are formed is
given as;
volume of produced biogenic gases
microbial retention time
=
Vbg
ϑ
=
Ah ϕ(1−Sor)
ϑ
(4)
But recalling (1), we have
Biogenic gas production rate= Ah 𝜙(1 − Sor)
(5)
Consider the horizontal reservoir below undergoing
microbial injection for Improved oil recovery with no
flow boundary condition and rectangular geometry
with a microbial injection rate of 500bbl/day
(microbe- water mixture).
Fig.1 schematic of discretized reservoir undergoing
microbial injection
Assuming
Recalling the gas flow equation in 1D
∂
∂x
AK
μg Bg
∂C
∂x
∆x + qg + qw Rsw + qoRso =
Vb ϕCt
αc
∂C
∂t
(6)
Assuming that the biogases produced is not soluble in
the residual oil and water, we have;
∂
∂x
β
AK
μg Bg
∂C
∂x
∆x + qg =
Vb ϕCt
αc
∂C
∂t
(7)
Recalling Fick’s law and replacing the
transmissibility coefficient with diffusivity
coefficient. Writing the above in a 2nd
order
derivative, we have
∂2C
∂x2 −Dg
AK
μg Bg
∆x + qg =
Vb ϕCt
αc
∂C
∂t
(8)
For a second order derivative, the equivalent finite
difference notation for the LHS in terms of
concentration is given as
∂2C
∂x2 =
Ci−1
t
−2Ci
t
+Ci+1
t
∆x2 (9)
For the RHS, change in concentration is with respect
to time, the equivalent finite difference
approximation is given as
∂C
∂t
=
Ci
t+1
−Ci
t
∆t
(10)
(8) can be written as
Ci−1
t
−2Ci
t
+Ci+1
t
∆x2 −Dg
AK
μg Bg
∆x + qg =
Vb ϕCt
αc
Ci
t+1
−Ci
t
∆t
(11)
Rearranging the above we have
Ci−1
t
− 2Ci
t
+ Ci+1
t
−Dg
A K
μg Bg ∆x
+ qg =
Vb ϕCt
αc ∆t
(Ci
t+1
−
Ci
t
) (12)
Considering the heterogeneous reservoir system with
varying permeability values shown below, we recall
the method of averaging for permeability.
Fig 2. A rectangular heterogeneous reservoir with
varying K values
Kavg =
Li
n
i=1
Li
Ki
n
i=1
(13)
(12) now becomes
Ci−1
t
− 2Ci
t
+ Ci+1
t
− Dg
A Kavg
μg Bg ∆x
+ qg =
Vb ϕCt
αc ∆t
(Ci
t+1
− Ci
t
) (14)
The diffusion of the biogenic gases produced by
the microbe will be accounted for using the biogas
concentration profile across the heterogeneous
reservoir at various positions i and time t.
Setting −Dg
A Kavg
μg Bg ∆x
as the diffusive flux, J’ and
neglecting the negative sign, we have;
Ci−1
t
− 2Ci
t
+ Ci+1
t
J′
+ qg =
Vb ϕCt
αc ∆t
(Ci
t+1
− Ci
t
)
(15)
Rearranging the above
J′
Ci−1
t
− 2 J′
Ci
t
+ J′
Ci+1
t
+ qg =
Vb ϕCt
αc ∆t
(Ci
t+1
−
Ci
t
) (16)
Accounting for biogas concentration at various
reservoir positions, we multiply through by
αc ∆t
Vb ϕCt
αc ∆t
Vb ϕCt
J′
Ci−1
t
− 2 J′
Ci
t
+ J′
Ci+1
t
+
αc ∆t
Vb ϕCt
qg =
Ci
t+1
− Ci
t
(17)
Setting transient tern as Z, we obtain
Z J′
Ci−1
t
− 2 J′
Ci
t
+ J′
Ci+1
t
+ Zqg = Ci
t+1
− Ci
t
(18)
The biogenic gas prediction equation in terms of
concentration with respect to position at any given
time is thus
Nmegbu Int. Journal of Engineering Research and Applications www.ijera.com
ISSN : 2248-9622, Vol. 4, Issue 6( Version 3), June 2014, pp.165-169
www.ijera.com 167|P a g e
Ci
t+1
=Ci
t
+ Z J′
Ci−1
t
− 2 J′
Ci
t
+ J′
Ci+1
t
+ Zqg
(19)
Assumptions
 Mass transfer occurs only by diffusion.
 Negligible gas influx, ie no flow boundary
condition
 Gas composition is homogenous, only CO2
produced.
 Diffusion occurs predominantly in the horizontal
direction
 Metabolite production mostly biogenic gases.
 Isothermal system as reservoir fluctuations in
temperature is regarded minimal.
 Negligible capillary action.
 No break in injection rates of microbes
 Microbial decay not considered.
 No indigenous microbe present.
 Chemotaxis not considered.
 No substrate and metabolite adsorption on the
pore walls, so Langmuir
 Equilibrium isotherm not considered.
 Gravitational effects considered negligible.
 Electrokinetic effects negligible.
 Unsteady state flow conditions.
 Other factors affecting growth rates such as
salinity and pH remains constant.
III. RESULTS AND DISCUSSION
Table 1.Reservoir and microbial parameters for
biogenic gas concentration analysis.
Parameters Value
Produced biogenic gas
diffusion coeff, Dbg
1.05× 10-6
ft2
/day
K1 K2 K3 K4 150, 200, 180, 129 (mD)
Ф1, Ф2, Ф3, Ф4 20, 36, 30, 16
Initial gas concentration,
Cgi
100lb/ft3
Microbial injection rate qg 500bpd
Reservoir thickness ∆𝑦 50 ft
Reservoir grid length ∆𝑥 1000ft
Reservoir breadth ∆𝑧 1500ft
Reservoir length 4000ft
Time increment, ∆𝑡 10days
Volume conversion
factor, 𝛼 𝑐
5.615
Total compressibility, 𝐶𝑡 3.0× 10-6
Gas formation volume
factor, 𝐵𝑔
0.000512scf
Gas viscosity, 𝜇 𝑔 0.017cp
Assuming that microbial injection rate = rate at
which microbes act on the oil= biogenic gas
production rateCalculating constants (diffusivity
component and transient term)
J′
= Dg
AKavg
μgBg∆x
= 9.23
Z =
αc∆t
VbϕCt
= 0.959
Recalling (19),
Ci
t+1
=Ci
t
+ Z J′
Ci−1
t
− 2 J′
Ci
t
+ J′
Ci+1
t
+ Zqg(20)
The concentration profile of the diffusing biogenic
gas is then predicted using the above and applying
the following boundary conditions.
C1 = Co, for all time steps.
C4 = C5, for all time steps.
No net or bulk influx of biogenic gases at the
boundaries of the reservoir.
The table below shows the concentration of the
biogas across the reservoir.
Table 2.Deduced concentration values of Produced
biogenic gas across the heterogeneous reservoir for
various time steps.
Grid blocks
(ft)
1 2 3 4
𝐶𝑖
10
(lb/ft3
) 580 524 476 433
𝐶𝑖
20
(lb/ft3
) 585.
05
535.5
7
490.66 484
𝐶𝑖
30
(lb/ft3
) 591.
41
545.2
4
532.41 526.8
6
𝐶𝑖
40
(lb/ft3
) 595.
07
579.4
0
569.10 564.2
4
Fig 3. Plot of CO2 concentration against time in
individual reservoir grids
Fig 3 shows the increasing concentration of
biogenic gases in each discrete point of the reservoir
at different periods during the microbial action.
Initial gas concentration in the reservoir was recorded
0
100
200
300
400
500
600
700
0 20 40 60
Biogasconcentration(lb/cft)
Time (days)
GB1
GB2
GB3
GB4
Nmegbu Int. Journal of Engineering Research and Applications www.ijera.com
ISSN : 2248-9622, Vol. 4, Issue 6( Version 3), June 2014, pp.165-169
www.ijera.com 168|P a g e
to be 100lb/ft3
, but was observed to increase to
certain levels during the breaking down process of
the residual crude by the microbes. The trend
observed in virtually all the grids shows that biogas
distribution across the heterogeneous reservoir was
tending towards the same value at a higher time step
of 40 days. For grid block 4, which is farther away
from the gas production point (injector), its trend
with time shows a continuous increment in gas
concentration and will only attain a value equal those
closer to the injector only by continuous biogas
diffusion phenomenon.
Fig 4. Biogas concentration profile across the
horizontal reservoir
It is established from the diffusion laws that
whenever equilibrium is reached, diffusion stops [5],
[9]. This statement is evident in Fig 4, showing the
concentration profile of the diffusing biogenic gas for
various reservoir positions of investigation at
different time. The concentration profiles of Biogenic
gases can only be ascertained if there is transport of
the gaseous phase (diffusion) through the porous
media. The linear and systematic orderly patterns
observed in the concentration profile across the
reservoir are traceable to the assumption that the
produced biogenic gases are insoluble in the oil. This
implies that since these gases do not go into solution
with the oil to cause viscosity reduction, these
produced biogenic gases continuously form a strong
gas cap layer that will re-pressurize the reservoir to
enhance oil flow. Consideration of gas solubility in
oil will cause a distortion in the gas concentration
profile across the reservoir. Another explanation to
the regular concentration profile seen above is the
adaptation of the method of averaging for
permeability and porosity. For the horizontal
heterogeneous reservoir of varying rock properties, it
is expected of the profile to take an irregular pattern
[8].
IV. CONCLUSION
Biogenic gases produced in-situ is a major
contributory factor in the whole microbial recovery
process. The above figures have revealed that the
concentration of the biogenic gas across the reservoir
tends to be evenly distributed across the reservoir
through the diffusion process. Since the gases do not
go into solution with the residual oil in the reservoir,
it should be, concluded that recovery mechanism of
the microbially produced biogenic gases is by
reservoir re- pressurize by gas cap formation. It is
therefore recommended that further study and
investigation should be conducted to ascertain
relationships for heterogeneous biogenic gas
compositions and gases solubility so as to account for
both viscosity reduction of the heavy crude and gas
cap formation.
V. ACKNOWLEDGEMENTS
The authors will like to acknowledge the
countless relentless efforts ofEzeagala Anthony and
Pepple Daniel Dasigha in making this research work
possible.
REFERENCES
[1] L.K. Jang, M. M. Sharma and T. F.
Yen.(1984). “The transport of bacteria in
porous media and its significance in
microbial enhanced oil recovery”. SPE-
12770 presented at California Regional
Meeting, Long Beach, California, USA, pp
11–13.
[2] D. Dejun, L. Chenglong, J. Quanyi,W.
Pingcang, .and F.L. Dietrich.(1999).
“Systematic Extensive Studies of Microbial
EOR Application Results in Chanqing
Oilfield.” SPE Paper 54380, in proceedings
of the 1999 SPE Asia Pacific Oil and Gas
Conference and Exhibition, Jakarta,
Indonesia, April 20th
-22nd
, 1999. PP 1-9.
[3] S. W. Webb,(1998).“Gas diffusion in porous
media – evaluation of an advective-
dispersive formulation and the dusty-gas
model for binary mixtures”.J. Porous Media
1, 187–199.
[4] D. C. Thorstenson, and D. W. Pollock.(
1989): “Gas transport in unsaturated zones:
multi-component systems and the adequacy
of Fick’s laws”. Water Resour. Res. 25, PP
477–507.
[5] E. Fathi, and I. Y. Akkutlu.(2008) .:
“Counter-Diffusion and Competitive
Adsorption Effects During CO2 Injection
and Coalbed Methane Production”, SPE
115482, paper presented at the 2008 SPE
0
100
200
300
400
500
600
700
0 10000 20000 30000 40000 50000
Biogasconcentration(lb/cft)
Grid block distance (ft)
10 days
20 days
30 days
40 days
Nmegbu Int. Journal of Engineering Research and Applications www.ijera.com
ISSN : 2248-9622, Vol. 4, Issue 6( Version 3), June 2014, pp.165-169
www.ijera.com 169|P a g e
Annual Technical Conference and
Exhibition held in Denver, Colorado, USA.
[6] L. K.Jang,M. M.Sharma, J. E. Findley, P.
W.Cang, and T. F. Yen. (1982): “An
Investigation of Transport of Bacteria
Through Porous Media.” Proc. Int. Con-
microbial enhancd oil recovery, Afton, OK,
DOE. Conf-8205140 PP 60-70 16th
– 21st
May,
[7] E.T. Premuzic and M.S.Lin. (1988). “Effects
of selectedmicroorganisms on crude oil at
elevated temperatures and pressures”,
Annual report BNL 42048, 1988.
[8] J.E. Warren and P.J. Root (1963).: “The
Behavior of Naturally Fractured
Reservoirs”. SPE J. 3 (3): 245–255; Trans.,
AIME, 228. SPE-426-PA.doi: 10.2118/426-
PA.
[9] D. B. JaynesandA. SRogowski.(1983),
“Applicability of Fick’s law to gas
diffusion”, Soil Sci. Soc. Am. J. 47, 425–430.
[10] SMaudgalya, R. M. Knapp, and M. J.
McInerney (2007). “Microbially enhanced
oil recovery technologies: A review of the
past, present and future”. SPE-106978
presented at the Production and Operations
Symposium, Oklahoma City, Oklahoma,
USA,
[11] U. Aslam.(2009). “Mechanisms of microbe
propagation in heterogeneous porous media
and analysis of various MEOR processes
involved in microbe transportation”. SPE-
119010 presented at Middle East Oil and
Gas Show and Conference, Bahrain,
Kingdom of Bahrain, 15–18 March.
[12] F.I.Stalkup..(1983). “Miscible
Displacement” (Soc. Pet. Eng. Monograph
Ser.), Vol. 8, Soc. Pet. Eng. of AIME,
Dallas.

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Ab04603165169

  • 1. Nmegbu Int. Journal of Engineering Research and Applications www.ijera.com ISSN : 2248-9622, Vol. 4, Issue 6( Version 3), June 2014, pp.165-169 www.ijera.com 165|P a g e Model for The Diffusionof Biogenic Gases In Heterogeneous Reservoirs Undergoing Transient Flow Nmegbu, Chukwuma Godwin Jacob * *(Department of Petroleum Engineering, Rivers State University of Science and Technology, Nigeria) ABSTRACT Microbially enhanced petroleum reservoirs confirms a recovery of about 30-40 % residual oil, with an integral composition of wide range of oil recovery mechanisms including wettability alteration by biosurfactant production, selective plugging of highly permeable channels by biopolymer production, creating fluid flow channels in carbonate reservoirs by rock dissolution attributed to bioacid formation, and a range of other exploitable recovery techniques. This study presents an investigation of biogenic gas produced in-situ and its concentration profile across the reservoir. An increasing concentration trend in the grids was observed and these increments were owed to the fact that diffusion of the biogenic occurred. It was also observed that after 40days of Desulfovibro injection, the produced CO2 across the reservoir was tending towards being even in values of concentration, implying that diffusion rate was approaching a zero value. Also, the distorting effect of reservoir heterogeneity on biogenic gas concentration profile was also resolved by adopting the method of averaging for permeability and porosity in the reservoir. Keywords–Biogenic gases, Concentration, Heterogeneity, Microbes I. INTRODUCTION Microbial enhance oil recovery is an aspect of biotechnology that utilizes the potentials of some microbes injected into petroleum reservoirs for certain oil recovery mechanisms. These mechanisms attempt to overcome the some obstacles in efficient oil recovery such as the low permeability, high viscosity of the residual crude oil, and high oil-water interfacial tensions that may result in high capillary forces retaining the oil in the reservoir rock, etc. [1].MEOR involves the use of specific bacteria capable of producing useful metabolites in-situ such as gases, acids, surfactants, solvents and polymers in order that their presence will aid further reduction of residual oil left in the reservoir after secondary recovery[1], [2]. Webb in 1998 outlined the production of biogenic gases creates a free gas phase that can account for incremental oil recovery in MEOR processes either by reduction of the oil viscosity by solution of the gas in the oil, or by re- pressurization of the reservoir through gas cap formation, causing displacement from trapped capillaries and enhancing mobilization of the oil to the producing wells [3], [4]. The most important gas- producing microbes include; Clostridium, Desulfovibrio, Pseudomonas, and some methanogen. The composition of the biogenic gas from bacteriametabolism can include carbon dioxide, hydrogen, methane and nitrogen [5], [6], [7]. This study not only aims at investigating the concentration profile of produced biogenic gases, but also tends to investigate the effects of reservoir heterogeneity on biogenic gas distribution across the reservoir. The knowledge of biogenic gas concentration profiles in heterogeneous reservoirs are of great importance when accounting for the overall recovery efficiency of the MEOR process either by solution gas drive or gas-cap formation.[2], [8]. II. METHODOLOGY 2.1 Microbial choice An anaerobic microbe was selected for this investigation. Its morphology confirms its ability to produce bioacids and biogases with a higher production of the later. Desulfovibrio having an excellent transport mechanism, tolerable pH range and extremely low decay rate in subsurface conditions proves the suitable microbe for this study. The biogenic gas produced was assumed to be Carbon dioxide (CO2) after microbial utilization of the residual hydrocarbon. 2.2 Biogenic gas concentration and diffusion account. Assuming that the rate at which microbes act on the oil is = microbial injection rate and Microbial injection rate = biogenic gas production rate (1) We can say that the governing statement above automatically tends to neglect microbial retention time. We Recall that the volume of biogenic gases produced = gas generated in pore volume of the reservoir, PV. (2) Where RESEARCH ARTICLE OPEN ACCESS
  • 2. Nmegbu Int. Journal of Engineering Research and Applications www.ijera.com ISSN : 2248-9622, Vol. 4, Issue 6( Version 3), June 2014, pp.165-169 www.ijera.com 166|P a g e PV= Ah 𝜙(1-Sor) (3) A = area of the reservoir (ft2 ) H is the height of the reservoir (ft) ϕis the average porosity of the heterogeneous reservoir The rate at which these biogenic gases are formed is given as; volume of produced biogenic gases microbial retention time = Vbg ϑ = Ah ϕ(1−Sor) ϑ (4) But recalling (1), we have Biogenic gas production rate= Ah 𝜙(1 − Sor) (5) Consider the horizontal reservoir below undergoing microbial injection for Improved oil recovery with no flow boundary condition and rectangular geometry with a microbial injection rate of 500bbl/day (microbe- water mixture). Fig.1 schematic of discretized reservoir undergoing microbial injection Assuming Recalling the gas flow equation in 1D ∂ ∂x AK μg Bg ∂C ∂x ∆x + qg + qw Rsw + qoRso = Vb ϕCt αc ∂C ∂t (6) Assuming that the biogases produced is not soluble in the residual oil and water, we have; ∂ ∂x β AK μg Bg ∂C ∂x ∆x + qg = Vb ϕCt αc ∂C ∂t (7) Recalling Fick’s law and replacing the transmissibility coefficient with diffusivity coefficient. Writing the above in a 2nd order derivative, we have ∂2C ∂x2 −Dg AK μg Bg ∆x + qg = Vb ϕCt αc ∂C ∂t (8) For a second order derivative, the equivalent finite difference notation for the LHS in terms of concentration is given as ∂2C ∂x2 = Ci−1 t −2Ci t +Ci+1 t ∆x2 (9) For the RHS, change in concentration is with respect to time, the equivalent finite difference approximation is given as ∂C ∂t = Ci t+1 −Ci t ∆t (10) (8) can be written as Ci−1 t −2Ci t +Ci+1 t ∆x2 −Dg AK μg Bg ∆x + qg = Vb ϕCt αc Ci t+1 −Ci t ∆t (11) Rearranging the above we have Ci−1 t − 2Ci t + Ci+1 t −Dg A K μg Bg ∆x + qg = Vb ϕCt αc ∆t (Ci t+1 − Ci t ) (12) Considering the heterogeneous reservoir system with varying permeability values shown below, we recall the method of averaging for permeability. Fig 2. A rectangular heterogeneous reservoir with varying K values Kavg = Li n i=1 Li Ki n i=1 (13) (12) now becomes Ci−1 t − 2Ci t + Ci+1 t − Dg A Kavg μg Bg ∆x + qg = Vb ϕCt αc ∆t (Ci t+1 − Ci t ) (14) The diffusion of the biogenic gases produced by the microbe will be accounted for using the biogas concentration profile across the heterogeneous reservoir at various positions i and time t. Setting −Dg A Kavg μg Bg ∆x as the diffusive flux, J’ and neglecting the negative sign, we have; Ci−1 t − 2Ci t + Ci+1 t J′ + qg = Vb ϕCt αc ∆t (Ci t+1 − Ci t ) (15) Rearranging the above J′ Ci−1 t − 2 J′ Ci t + J′ Ci+1 t + qg = Vb ϕCt αc ∆t (Ci t+1 − Ci t ) (16) Accounting for biogas concentration at various reservoir positions, we multiply through by αc ∆t Vb ϕCt αc ∆t Vb ϕCt J′ Ci−1 t − 2 J′ Ci t + J′ Ci+1 t + αc ∆t Vb ϕCt qg = Ci t+1 − Ci t (17) Setting transient tern as Z, we obtain Z J′ Ci−1 t − 2 J′ Ci t + J′ Ci+1 t + Zqg = Ci t+1 − Ci t (18) The biogenic gas prediction equation in terms of concentration with respect to position at any given time is thus
  • 3. Nmegbu Int. Journal of Engineering Research and Applications www.ijera.com ISSN : 2248-9622, Vol. 4, Issue 6( Version 3), June 2014, pp.165-169 www.ijera.com 167|P a g e Ci t+1 =Ci t + Z J′ Ci−1 t − 2 J′ Ci t + J′ Ci+1 t + Zqg (19) Assumptions  Mass transfer occurs only by diffusion.  Negligible gas influx, ie no flow boundary condition  Gas composition is homogenous, only CO2 produced.  Diffusion occurs predominantly in the horizontal direction  Metabolite production mostly biogenic gases.  Isothermal system as reservoir fluctuations in temperature is regarded minimal.  Negligible capillary action.  No break in injection rates of microbes  Microbial decay not considered.  No indigenous microbe present.  Chemotaxis not considered.  No substrate and metabolite adsorption on the pore walls, so Langmuir  Equilibrium isotherm not considered.  Gravitational effects considered negligible.  Electrokinetic effects negligible.  Unsteady state flow conditions.  Other factors affecting growth rates such as salinity and pH remains constant. III. RESULTS AND DISCUSSION Table 1.Reservoir and microbial parameters for biogenic gas concentration analysis. Parameters Value Produced biogenic gas diffusion coeff, Dbg 1.05× 10-6 ft2 /day K1 K2 K3 K4 150, 200, 180, 129 (mD) Ф1, Ф2, Ф3, Ф4 20, 36, 30, 16 Initial gas concentration, Cgi 100lb/ft3 Microbial injection rate qg 500bpd Reservoir thickness ∆𝑦 50 ft Reservoir grid length ∆𝑥 1000ft Reservoir breadth ∆𝑧 1500ft Reservoir length 4000ft Time increment, ∆𝑡 10days Volume conversion factor, 𝛼 𝑐 5.615 Total compressibility, 𝐶𝑡 3.0× 10-6 Gas formation volume factor, 𝐵𝑔 0.000512scf Gas viscosity, 𝜇 𝑔 0.017cp Assuming that microbial injection rate = rate at which microbes act on the oil= biogenic gas production rateCalculating constants (diffusivity component and transient term) J′ = Dg AKavg μgBg∆x = 9.23 Z = αc∆t VbϕCt = 0.959 Recalling (19), Ci t+1 =Ci t + Z J′ Ci−1 t − 2 J′ Ci t + J′ Ci+1 t + Zqg(20) The concentration profile of the diffusing biogenic gas is then predicted using the above and applying the following boundary conditions. C1 = Co, for all time steps. C4 = C5, for all time steps. No net or bulk influx of biogenic gases at the boundaries of the reservoir. The table below shows the concentration of the biogas across the reservoir. Table 2.Deduced concentration values of Produced biogenic gas across the heterogeneous reservoir for various time steps. Grid blocks (ft) 1 2 3 4 𝐶𝑖 10 (lb/ft3 ) 580 524 476 433 𝐶𝑖 20 (lb/ft3 ) 585. 05 535.5 7 490.66 484 𝐶𝑖 30 (lb/ft3 ) 591. 41 545.2 4 532.41 526.8 6 𝐶𝑖 40 (lb/ft3 ) 595. 07 579.4 0 569.10 564.2 4 Fig 3. Plot of CO2 concentration against time in individual reservoir grids Fig 3 shows the increasing concentration of biogenic gases in each discrete point of the reservoir at different periods during the microbial action. Initial gas concentration in the reservoir was recorded 0 100 200 300 400 500 600 700 0 20 40 60 Biogasconcentration(lb/cft) Time (days) GB1 GB2 GB3 GB4
  • 4. Nmegbu Int. Journal of Engineering Research and Applications www.ijera.com ISSN : 2248-9622, Vol. 4, Issue 6( Version 3), June 2014, pp.165-169 www.ijera.com 168|P a g e to be 100lb/ft3 , but was observed to increase to certain levels during the breaking down process of the residual crude by the microbes. The trend observed in virtually all the grids shows that biogas distribution across the heterogeneous reservoir was tending towards the same value at a higher time step of 40 days. For grid block 4, which is farther away from the gas production point (injector), its trend with time shows a continuous increment in gas concentration and will only attain a value equal those closer to the injector only by continuous biogas diffusion phenomenon. Fig 4. Biogas concentration profile across the horizontal reservoir It is established from the diffusion laws that whenever equilibrium is reached, diffusion stops [5], [9]. This statement is evident in Fig 4, showing the concentration profile of the diffusing biogenic gas for various reservoir positions of investigation at different time. The concentration profiles of Biogenic gases can only be ascertained if there is transport of the gaseous phase (diffusion) through the porous media. The linear and systematic orderly patterns observed in the concentration profile across the reservoir are traceable to the assumption that the produced biogenic gases are insoluble in the oil. This implies that since these gases do not go into solution with the oil to cause viscosity reduction, these produced biogenic gases continuously form a strong gas cap layer that will re-pressurize the reservoir to enhance oil flow. Consideration of gas solubility in oil will cause a distortion in the gas concentration profile across the reservoir. Another explanation to the regular concentration profile seen above is the adaptation of the method of averaging for permeability and porosity. For the horizontal heterogeneous reservoir of varying rock properties, it is expected of the profile to take an irregular pattern [8]. IV. CONCLUSION Biogenic gases produced in-situ is a major contributory factor in the whole microbial recovery process. The above figures have revealed that the concentration of the biogenic gas across the reservoir tends to be evenly distributed across the reservoir through the diffusion process. Since the gases do not go into solution with the residual oil in the reservoir, it should be, concluded that recovery mechanism of the microbially produced biogenic gases is by reservoir re- pressurize by gas cap formation. It is therefore recommended that further study and investigation should be conducted to ascertain relationships for heterogeneous biogenic gas compositions and gases solubility so as to account for both viscosity reduction of the heavy crude and gas cap formation. V. ACKNOWLEDGEMENTS The authors will like to acknowledge the countless relentless efforts ofEzeagala Anthony and Pepple Daniel Dasigha in making this research work possible. REFERENCES [1] L.K. Jang, M. M. Sharma and T. F. Yen.(1984). “The transport of bacteria in porous media and its significance in microbial enhanced oil recovery”. SPE- 12770 presented at California Regional Meeting, Long Beach, California, USA, pp 11–13. [2] D. Dejun, L. Chenglong, J. Quanyi,W. Pingcang, .and F.L. Dietrich.(1999). “Systematic Extensive Studies of Microbial EOR Application Results in Chanqing Oilfield.” SPE Paper 54380, in proceedings of the 1999 SPE Asia Pacific Oil and Gas Conference and Exhibition, Jakarta, Indonesia, April 20th -22nd , 1999. PP 1-9. [3] S. W. Webb,(1998).“Gas diffusion in porous media – evaluation of an advective- dispersive formulation and the dusty-gas model for binary mixtures”.J. Porous Media 1, 187–199. [4] D. C. Thorstenson, and D. W. Pollock.( 1989): “Gas transport in unsaturated zones: multi-component systems and the adequacy of Fick’s laws”. Water Resour. Res. 25, PP 477–507. [5] E. Fathi, and I. Y. Akkutlu.(2008) .: “Counter-Diffusion and Competitive Adsorption Effects During CO2 Injection and Coalbed Methane Production”, SPE 115482, paper presented at the 2008 SPE 0 100 200 300 400 500 600 700 0 10000 20000 30000 40000 50000 Biogasconcentration(lb/cft) Grid block distance (ft) 10 days 20 days 30 days 40 days
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