transporte de np en medio poroso

Upload: roberto-g-silva

Post on 03-Jun-2018

224 views

Category:

Documents


0 download

TRANSCRIPT

  • 8/12/2019 Transporte de NP en Medio Poroso

    1/8

    Powder Technology 192 (2009) 195202

    Contents lists available at ScienceDirect

    Powder Technology

    journal homepage: www. el sevier. com/l oca te/ powtec

    Experimental study and mathematical model of nanoparticle transport in porous

    media

    Binshan Ju , Tailiang Fan

    School of Energy Resources, Key Laboratory of Marine Reservoir Evolution and Hydrocarbon Accumulation Mechanism, Ministry of Education, China University of Geosciences (Beijing), Beijing

    100083, China

    a r t i c l e i n f o

    Article history:Received 22 August 2008Received in revised form 7 November 2008

    Accepted 22 December 2008Available online 7 January 2009

    Keywords:NanoparticleOil recoveryWater injectionPorous mediaMathematical model

    a b s t r a c t

    Two types of polysilicon nanoparticles (PN) were used in oil fields to improve oil recovery and enhance water injection

    respectively in this work. The physical properties of the nanoparticles were studied experimentally, and pore characteristics of

    sandstone were investigated by mercury injection experiments. The adsorption experiments of lipophobic and hydrophilic

    polysilicon nanoparticles (LHPN) were conducted to testify wettability change (from oil wetting to water wetting) of

    sandstone surface, and the nanoparticles attached to pore walls were observed bya transmission electron microscope (TEM). A

    mathematical model to describe the nanoparticles transport carried by two-phase flow in random porous media was presented

    and a numerical simulator was developed to simulate two application examples of the nanoparticles in oil fields. An important

    discovery is that water-phase permeabilities of these sandstones increase from 1.6 to 2.1 times of their original values.

    However, there are decreases in their absolute permeabilities because of nanoparticle adsorption on pore surfaces and

    nanoparticle capture at pore throats. The important parameters such as the distributions of porosities and permeabilities, the

    changes in water injection capability and oil recovery are obtained successfully by numerical simulation approach.

    Furthermore, the permeabilities obtained from numerical simulation have a good match with experimental data. The

    conclusion that polysilicon nanoparticles are effective agents for enhancing water injection capability or improving oil

    recovery can be safely drawn.

    2009 Elsevier B.V. All rights reserved.

    1. Introduction

    Nanometer particles have many special physical effects [1]and they can

    be made in different ways [25]. Their applications in chemicals, metallurgy,

    ceramics, medicines and other fields have been reported frequently in recent

    years. Ding and Wen [6]presented a theoretical model for predicting particle

    concentration and velocity fields of nanofluids flowing through a pipe. By

    contrast, the flow paths in random porous media look like network

    interconnected by pore throats and pore bodies. The sandstone in oil

    formation can be regarded as a kind of complicated random porous media and

    the transport process of nanoparticles carried by fluids in sandstone belongs to

    multiphase flow.

    As far as it goes, only few papers address the issues of the application ofnanopowders in oilfields to enhance water injection by virtue of changing the

    wettability of reservoir rock through their adsorption on porous walls of

    sandstones. Ju and Dai [7] reported that one nanometer-scale polysilicon

    material could change the wettability of porous surfaces of sandstone and

    consequently have effects on the flows of water and oil in oil formation when

    the suspension of the nanoparticles is injected into an oil reservoir. There are

    only few papers [811]dealing with mathematical modeling of fine particles

    migration in formation;

    Corresponding author.

    E-mail address:[email protected](B. Ju).

    0032-5910/$see front matter 2009 Elsevier B.V. All rights reserved.

    doi:10.1016/j.powtec.2008.12.017

    however, none of which deals with the migration and adsorption of

    nanometer-scale materials in porous media.During PN transport in porous media, there is a mass exchange between

    the PN on pore framework and the PN in fluids by adhering to pore walls,

    detaching from pore walls and blocking at pore throats. In addition, the

    covering of PN on pore walls will change the wettability of pore surfaces. To

    understand the PN transport behaviors in random porous media, theoretical

    and experimental approaches were used in the present investigation and a

    mathematical model for predicting PN transport performances and its effects

    on two-phase flow behaviors was developed. Two examples, enhancing water

    injection capacity of low permeability reservoirs and improving oil recovery

    of high permeability reservoirs, were also studied by numerical simulation

    approach on the simulator developed in current work.

    2. Experimental studies on physical properties of the nanoparticles, random

    porous media and flowability with HLPN treatment

    2.1. Physical properties of the polysilicon nanoparticles

    The PN in this study is a kind of modified ultra-fine powder (see Fig. 1),

    which is made from SiO2and an additive. The shape of ananoparticle looks

    like an approximate sphere when observed under a TEM and the particle

    diameters are from 10 to 500 nm (see Fig. 2).

  • 8/12/2019 Transporte de NP en Medio Poroso

    2/8

    196 B. Ju, T. Fan / Powder Technology 192 (2009) 195202

    Fig. 3. Particle size distribution curve.Fig. 1. The nanopower in a beaker.

    Fig. 3 indicates that the sizes of the particles have a quasi-Gaussian

    distribution. The bulk density of the nanopowder is 0.056 g/cm3. According

    to wettability of the surface of the polysilicon nanoparticles, they can be

    classified into two types: lipophobic and hydrophilic polysilicon nanoparticle

    (LHPN) and hydrophobic and lipophilic polysilicon nanoparticle (HLPN).

    2.2. Physical properties of random porous media (sandstone)

    Sandstone oil and gas reservoir is one major type of reservoirs discovered

    by the petroleum companies in the world. Therefore sandstone was selected to

    be as an example of random porous media. As we know, sandstone,

    composed of grains of different sizes, is porous media deposited under the

    combination of consolidation and compaction through a long geological

    period. Sandstone contains voids dispersed in a solid matrix and it can be

    considered equivalent to a system in which the solid particles and void phases

    are randomly dispersed in such a way that both phases form continuous

    conducting paths through the medium. Void space is generally known as the

    pore space as it is known to consist of randomly distribution pores of various

    shapes and sizes. The void spaces in sandstone can be divided into pore

    throats (the narrowest segments of pores) and pore chambers (the widestsegments of pores). The sizes of pore throats in sandstone are from 0.5 to 5.0

    m, and the size of pore chamber is from 5.0 to 50.0 m [12,13].

    In the laboratory, the physical properties of sandstone cores, obtained

    from the drilling wells in H.Z.J oil field, China, are studied by mercury

    injection experiments. The main data of the sandstone cores used in these

    experiments are shown in Table 1. The data obtained by mercury injection

    experiments are shown in Fig. 4. It indicates that the radii of most pores fall in

    the range of 0.4 to 10 m. The pores of radii less than 0.4 m have little

    contribution for mercury permeation.

    Fig. 2. The images of polysilicon nanoparticles observed under TEM.

    2.3. Experimental studies on the effects of nanoparticles on the physical

    properties of the porous media

    The experimental data from the above section show that the sizes of

    polysilicon particles are from 10100 to 5.010

    2 nm, and pore radii of

    sandstone are in the range of 6.010

    0

    6.310

    4

    nm. In the process of thenanoparticle transport with flow in porous media, a particle larger than a pore

    throat may block at the pore throat. Two or more than two particles that sizes

    are slightly less than a pore throat may bridge at the pore throat. If the sizes of

    particles are far less than pore sizes, the nanoparticles can be adhered to the

    pore walls. The theoretical analysis of adsorption is given in the Ref. [7].

    Generally, the wettability of polysilicon particles and the wettability of

    sandstone pore walls are different. Therefore, the adsorption of polysilicon on

    sandstone pore walls leads to wettability change of pore walls. The following

    experiments were conducted to study the effects of polysilicon nanoparticles

    on the physical properties of the porous media.

    2.4. Macroscopic experiment on wettability change

    In order to study the wettability change of sandstone surface, themeasurement of wetting angles was conducted. First, a rock slice sawed froma block of sandstone was furbished on ultra-fine sand paper; then, a drop of

    water was placed on the rock slice surface and the wetting angle ( 1) wasmeasured; finally, the rock slice was immersed in an aqueous LHPN solution

    for 2 h and the wetting angle (2) was measured. Fig. 5(a) indicates that the

    wetting angle (1) is much larger than /2, while (b) shows that the wetting

    angle (2) after LHPN treatment becomes much smaller than /2. The changein wetting angles indicates the wettability of surface of reservoir rock can bechanged from oil-wet to water-wet by adsorbing LHPN. The image (c) of

    wetting angle (3) of the rock immerged in pure water for 2 h shows that 3is

    slightly higher than /2. It indicates that the wettability in this case is weakoil-wetting.

    2.5. Microscopic adsorption observation under a TEM

    Two furbished slices from an oil-wet sand core were first extracted with

    benzene, then, one was directly observed under a TEM, the other was

    observed under a TEM after it was dipped in an aqueous LHPN solution for 2

    h. Fig. 6(a) is an image of sandstone surface without adsorbing LHPN. Fig. 6

    (b) shows that the adsorbed LHPN looks like a layer of white frost.

    2.6. Experimental study on flowability with HLPN treatment

    Dynamic core displacements were conducted to study the fluid flowability

    in porous media after treatment with HLPN under the reservoir temperature

    and pressure.

  • 8/12/2019 Transporte de NP en Medio Poroso

    3/8

    B. Ju, T. Fan / Powder Technology 192 (2009) 195202 197

    Table 1The parameters of sandstone cores.

    Sandstone core name Depthaof core, m Length of Rock density, Diameter of Porosity,% Permeability, Sedimentarysandstone core, cm g/cm3 sandstone core, cm 103m2 microfacies

    RC3-1 2271.9 2.20 2.15 2.496 21.40 352.1 River channel faceSS6-1 2365.1 2.40 2.04 2.495 25.12 150.5 Sand sheet faceDB4-1 2374.4 2.42 2.00 2.495 22.25 79.3 Distal Bar faceaThe depth of core is the location of the core before it was drilled. For instance, RC3-1 core was buried underground 2271.9 m from well head before it was drilled.

    The displacement routine for each core is listed in the following steps:

    (1) Heat the core holder with core sample up to a constant temperature of

    80 C.

    (2) Flooded by diesel oil until the flow rate reaches at a constant and the

    outflow shows no water.

    (3) Flooded by brine until the flow rate reaches at a constant and

    the outflow shows no hydrocarbon, then record overall differential

    pressure, Pi(=PinPout) and flow rate qiw(ml/s).

    (4) Flooded by the suspension of HLPN in diesel oil until 10 pore volumes

    (PV) of the suspension pass the core.

    (5) Flooded by brine again until the flow rate reaches at a constant

    and the outflow shows no diesel oil, then record overall differential

    pressure, P (=PinPout) and flow rate qw(ml/s).

    As we know, the formation near the wellbore is very important where thepressure drop of the oil-field mainly depletes [6]. The mobile oil in thevicinity of injection well has been displaced by water, so the flow in the poresof the reservoir rock around wellbore can be regarded as single-phase flow.Therefore, the water injectability can be evaluated by comparing the effective

    perme-ability of water, Kwb, (= KKrwb), before HLPN treatment, with the

    effective permeability of water, Kwa(= KKrwa) after the treatment as long as

    the maximum water saturation is reached (only water phase flow). Theeffective permeability of water can be calculated by Darcy's law on condition

    that the length (L), cross-sectional area (A) of a core, viscosity of water ( w),

    overall differential pressure ( P) and injection rate (qw) are measured.

    Kw=q

    Aww

    PL

    :

    The parameters of rock cores and experimental results are shown in Table

    2. The data inTable 2 show that the effective permeabilities of water after

    HLPN flooding are improved 1.6272.136 times for the four cores.

    3. Mathematical model to describe the nanoparticle transport process in

    random porous media

    3.1. Assumptions

    The model simulating two-phase displacement is based on the following

    assumptions:

    (1) The flow is one-dimensional under isothermal condition. The rock and

    fluids are supposed to be incompressible.

    (2) The porous media is heterogeneous.

    (3) The oil and water flows in porous media follow Darcy's law and the

    gravity force is neglected.

    (4) The nanoparticles are discretized into n size intervals.(5) The viscosity and density of the fluids are constant and oil and water

    are Newtonian fluids.

    3.2.Transport of fluids in porous media

    Since the flows of oil and water in porous media follow Darcy's law, the

    continuity equations of oil (o) and water (w) phases for incompressible

    Newtonian flow are given by the following equation:

    A K P_Sl _ l _= 0 ;l = o;w; 1At x

    l

    where x is the distance from the inlet of the sand core, t is time, is the

    porosity of the porous media, Sl, l and Pl are saturation, viscosity, and

    pressure of phase l, respectively, and Kl(=Krl) is the effective permeability ofphase l. The expression [14]for capillary force is

    Pc= PoPw= a + bsw=1 + csw; 2

    where a, b and c are empirical parameters. swis water saturation.

    Fig. 4. Mercury saturation histogram and cumulative permeability contribution curve.

  • 8/12/2019 Transporte de NP en Medio Poroso

    4/8

    198 B. Ju, T. Fan / Powder Technology 192 (2009) 195202

    Fig. 5. Wettability change of sandstone after absorbing LHPN.

    3.3. Transport of PN in porous media

    Since PN have wettabilities, LHPN exist in the water, and HLPN exist in

    the oil phase. Inasmuch as the sizes of PN are in the range of 10 to 500 nm,

    Brownian diffusion should be considered. Thus, the continuity equation for

    size interval i of PN can be expressed as

    AC AC C

    _li;l

    + _Sli;l

    _

    l i;li;l

    + Ri;l= 0; 3Ax At x

    x

    where i =1,2n.The initial and boundary conditions, respectively, for Eq. (3) are given by

    Ci;l= 0;t = 0; 4

    Ci;l

    =

    Ci;l;in

    ;

    x

    = 0; 5

    where Ci,lis the volume concentration of PN in interval i in phase l, D i,lis the

    dispersion coefficient of PN in size interval i in phase l, Ri,lis the net rate of

    loss of PN in interval i in phase l, and C i,in is the con-centration of theinterval i of PN in the injected fluids.

    3.4. Net loss rate of PN in transport process

    The pore spaces in sandstone mainly consist of interconnected pore bodies

    and pore throats. For the PN transport carried by fluid stream in the porousmedia, two types of particle retention in the pores may occur: deposition on

    pore surfaces and blockage in pore throats. For the retained particles on pore

    surfaces, they may desorb for hydrodynamic forces, and then possibly adsorb

    on other sites of the pore bodies or get entrapped at other pore throats. By

    modifying the Ju and Dai's model [7], Ri,lin Eq. (3) is given by

    Ri;l

    =

    Ai;l

    +

    Ai;l

    ; 6At Atwhere i,lis the volume of PN i in contact with phase l available on the pore

    surfaces per unit bulk volume of sandstone, i,l is the volume of PN i

    entrapped in pore throats from phase l per unit bulk volume of sandstone dueto plugging and bridging.

    According to Gruesbeck and Collins [15], there exists a critical velocity

    for surface deposition, below which only particle retention occurs and above

    which retention and entrainment of PN particles take place simultaneously. A

    modified Gruesbeck and Collins's model for the surface deposition is

    expressed byA

    i;l

    d i l

    ul

    Ci l ;when ulbulc

    =_

    d;i;;lu

    ;lCi;l

    ; e;i;li;lul ulc ;when ulNulc : 7At

    The initial condition for Eq. (7) is

    i;l= 0;t= 0: 8In Eq. (7), d,i,l and e,i,l are rate coefficients for surface retention and

    entrainment respectively of PN in interval i in the phase l, and u lc is the

    critical velocity for the phase l to entrain particles.

    The rate equation for the entrapment of the particles in interval i in pore

    throats in phase l can be written as

    Ai;l=

    pt;i;l

    ul

    Ci;l

    ; 9At

    where p,i,lis a constant for pore throat blocking. The initial condition for Eq.

    (9) is

    i;l= 0;t= 0: 103.5. Change of porosity and absolute permeability

    Both PN deposition on the pore surfaces and blocking in pore throats may

    lead to the reduction in porosity and permeability. The instantaneous porosity

    is expressed by

    _= _0_; 11

    where denotes the variation of porosity by release and retention of PN inthe porous media, and it is expressed by

    _

    =

    i;l+

    i;l

    : 12

    According to Ju and Dai's model [7], the expression for the instantaneous

    permeability due to the deposition and blocking of particles can thus be

    written as

    K = K0 1f kf+ f _=_0&n; 13

    where K0 and 0 are initial permeability and porosity, K and are

    instantaneous local permeability and porosity of the porous media, kf is a

    constant for fluid seepage allowed by the plugged pores, and f is the fractionof the original cross-sectional area open to flow.

    3.6. Evaluation of relative permeability

    As we know, the wettability of pore surfaces is the most important factor

    to determine the relative permeability of a porous media. The PN retention in

    porous media may induce wettability changes and the shape of relative

    permeability curve can also be changed. If Vi,lis the

    Fig. 6. TEM images of the sandstone surfaces.

  • 8/12/2019 Transporte de NP en Medio Poroso

    5/8

    B. Ju, T. Fan / Powder Technology 192 (2009) 195202 199

    Table 2Parameters of cores and experimental results.

    The core Cross-sectional Length of The effective The effective wa wbame area, A, cm2 core, L, cm permeability permeability

    measured before measured afterHLPN flooding, HLPN flooding,Kwb, 10

    3m

    2 Kwa103m2N1 4.91 7.91 4.434 9.471 2.136M1 4.91 7.23 2.133 4.212 1.975M2 4.91 7.62 4.345 8.783 2.021M3 4.91 7.14 1.162 1.891 1.627

    size interval i entrapped in pores, the total PN retention volume satis fies the

    following equation:

    nV = Vi;l: 14

    i = 1;l = w;o

    Supposing the spherical particles in size interval i touching each other in

    the form of point contact and using the real volume of particles as the

    denominator, the specific area of the particles in size interval i can be defined

    asAt n

    3d2 6

    sbi= =i i

    = : 15V 61ni3di3 diSupposing i,lis the PN volume in interval i adsorbed on the pore

    surfaces and is the volume of PN in interval i entrapped in porei,l

    throats per unit bulk volume of the porous media. PN adhered to the pore

    walls first spread as a single layer, the surface area for particles in interval i is

    given by

    si=_

    i;l+ i;l

    _

    sbi: 16The total surface area in contact with fluids for all the size intervals of PN

    per unit bulk volume of the porous media is calculated by

    n n6

    s = si= i;l+i;l

    _

    ;

    17

    i = 1 i = 1;l = w;o_

    diwhere is the surface area coefficient. The specific area of a sand core can be

    calculated by the following empirical equation [16],

    _s= 7000_

    rffiffiffiffiffi :

    18K

    We suppose that the relative permeabilities of water and oil phases are,

    respectively, Krwj and Krojat a water saturation, Swj. When s s, the totalsurfaces per unit bulk volume of the porous media are

    Table 3Parameters of HLPN used for numerical simulation.

    HLPN Diameter HLPN d,i,l, e,i,l, p,i,l, i,l, ulc,composition of HLPN, concentration, cm cm cm cm s cm s

    umber nm cm3/cm3C1 40 0.004 0.16 0.3 0.0128 0.00056 0.00046C2 50 0.0065 0.2 0.24 0.02 0.00036 0.00058C3 60 0.009 0.24 0.2 0.0288 0.00025 0.00069C4 70 0.01045 0.28 0.17143 0.0392 0.00018 0.00081C5 80 0.0075 0.32 0.15 0.0512 0.00014 0.00092C6 90 0.005 0.36 0.13333 0.0648 0.00011 0.00103C7 100 0.0035 0.4 0.12 0.08 0.00009 0.00115C8 150 0.002 0.6 0.08 0.18 0.00004 0.00172C9 200 0.00115 0.8 0.06 0.32 0.00002 0.0023C10

    300

    0.0009

    1.2

    0.04

    0.72

    0.00001

    0.00345

    Fig. 7. Concentration distribution of HLPN particles along the dimensionless distance at

    different injection PV.

    completely covered by PN adsorbed on pore body surfaces or entrapped in

    pore throats, and wettability is determined by PN. However, when s bs, onlypart of the surfaces per unit bulk volume of the porous media is occupied byPN.

    When the surfaces per unit bulk volume of the porous media arecompletely occupied by PN, the relative permeabilities of water and oil

    phases are taken as Krwj and Kroj respectively; otherwise, the relative

    permeabilities of water and oil phases are taken as a linear function of the

    surfaces covered by PN, that is, when 0 bs bs, the relative permeabilities ofwater and oil are given by

    Krwjp

    V= Krwj+

    Krwj

    V

    Krjw

    s 19sand

    KrojVKrowK

    rojp

    V= Kroj+ s: 20s

    4. The solution method to mathematical model

    The overall mathematical model is a nonlinear system that includes the

    continuity equations of oil (o) and water (w) phases (Eq. (1)), the convectiondiffusionadsorption equation (Eq. (3)), and a series of auxiliary equations.

    The finite-difference method is used for solving the nonlinear equation

    system. In this work, the Implicit-Pressure/Explicit-Saturation (IMPES)

    technique was used to solve the pressuresaturation equation (Eq. (1)) and an

    explicit method was employed to solve the convection-diffusion-adsorption

    equation (Eq. (3)). The solving procedures are: first, the pressure

    distribution is obtained by solving the mass balance equation; then, the

    velocity is calculated by Darcy's law; the PN concentration distribution in

    interval i is obtained by solving the convectiondiffusionadsorption Eq. (3);

    the new porosity , absolute permeability K, relative permeabilities of oil

    and water phases for

    Fig. 8. Porosity distribution along the dimensionless distance at different injection PV.

  • 8/12/2019 Transporte de NP en Medio Poroso

    6/8

    200 B. Ju, T. Fan / Powder Technology 192 (2009) 195202

    Table 4Comparisons of permeabilities between experimental and numerical results.

    Core name N101A N2B RZ1Before treatment, Kwb, 10

    m Experiment 1.400 4.330 1.130

    After treatment, Kwa, 103

    m2Kwa/Kwb

    Numericals 1.378 4.336 1.127Experiment 0.570 9.470 4.100Numericals 0.572 9.480 4.107Experiment 0.407 2.187 3.628Numericals 0.415 2.186 3.644

    Fig. 9. Permeability distribution along the dimensionless distance at different injection PV.

    each grid are calculated, and then return to the first step if maximum

    simulated time is not reached.

    5. Application examples and discussion

    This section gives two examples concerning oil field development. Since

    PN can adhere to sandstone pore walls and change the wettabilities of pore

    walls, it can be used in oil field-development to enhance oil recovery. The first

    example is that HLPN is used in a low permeability oil reservoir to enhance

    water injection capacity. The second one is that LHPN is used in a high

    permeability oil reservoir to improve oil recovery.

    5.1. Examples 1: Enhancing water injection capacity of a well in a low

    permeability reservoir

    Water injection into a low permeability reservoir either for pressure

    maintenance or for secondary oil recovery is very difficult for the following

    conflicts. On one hand, injection rates must be low enough to prevent

    formation damages from over pressuring and inducing unwanted fractures.

    On the other hand, these rates must be high enough to make the costly fluid

    injection process economic. Formation damages caused by clay minerals

    (Illite, Kaolinite, Calcium montmorillonite and Sodium montmorillonite)

    easily occur in low permeability reservoirs. Although some conventional

    stimulations, such as hydraulic fracturing [17,18]and acidizing [19,20], are

    used to improve the flow conductivity of low permeability reservoirs, the

    stimulations may fail to acquire expected designation for geological

    complexity. Wettability of reservoir rock pore walls can be changed into

    hydrophobic by HLPN adsorption, which supplies a new approach to enhance

    water injection capacity of wells in low permeability reservoirs.

    Numerical simulation approach is also used in the present work to study

    the transport performances of HLPN in porous media and its effects on

    physical characteristics of sandstone. The parameters of

    each composition of HLPN used for numerical simulation are shown in Table

    3.Fig. 7 gives the distribution of dimensionless concentration of C1 of

    HLPN from inlet (dimensionless distance is equal to 0.0) to outlet

    (dimensionless distance is equal to 1.0) of the sand core at different injection

    PV (1 PV is defined as the total porous volume of the simulation model at

    initial time). It indicates that the wave of HLPN concentration travels toward

    the outlet and the concentration curves become flatter and flatter with the

    increasing injection PV.Figs. 8 and 9 show that both the ratios of porosity (/0) and theratios of

    permeability (K/K0) decline with the increasing injection PV. For an injection

    volume, the ratios of porosity and permeability are smaller at the vicinity of

    inlet than those at the vicinity of outlet. The decrease in porosity andpermeability results from the HLPN adsorption on pore walls and capture inpore throats.

    Fig. 10 indicates that water injection capability (Iw/Iw0 = KwKrw/

    (KwoKrw0)) doesn't increases linearly with HLPN injection volume. The

    water injection capability reaches maximum at injection volume of 1.8 PV, so

    the 1.52.0 PV of injection with total concentration of 5 vol.% of HLPN is

    recommended to enhance water injection capability for low permeability

    oilfields. It is very difficult to measure porosity and permeability of each point

    along a sand core by experimental approach; however, the average porosity of

    a sand core can be obtained by experiments and the average permeability can

    be calculated by Darcy's law when having experimental data. Numerical

    results and experimental data are shown in Table 4.

    5.2. Examples 2: Improving oil recovery of high permeability reservoirs

    It is well known that the water-flood sweep efficiency in a slight water-

    wetting reservoir is lower than that in a strong water-wetting one. Since

    LHPN has an ability to increase the tendency of strong water-wetting by

    adsorption of LHPN on porous surfaces, it can be used to improve oil

    recovery in the oil fields flooded by water injection. The following simulation

    example is conducted to predict production performance with injection

    LHPN. The main parameters used the numerical simulation runs are shown in

    Table 5.This example clearly shows how we can use LHPN to enhance oil

    recovery. The one-dimensional numerical simulator developed in this work

    was used to study flooding performances displaced by LHPN solution of 5.0

    vol.%.Fig. 11 shows that the numerical results have good matches with

    experimental data. Fig. 12indicates that permeability declines

    Fig. 10. The relations between water injection capability (Iw/Iw0) and HLPN injectionvolume Iw/Iw0= KwKrw/(KwoKrw0).

    Table 5Parameters for simulation.

    Number of grid 40Grid size, dx/m 0.025Cross-sectional area/10

    4m

    2 5.100Original porosity, 0.254Original permeability/m

    2 0.300Original saturation of oil 0.730Viscosity of reservoir oil/mPas 5.100Viscosity of injection water/mPas 0.515Injection rate of water/10

    m s

    1.500

    Production rate of fluid / /10

    8

    m

    3

    s

    1

    1.500

  • 8/12/2019 Transporte de NP en Medio Poroso

    7/8

    B. Ju, T. Fan / Powder Technology 192 (2009) 195202 201

    Fig. 11. The comparison of permeability ratios between experimental and numerical results.

    (7) HLPN is suitable for enhancing water injection capacity for lowpermeability reservoirs, and LHPN can be used to improve oil

    considerably in the vicinity of injection inlet. The mechanism of this recovery.kind of formation damage caused by LHPN injection is same as that

    Nomenclaturecased by HLPN. Fig. 13shows that oil recovery has been improved to aA cross sectional area, m considerable extent from 52.2% to 69.8% after injection of 2.0 PV LHPN.a,b constants for capillary pressure correlations, PaThe recovery is improved 17.6%.c constants for capillary pressure correlationsThe simulation model is one-dimension, so the sweep efficiency is

    Ci volume concentration of interval i of PN particles, m m almost up to 100%. In an oil reservoir, the sweep efficiency can be onlyup to 4060% due to heterogeneity and the existence of well pattern Di dispersion coefficient of interval i in oil phase, m s

    dead area. Therefore, the recovery is approximately improved 7.04 to di diameter of interval i, m

    10.56% in an oil reservoir. f flow efficiency factorK absolute permeability of porous media, m

    6. Conclusion Kr relative permeability of porous mediaf constant for fluid seepage allowed by the plugged pores

    (1) The experimental data show that the sizes of the nanoparticles in P pressure, Paq injection rate or production rate, m s this study are in the range of 10 to 500 nm, and the diameters ofRi volume changing rate of PN particles in interval i in thethe nanoparticles approximately follow a normal distribution.

    (2) The mercury injection tests show that the pore radii of the water phase per unit bulk volume of the porous mediam m

    s sandstone fall in the range of 6.06.310 4 nm.

    S saturation(3) The change of wetting angles indicates that the wettability ofs total surface area in contact with fluids for all particles of PNsurface sandstone can be changed from oil-wet to water-wet by

    per unit bulk volume of the porous media, m m

    adsorbing LHPN.sv specific area of sand core, m m

    (4) Microscopic adsorption tests imply that these nanoparticles canbe adsorbed on pore surfaces of sandstones and in turn reduce t time, s

    u flow velocity, ms the pore radii.wc critical velocity for water phase, ms (5) An important discovery is the sandstones' effective permeabil-

    ities of water increase from 1.6 to 2.1 times of their original V total volume of retention of PN per unit bulk volume of theporous media, m m

    values in spite of the decease in their absolute permeabilities.i volume of particles i of PN available on pore surfaces per(6) The mathematical model presented in this paper is able to

    simulate successfully the transport process of nanoparticles in unit bulk volume of the porous media, m m

    i volume of particles i of PN entrapped in pore throats perrandom porous media, and numerical results have good matchwith experimental data. unit bulk volume of the porous media, m m

    x distance, m rate constant, m surface area coefficient

    porosity of porous media viscosity of fluid, Pas wetting angle

    Subscripts0 initial valuec critical value or capillary pressured depositione entrainmentfe flow efficiencyi one compositionpt pore throat

    Fig. 12. The distribution of permeability ratio by numerical simulating approach along o oildistance at different injection volume. w water

    g. . e re at ons etween o recovery an n ect ng vo ume o .

  • 8/12/2019 Transporte de NP en Medio Poroso

    8/8

    202 B. Ju, T. Fan / Powder Technology 192 (2009) 195202

    SI metric conversion factors1 cm 110 m1m 110 m1 nm 110 m1MPa 110 Pa

    1 mPa 1103Pa

    Acknowledgments

    The authors would like to thank Prof. Zhian Luan, the teachers and

    graduates, laboratory of displacement mechanism, U.P.C, East China, for

    their partial experimental work. The authors would also like to thank Dr.

    Guodong Jin, Institute of Mechanics, Chinese Academy of Sciences, and Dr.

    Faisal Qureshi, Department of Physics, to thank Faisal Qureshi, Department

    of Physics, Institute of Heavy Ion Physics Peking University, China, for their

    proof reading and improving the English expression.

    References

    [1] L.D. Zhang, Preparation and Application Technology for Ultrafine Powder, Sinopec Press,

    2001, pp. 2330, ISBN:780043970.

    [2] G.G. Chen, G.S. Luo, J.H. Xu, J.D. Wang, Membrane dispersion precipitation method to

    prepare nanoparticles, Powder Technol. 139 (2004) 180185.

    [3] J.F. Chen, Y.H. Guo, F. Wang, X.M. Wang, C. Zheng, Synthesis of nanoparticles withnovel technology: high-gravity reactive precipitation, Ind. Eng. Chem. Res. 39 (2000)

    948954.

    [4] R.Y. Hong, J.M. Ding, G.L. Zheng, Thermodynamic and particle-dynamic studies on

    synthesis of silica nanoparticles using microwave-induced plasma CVD, China

    Particuology 2 (2004) 207214.

    [5] J.F. Chen, L. Shao, Mass production of nanoparticles by high gravity reactive precipitation

    technology with low cost, China Particuology 1 (2003) 6469.

    [6] Y.L. Ding, D.S. Wen, Particle migration in a flow of nanoparticle suspensions, Powder

    Technol. 149 (2005) 8492.

    [7] B.S. Ju, S.G. Dai, A study of wettability and permeability change caused by adsorption of

    nanometer structured polysilicon on the surface of porous media[C],

    SPE77938, SPE Asia Pacific Oil and Gas Conference and Exhibition held in Melbourne,

    Australia, 810 October, 2002, pp. 915926.[8] X.H. Liu, Civian Faruk, Characterization and prediction of formation damage in two-phase

    flow systems, Paper SPE25429 Presented at the Production Operations Symposium Held

    in Oklahoma City, OK, U.S.A., March 2123, 1993, pp. 231238.

    [9] X.H. Liu, Civan Faruk, A multiphase mud fluid infiltration and filter cake formation model,

    paper SPE25215, SPE International Symposium on Oilfield Chemistry Held in New

    Orleans, LA, U.S.A., March 25, 1993, pp. 607614.

    [10] X.H. Liu, Civan Faruk, Formation damage and skin factor due to filter cake formation and

    fines migration in the Near-Wellbore Region, paper SPE 27364, SPE Symposium on

    Formation Damage Control Held in Lafayette, Louisiana, 710 February, 1994, pp. 259

    265.[11] S. Vitthal, M.M. Sharma, K. Sepehrnoori, A one-dimensional formation damage simulator

    for damage due to fines migration, paper SPE 17146, SPE Formation Damage Control

    Symposium held in Bakersfield, California, February 89, 1988, pp. 2936.

    [12] F.A.L. Dullien, G.K. Dhawan, Characterization of pore structure by a combination of

    quantitative photomicrography and mercury porosimetry, J. Colloid Interface Sci. 47

    (1974) 337349.

    [13] Kartic C. Khilar, Fogler Hscott, Migration of Fines in Porous Media, 1 edition, Springer,

    1999, pp. 3052, SBN-13: 978-0792352846.

    [14] E.C. Donaldson, N. Ewall, B. Singh, Characteristics of capillary pressure curves, J. Pet.

    Sci. Eng. 6 (1991) 249258.

    [15] C. Gruesbeck, R.E. Collins, Entrainment and deposition of fines particles in porous media,

    Soc. Pet. Eng. J. 24 (1982) 847855.[16] J.S. Qin, A.F. Li, Physics of Oil Reservoir, Publishing Company, U. P. C, 2001, pp.151152.

    [17] M. James, B. Amar McGowen, Ziada Abdelhak, Increasing oil production by hydraulic

    fracturing in the Hassi Messaoud Cambrian Formation, Algeria, SPE paper 36904, SPE

    European Petroleum Conference held in Milan, Italy, 2224 October, 1996, pp. 303309.

    [18] M.R. Jackson, M. Rylance, L.G. Acosta, Hydraulic fracturing of high productivity wells in

    a tectonically active area, SPE paper 38608, SPE Annual Technical Conference andExhibition Held in San Antonio, Texas, U.S.A., 58 October, 1997, pp. 425429.

    [19] K.M. Bartko, A.M. Acock, J.A. Robert, R.L. Thomas, A field validated matrix acidizing

    simulator for production enhancement in sandstone and carbonates, SPE paper 38170, SPE

    European Formation Damage Conference Held in The Hague, The Netherlands, 23 June,

    1997, pp. 283288.

    [20] C.N. Fredd, SPE, H.S. Fogler, Alternative stimulation fluids and their impact on carbonate

    acidizing, SPE paper 31074, the SPE International Symposium on Formation Damage

    Control Held in Lafayette, Louisiana, U.S.A., 1415 February, 1996, pp. 2122.