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Impact of Surfactant Impact of Surfactant Structure on Structure on Wettability and Wettability and Pore Pore-Scale Displacement Scale Displacement Mechanisms of Mechanisms of Non Non-aqueous aqueous-Phase Phase Liquids Liquids in Heterogeneous Rocks in Heterogeneous Rocks Gina Javanbakht Lamia Goual Lamia Goual Department of Petroleum Engineering University of Wyoming November 9 th 2016
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Page 1: Impact of Surfactant Impact of Surfactant Structure on ... · PDF file• Surfactant enhanced aquifer remediation ... Removal Removal Mechanisms Mechanisms ... NAPL layer causes asphaltene

Impact of Surfactant Impact of Surfactant Structure on Structure on Wettability and Wettability and PorePore--Scale Displacement Scale Displacement

Mechanisms of Mechanisms of NonNon--aqueousaqueous--Phase Phase Liquids Liquids in Heterogeneous Rocksin Heterogeneous Rocks

Gina Javanbakht

Lamia GoualLamia Goual

Department of Petroleum Engineering

University of Wyoming

November 9th 2016

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Introduction

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Contamination by nonaqueous phase liquids (NAPLs)

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NAPLsNAPLs

Light nonaqueous phase liquids (LNAPLs)

Dense nonaqueous phase liquids (DNAPLs)

• Crude oil

• Gasoline

• Coal tar

• Creosote• Gasoline

• Benzene

• Toluene

• Creosote

• Polychlorinated biphenyl

• Mercury

4

(U.S. Environmental Protection Agency, 2010)

• Asphaltene

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RRemediation emediation MMethodsethods

• Water flooding

• Thermal desorption

• Pump and treat

• In situ oxidation

• Nanoremediation• Nanoremediation

• Surfactant enhanced aquifer remediation (SEAR)

5

rP SolidNAPLBrineNAPLBrine

C

)cos(2 −−−= θγ

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SurfactantsSurfactants

Hydrophilic-lipophilic balance number (HLB)• Oil-in-water microemulsion (HLB >> 10)

• Water-in-oil microemulsion (HLB << 10)

• Middle-phase microemulsion (HLB ≈ 10)

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Microemulsion Microemulsion Phases Formed Phases Formed by by SurfactantSurfactant

O/W(Winsor type I) Winsor type III W/O(Winsor type II)

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Hydrophil > lipophil Hydrophil = lipophil Hydrophil < lipophil

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Removal Removal MechanismsMechanisms

� Mobilization

Desirable in aquifer contaminated by LNAPLs

� Micellar solubilization

Solubilize adsorbed DNAPLs

(i.e., asphaltenes)

Javanbakht, G.; Goual, L. Mobilization and Micellar

Solubilization of NAPL Contaminants in Aquifer Rocks.

Journal of Contaminant Hydrology 2016, 185–186, 61–73.

8

LNAPL (Mobilization)

DNAPL (Solubilization)

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Materials and MethodsMaterials and Methods

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RockRock

Fountain formation, a heterogeneous Pennsylvanian sedimentary rock consisting primarily of Conglomerate, Sandstone, or Arkose formed from the Sherman Granite.

Porosity: 12-15% Permeability: 2-5 mD

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NAPLNAPLNAPL is Milne point crude oil from Alaska

NAPL

ρ20C (g/mL) 0.9214

Reflective Index at 20°°°°C 1.5222

Viscosity (mPa.s) 112.0

C (%) 85.07

H (%) 7.75

11

H (%) 7.75

N (%) 1.09

O (%) 1.61

S (%) 4.63

H/C 1.1

Asphaltenes (wt%) 9.03

TAN (mg of KOH/g) 1.69

TBN (mg of KOH/g) 2.25

TBN/TAN 1.33

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SurfactantsSurfactants

• Alkyl polyglucosides : (n-Dodecyl β-D-Maltoside)nonionic, sugar based environmental friendly

• Alkyl phenyl ethoxylates : (Triton X-100) nonionic,

environmental friendly with a branched-alkyl chain tail

• Alkyl ethoxylates : (Bio-Soft N1-7) linear alcohol alcoxylates , nonionic, and environmental friendly

• Biosurfactants : (Saponin) nonionic, and

environmental friendly with complex structure

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Surfactants Surfactants (Cont’d)(Cont’d)

Name Structure Chemical formula MW

(gr/mol)HLB CMC

(wt%)

n-Dodecyl β-D-

Maltoside

C24H46O11 511 13.35 0.02

Bio-Soft N1-7 H3(CH2)10-

O(CH CH O) H647 12.9 0.01

O(CH2CH2O)7H

Triton X-100 C14H22O(C2H4O)10H 625 13.5 0.02

Saponin C45H73NO15 1650 36.3 0.01

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Experimental Setup and ProcedureProcedure

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Rock MineralogyRock Mineralogy

• Scanning electron microscopy (SEM) images and energy dispersive X-ray analysis spectroscopy element maps

• Transmission micro-CT scanner (3D high-resolution map of pore space)

15

Micro-CT scannerScanning electron microscopy

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Phase Phase BehaviorBehavior

Brine solution (0.2 wt% surfactant in brine) and NAPLs at a volume ratio of 1:1 were shaken for 1 hour with a speed of 300 strokes/minute and then rested for two days at 25 °C and atmospheric pressure

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High Resolution Transmission Electron Microscopy High Resolution Transmission Electron Microscopy ((HRTEM)HRTEM)

O/w microemulsions extracted from the rag layer between NAPL and diluted brine

17

Microemulsions

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Interfacial Interfacial TensionTension

Rising/captive bubble

Tensiometry for high IFTs

18

Experimental set up

Spinning drop tensiometry for low IFTs

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Contact AngleContact Angle

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Dynamic CA on clean quartz Dynamic CA on contaminated quartz

Static CA measurements during spontaneous imbibition

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Spontaneous Imbibition Spontaneous Imbibition

20

Vacuum pump and cell

(100% water saturation)

Arkose core sample(38 × 50.8 mm)

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Spontaneous Imbibition Spontaneous Imbibition (Cont’d(Cont’d))

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Amott imbibition cells Core flooding system

(50% NAPL saturation)

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Results and Discussions

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Rock Characterization Rock Characterization

Arkose minerals

• Feldspar and clay (78.5%)

• Quartz (14.2%)

• Calcite (7.0%)

• Muscovite (0.3%)

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Phase Behavior Phase Behavior

Surfactants formed Winsor type III microemulsion phase with NAPL

24

n-Dodecyl β-D-maltoside Bio-soft N1-7 Triton X-100 Saponin

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HRTEM ImagingHRTEM Imaging

n-Dodecyl β-D-maltoside N1-7 Triton X-100 Saponin

25

800 nm 200 nm800 nm400 nm

Aged Saponin

> 1 micron

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Interfacial Interfacial TensionTension

MEs promote mobilization by increasing the capillary number

NAPL/brine IFT : 22.5 mN/m

2.5

3

/m

)

Maltoside

Triton X-100L

N1-7

Saponin

26

0

0.5

1

1.5

2

Inte

rfa

cia

l T

en

sio

n (

mN

/m

)

Saponin

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Contact Angle Contact Angle (Cont’d)(Cont’d)

• Surfactant alters the wettability of contaminated rock surfaces from weakly-water wet back to water-wet

• The adsorption of surfactant molecules via their hydrophobic tails on the thin NAPL layer causes asphaltene molecules to detach and form Winsor Type I microemulsions

10

12

Brine Saponin Triton N1-7 Maltoside

6

8

10

12

uency

Saponin - First day

Saponin- 4th day

28

0

2

4

6

8

10

0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150 160 170 180

Frequency

CA (Degree)

0

2

4

6

80 90 100 110 120 130 140

Frequ

CA (Degree)

Brine

Saponin

Triton

N1-7

Maltoside

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Spontaneous Imbibition

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Solubilization vs. Solubilization vs. MobilizationMobilization

Effect of surfactant (maltoside)-in-brine on NAPL removal from Arkose core samples containing 50% water and 50% NAPL

20

25

NA

PL

Rem

ov

al (

vo

l %

)

Solubilization by surfactant (3 vol%)

Additional mobilization by surfactant (2 vol%)

Wettability alteration

31

0

5

10

15

0 20 40 60 80 100 120 140

NA

PL

Rem

ov

al (

vo

l %

)

Time (Hours)

Without surfactant With surfactant

Mobilization without surfactant (15vol%)

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Thin SThin Sections Analysisections Analysis

• The channels that contained dolomite cement were remained

contaminated after surfactant treatment

• Surface roughness plays an important role in wettability alteration

Without surfactant With n-dodecyl β-D-maltoside

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Conclusions Conclusions (Cont’d)(Cont’d)

� Surfactant self-assembly reduces the NAPL mobilization rate especially in low permeability rocks

� This work suggest that mixtures of surfactants with two structural types can promote both mobilization and micellar solubilization of NAPL in porous media. Type 1 contains a linear tail and a large hydrogen-bonding head, whereas type 2 has a highly branched tail and a smaller hydrogen-head, whereas type 2 has a highly branched tail and a smaller hydrogen-bonding head.

� References:

• “Mobilization and Micellar Solubilization of NAPL Contaminants in Aquifer Rocks”

Javanbakht, G.; Goual, L. Journal of Contaminant Hydrology 2016, 185–186, 61–73.

• “Impact of Surfactant Structure on NAPL Mobilization and Solubilization in Porous

Media.” Javanbakht, G.; Goual, L. Ind. Eng. Chem. Res. 2016.

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AcknowledgementsAcknowledgements

We gratefully acknowledge financial support of

� National Science Foundation (CAREER Award # 1351296 )

� HESS Corporation

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Thank youQuestions?Questions?

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Spontaneous ImbibitionSpontaneous Imbibition

40

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HRTEMHRTEM

Tecnai TF20 S-Twin High Resolution Transmission Electron Microscope (HRTEM) from FEI. The microscope features a TIETZ F415MP 4k × 4k multiport CCD camera with a 4-port readout and 15 µm pixel size. Two types of samples were prepared on silicon dioxide custom coated carbon TEM grids from SPI Supplies. The first sample contained surfactant micelles obtained by mixing 0.2 wt% of surfactant in brine. The second micelles obtained by mixing 0.2 wt% of surfactant in brine. The second sample consisted of o/w microemulsions prepared by extracting a small amount of the rag layer between NAPL and brine. Because the rag layer phase was too thick to image under microscope, it was diluted 40 times in the same brine. All samples were imaged by the microscope at 200 kV accelerating voltage under bright field illumination mode. Image J software was used for processing the images to measure the average size of the micelles and microemulsions particles.

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CACA� The thin brine film between NAPL and mineral surface

becomes unstable and collapses because of weak DLVO forces and more dominant electrostatic and van der Waals forces.Thecollapse of the brine film allows asphaltenes to adsorb onto the mineral surface and alter its wettability.

� The contact angles were smaller since NAPL 2 is less basic � The contact angles were smaller since NAPL 2 is less basic than NAPL 1, thus there is less electrostatic repulsion between Ca2+ ions of brine and dissociated basic groups of NAPL.

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CTCT-- scanner scanner To determine the abundance of each mineral, a rock sample was placed in a miniature Hassler type core holder made of carbon fiber and imaged at high resolution using a transmission micro-CT scanner (VersaXRM-500, Zeiss). The X-ray source was operated at a voltage of 60 kV and a power of 5 W. The 3D map of pore space was reconstructed based on 2000projections with an angular coverage from -104° to 104° and an angular step size of 0.104°. For each projection, 5 s step (exposure + motion) and3 s exposure (dwell)time each projection, 5 s step (exposure + motion) and3 s exposure (dwell)time were used. Each projection is a 2030 × 2030 pixel image with a resolution of 2.02 microns per pixel. Reconstruction of the projections with an appropriate center shift value gave the 3D high-resolution map of the pore space shown in. A binary voxel map of the pore space was then generated using Avizo Fire 8.0 visualization and analysis software. The non-local means filter was applied to smoothen the raw data and reduce noises. The intensity ranges for different minerals were determined by applying the interactive thresholding tool of Avizo software. The Edit new label field tool was used to assign each intensity range to each mineral.

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BrineBrine

1 M CaCl2

Cation Concentration (ppm)

Al+3

B+3

Ca+

Cu+2

Fe+2

0.1163.03120.430.0220.078

46

Fe+2

K+1

Mg+2

Mn+2

Na+1

0.0782.8680.4450.0073.609

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CMCCMC

� Effect of surfactant concentration on surface tension

� CMC point of surfactant (low CMC)

60

70

80

Su

rfac

e T

ensi

on

(m

N/m

)

47

0

10

20

30

40

50

60

0 0.05 0.1 0.15 0.2 0.25

Su

rfac

e T

ensi

on

(m

N/m

)

Surfactant Concentration (wt%)


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