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. 2018 May 23;19:475–480. doi: 10.1016/j.dib.2018.05.046

Dataset on experimental investigation of gum arabic coated alumina nanoparticles for enhanced recovery of nigerian medium crude oil

Oyinkepreye D Orodu 1, Kale B Orodu 1, Richard O Afolabi 1,, Eboh A Dafe 1
PMCID: PMC5997916  PMID: 29900344

Abstract

The dataset in this article are related to an experimental Enhanced Oil Recovery (EOR) scheme involving the use of dispersions containing Gum Arabic coated Alumina Nanoparticles (GCNPs) for Nigerian medium crude oil. The result contained in the dataset showed a 7.18% (5 wt% GCNPs), 7.81% (5 wt% GCNPs), and 5.61% (3 wt% GCNPs) improvement in the recovery oil beyond the water flooding stage for core samples A, B, and C respectively. Also, the improvement in recovery of the medium crude oil by the GCNPs dispersions when compared to Gum Arabic polymer flooding was evident in the dataset.

Keywords: Oil recovery, Waterflooding, Gum arabic, Nanoparticles, Nigerian medium crude oil


Specifications Table

Subject area Petroleum Engineering
More specific subject area Enhanced Oil Recovery/Tertiary Oil Recovery
Type of Data Tables and Figures
How Data was Acquired Core Flooding Experiment using the OFITE®Reservoir Permeability Tester
Data Format Raw Data
Experimental Factors
  • 1.

    GCNP preparation using Al2O3 nanoparticles and Gum Arabic

  • 2.

    Core plugs were cleaned with acetone using the Soxhlet apparatus

  • 3.

    Saturation of the plugs were done using Vinci Technologies® High Pressure Core Saturator

  • 4.

    Core flooding of the plugs using OFITE® Reservoir Permeability Tester at different flow rates for waterflood and GCNP

Experimental Features Improvement in recovery of the medium crude oil by the GCNPs dispersions when compared to water or Gum Arabic polymer flooding
Data Source Location Department of Petroleum Engineering, Covenant University, Nigeria
Data Accessibility Data is with the article

Value of data

  • Core flooding results show the relevance of polymer coated nanoparticles for the recovery of crude oil from conventional reservoirs.

  • The GCNPs provided improved recovery of oil beyond the capacity of water flooding and polymer flooding.

  • Incremental oil recovery over that of waterflooding was encouraging despite permeability impairment by about half the initial measured value.

  • The results obtained calls for a detailed study on the mechanisms at play with respect to the polymeric and surfactant property of Gum Arabic. Likewise, the performance of Gum Arabic should be evaluated and compared to that of known and standard polymers used in the industry.

1. Data

Nanoparticles are reported in [1], [2], [3] to improve oil recovery but its instability paved the way for stable polymer coated nanoparticles [4]. The dataset presented in this paper provides an experimental investigation of Gum Arabic coated Alumina Nanoparticles (GCNPs) for enhanced recovery of Nigerian medium crude oils. Gum Arabic is a naturally occurring polymer that is abundant in Nigeria and Sudan. Table 1 shows the properties of the various cores, inclusive of the impact of GCNPs flooding on permeability causing impairment of the cores. Table 2 shows the results for the determination of connate water saturation in the cores after the oil injection process. Table 3 gives values for the residual oil saturation and recovery factors after water flooding. Table 4 gives the additional oil recovery obtained using GCNPs and the irreducible oil saturation. Whereas Fig. 1 displays graphically, the impact of the incremental oil recovered by GCNPs after the optimal recovery by the waterflooding process. The dataset for Fig. 1 is presented in Table 5.

Table 1.

Rock properties of the Berea cores. The effect of the GCNPs on the absolute permeability are captured in the last two columns.

Core samples Length Diameter Bulk volume Wet weight Dry weight Pore volume Porosity Absolute K (Pre flooding) Absolute K (Post flooding)
(cm) (cm) (ml) (g) (g) (ml) (%) (mD) (mD)
Core A 6.30 3.7 67.77 165.3 151.2 12.48 18.41% 262.3 125.8
Core B 6.25 3.7 67.23 165.1 151.0 12.48 18.56% 278.8 115.4
Core C 6.30 3.7 67.77 164.7 151.0 12.12 17.89% 251.7 173.2
Core D 6.25 3.7 67.23 165.2 151.9 11.77 17.51% 245.0 223.7

Table 2.

Determination of connate water saturation from oil injection process.

Core Total pore volume of the core (ml) Volume of water expelled from core (ml) Total oil in place (ml) Connate volume of water (ml) Soi Swc
A 12.48 9.75 9.75 2.73 0.78 0.22
B 12.48 9.60 9.60 2.88 0.77 0.23
C 12.12 9.80 9.80 2.32 0.81 0.19
D 11.77 9.50 9.50 2.27 0.81 0.19

Table 3.

Residual oil saturation and recovery factor after water flooding process.

Cores Total recovered oil volume Residual oil volume Sw Sor Recovery factor
mL mL %
A 4.50 5.25 0.58 0.42 46.15%
B 4.55 5.05 0.60 0.40 47.40%
C 4.70 5.10 0.58 0.42 47.96%
D 5.50 4.00 0.66 0.34 57.89%

Table 4.

Additional oil recovery using GCNPs and the irreducible oil saturation.

Cores Total recovered oil volume Residual oil volume Soirr Additional recovery Recovery factor
mL mL % %
A 5.20 4.55 0.36 7.18% 53.33%
B 5.30 4.30 0.34 7.81% 55.21%
C 5.25 4.55 0.38 5.61% 53.57%
D 5.75 3.75 0.32 2.63% 60.53%

Fig. 1.

Fig. 1

Effect of GCNPs on the EOR process after water flooding for cores A, B, C and D.

Table 5.

Oil recovery of GCNPs assisted waterflooding for cores A, B, C and D.

Core A (GCNPs 5 wt%)
Core B (GCNPs 5 wt%)
Core C (GCNPs 3 wt%)
Core D(GCNPs 3 wt%)
Flooding Rate Pore Volume Injected Oil Recovery Flooding Rate Pore Volume Injected Oil Recovery Flooding Rate Pore Volume Injected Oil Recovery Flooding Rate Pore Volume Injected Oil Recovery
(cc/min) (-) (-) (cc/min) (-) (-) (cc/min) (-) (-) (cc/min) (-) (-)
H2O 3cc/min 0 0 H2O 3cc/min 0 0 H2O 3cc/min 0 0 H2O 3cc/min 0 0
H2O 3cc/min 1.201923 0.066667 H2O 3cc/min 1.201923 0.057292 H2O 3cc/min 1.237624 0.061224 H2O 3cc/min 1.274427 0.036842
H2O 3cc/min 2.403846 0.148718 H2O 3cc/min 2.403846 0.161458 H2O 3cc/min 2.475248 0.137755 H2O 3cc/min 2.548853 0.078947
H2O 3cc/min 3.605769 0.164103 H2O 3cc/min 3.605769 0.192708 H2O 3cc/min 3.712871 0.204082 H2O 3cc/min 3.82328 0.152632
H2O 3cc/min 4.807692 0.215385 H2O 3cc/min 4.807692 0.223958 H2O 3cc/min 4.950495 0.25 H2O 3cc/min 5.097706 0.194737
H2O 3cc/min 6.009615 0.261538 H2O 3cc/min 6.009615 0.260417 H2O 3cc/min 6.188119 0.280612 H2O 3cc/min 6.372133 0.242105
H2O 3cc/min 7.211538 0.297436 H2O 3cc/min 7.211538 0.317708 H2O 3cc/min 7.425743 0.326531 H2O 3cc/min 7.646559 0.294737
H2O 3cc/min 8.413462 0.34359 H2O 3cc/min 8.413462 0.338542 H2O 3cc/min 8.663366 0.372449 H2O 3cc/min 8.920986 0.347368
H2O 3cc/min 9.615385 0.4 H2O 3cc/min 9.615385 0.385417 H2O 3cc/min 9.90099 0.418367 H2O 3cc/min 10.19541 0.405263
H2O 3cc/min 10.81731 0.441026 H2O 3cc/min 10.81731 0.427083 H2O 3cc/min 11.13861 0.464286 H2O 3cc/min 11.46984 0.473684
H2O 3cc/min 12.01923 0.45641 H2O 3cc/min 12.01923 0.463542 H2O 3cc/min 12.37624 0.479592 H2O 3cc/min 12.74427 0.515789
H2O 3cc/min 13.22115 0.461538 H2O 3cc/min 13.22115 0.473958 H2O 3cc/min 13.61386 0.489796 H2O 3cc/min 14.01869 0.552632
H2O 3cc/min 14.42308 0.461538 H2O 3cc/min 14.42308 0.479167 H2O 3cc/min 14.85149 0.494898 H2O 3cc/min 15.29312 0.563158
GCNP 0.5cc/min 14.6234 0.466667 H2O 3cc/min 15.625 0.479167 H2O 3cc/min 16.08911 0.494898 H2O 3cc/min 16.56754 0.573684
GCNP 0.5cc/min 14.82372 0.476923 GCNP 0.5cc/min 15.82532 0.489583 GCNP 0.5cc/min 16.29538 0.5 H2O 3cc/min 17.84197 0.578947
GCNP 0.5cc/min 15.02404 0.482051 GCNP 0.5cc/min 16.02564 0.494792 GCNP 0.5cc/min 16.50165 0.510204 H2O 3cc/min 19.1164 0.578947
GCNP 0.5cc/min 15.22436 0.487179 GCNP 0.5cc/min 16.22596 0.505208 GCNP 0.5cc/min 16.70792 0.520408 GCNP 0.5cc/min 19.3288 0.589474
GCNP 0.5cc/min 15.42468 0.487179 GCNP 0.5cc/min 16.42628 0.505208 GCNP 0.5cc/min 16.91419 0.520408 GCNP 0.5cc/min 19.54121 0.594737
GCNP 0.5cc/min 15.625 0.497436 GCNP 0.5cc/min 16.6266 0.510417 GCNP 0.5cc/min 17.12046 0.52551 GCNP 0.5cc/min 19.75361 0.6
GCNP 0.5cc/min 15.82532 0.5078 GCNP 0.5cc/min 16.82692 0.510417 GCNP 0.5cc/min 17.32673 0.52551 GCNP 0.5cc/min 19.96602 0.6
GCNP 0.5cc/min 16.02564 0.512821 GCNP 0.5cc/min 17.02724 0.520833 GCNP 0.5cc/min 17.533 0.530612 GCNP 0.5cc/min 20.17842 0.605263
GCNP 0.5cc/min 16.22596 0.528205 GCNP 0.5cc/min 17.22756 0.53125 GCNP 0.5cc/min 17.73927 0.530612 GCNP 0.5cc/min 20.39082 0.605263
GCNP 0.5cc/min 16.42628 0.528205 GCNP 0.5cc/min 17.42788 0.53125 GCNP 0.5cc/min 17.94554 0.535714 GCNP 0.5cc/min 20.60323 0.605263
GCNP 0.5cc/min 16.6266 0.533333 GCNP 0.5cc/min 17.62821 0.541667 GCNP 0.5cc/min 18.15182 0.535714 GCNP 0.5cc/min 20.81563 0.605263
GCNP 0.5cc/min 16.82692 0.533333 GCNP 0.5cc/min 17.82853 0.546875 GCNP 0.5cc/min 18.35809 0.535714
GCNP 0.5cc/min 17.02724 0.533333 GCNP 0.5cc/min 18.02885 0.546875 GCNP 0.5cc/min 18.56436 0.535714
GCNP 0.5cc/min 17.22756 0.533333 GCNP 0.5cc/min 18.22917 0.552083
GCNP 0.5cc/min 17.42788 GCNP 0.5cc/min 18.42949 0.552083
GCNP 0.5cc/min 18.62981 0.552083

2. Experimental design, materials and methods

2.1. Core cleaning

The Berea sandstone cores (labelled A, B, C and D, all purchased from Cleveland Quarries Inc.) were immersed in acetone vapors (at 110 °C), as acetone (analytical grade) is boiled slowly in a Pyrex flask with its vapor moving upwards in a Soxhlet apparatus. Water contained in the thimble housing the core sample in the thimble is vaporized. Re-condensed acetone together with liquid water falls from the base of the condenser onto the core sample in the thimble; the acetone soaks the core sample and dissolves any oil with which it comes into contact. When the liquid level within the Soxhlet tube reaches the top of the siphon tube arrangement, the liquids within the Soxhlet tube are automatically emptied by a siphon effect and flow into the boiling flask. The acetone is then ready to start another. Afterwards, a desiccator was employed in drying the core samples.

2.2. Preparation of brine

The brine was prepared to about 3.0 wt.% (0.03 g/ml). 30 g of NaCl salt (analytical grade) was measured with the use of the weighing balance and diluted in 750 ml of water. The salt was poured into the cylinder and stirred properly so as to dissolve evenly. Then water was poured into the measuring cylinder filling it up to 1000 ml.

2.3. Preparation of gum arabic coated nanoparticles (GCNPs)

The nanoparticle in use was Al2O3 (30–60 nm, purity greater than 99%; manufactured by Sigma Aldrich and purchased from Equilab Solutions in Nigeria.). 50 g of Al2O3 was dispersed in 1 l of deionized water to make nano-fluid suspensions, making a 5 wt.% mixture. It was further diluted to 3 wt% in order to completely carry out further experiments. The Gum Arabic (a polymer; purchased locally in Nigeria) was mixed with the prepared nanofluids at a concentration of 10 wt.%.

2.4. Determination of porosity and absolute permeability

The dimensions of the cleaned dry cores (length, diameter and weight) were taken before being saturated with brine using the Vinci Technologies® High Pressure Core Saturator. The pore volume for each core was calculated as;

Length of core = Lc Diameter of core = Dc (radius = rc)
Bulk volume of core = VT = πrc2Lc Weight of dry core = WD
Weight of core saturated with brine = Ws Density of brine = ρb = 1.13 g/cm3
Pore volume = Vp = WsWDρb Porosity = =VpVT

The permeability of the cores was determined using the reservoir permeability tester.

2.5. Core flooding

The cores were saturated with 100% brine and the flooding experiments started with a primary drainage process. Oil was injected into the core plugs at 5 cc/min until brine was no longer produced. This procedure established the initial/connate water saturation, ‘Swc’. The next stage was the water flooding; water was injected into the core plugs at 3 cc/min until oil was no longer produced for secondary recovery. This established the residual oil saturation, ‘Sor’. GCNPs and polymers were initiated as an enhanced oil recovery (EOR) process. To investigate if they had any effect on the oil recovery, “they were injected into the core plug after the water flooding”. The extra oil produced during the EOR process increased the recovery factor and hence proved that GCNPs potentially can work as an EOR agent (Fig. 1). As there was no automated way to measure the recovery, the experiment had to be monitored during the whole flooding sequence. Samples of the effluent fluids were manually taken every (five) 5 min at the outlet of the core holder in test tubes. The samples were used to measure the amount of oil and brine produced and used for calculating saturations as well as recovery factor.

Acknowledgement

The authors would like to thank the management of Covenant University for providing the needed facilities to carry out this research.

Footnotes

Transparency document

Transparency data associated with this article can be found in the online version at 10.1016/j.dib.2018.05.046.

Transparency document. Supporting information

Supporting information

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References

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Associated Data

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Supplementary Materials

Supporting information

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