Introduction

Oil production from existing oilfields is dropping due to reservoir depletion. Different secondary and tertiary oil recovery methods are used to improve oil production. As an effective technique, chemical enhanced oil recovery (CEOR) methods are used indifferent projects worldwide. CEOR includes injecting various chemicals such as polymer, surfactant, and alkaline1,2,3,4,5,6. These chemicals are used for increasing the oil recovery by changing the effective parameters of capillary forces such as interfacial tension and wettability. Two main challenges in the CEOR approach are the cost of chemicals and high chemical loss in the porous media due to adsorption and trapping7,8. So, novel, efficient, and cheaper CEOR methods are being developed through the application of nanotechnology. Because of their small size and high surface-to-volume ratio, nanofluids are being researched as novel CEOR agents9,10,11. Kumar et al.11 used SiO2-HPAM for IFT reduction, and wettability alteration. CaCl2 (1000 mg/L), and NaCl (30,000 mg/L) at 80 °C and 25 °C were used, and it was found that reduction of interfacial tension, and contact angle were higher in the presence of SiO2-HPAM in compared to SiO2, and presented material was suggested for CEOR10. Lashari et al.12 used HPAM/GO-SiO2 for wettability alteration. At 0.05 wt. % of nanocomposites, the percentage of incremental oil recovery was raised to 30.82%11.

The injection of nanofluids alters the sweep efficiency in reservoirs by mechanisms such as wettability alteration and interfacial tension reduction13. The high surface energy of the nano-structures provides exceptional electrical, rheological, thermal, and interfacial performance14,15. ZnO/SiO2/Xanthan was employed by Ahmadi et al.15 to reduce wettability and interfacial at varying salinities. The findings showed that at 2 SW (sea water) and 10 SW, the contact angle fell from (79°, 75°) to (78°, 74°) and (70°, 62°), respectively. Therefore, due to their high surface area and small size, nanoparticles can easily pass through porous media and pore throats16. Different types of nanoparticles have been used to improve oil recovery, such as silica17, ZnO18, silica/graphene19, carbon20,21, kaolinite22, and metal oxide23 through different mechanisms such as viscosity, IFT, and contact angle reduction. Taborda et al.17 used Silica nanoparticles, and it was found that viscosity reduced from 12 to 45%. ZnO with two distinct diameters, 55.7 and 117.1 nm, was employed by Adil et al.18 for EOR on sand packs ranging in size from 265 to 300 mD at 95 °C and 0.1 weight percent concentration. In the presence of ZnO, a tertiary recovery of 9–10.4% was noted. Additionally, silica/grapheme was utilized by Afzalitabar et al.19 for IFT and contact angle reduction. Their findings showed that the IFT dropped from 53.90 to 29.82 mN/m and the contact angle decreased from 143.47° to 58.50°.

Multiple mechanisms are at play during the flooding of nanoparticles to enhance oil detachment. For instance, the presence of nanoparticles causes a layer to form between the oil and water during flooding via a porous media, which lowers the interfacial tension9,12. In certain circumstances, variations in viscosity, wettability, and disjoining pressure are also believed to be helpful mechanisms.

Small ZnO nanoparticles, ranging in size from 10 to 100 nm, have been utilized in CEOR and documented in multiple publications. ZnO/SiO2 nanocomposites were employed for EOR in the Kurdistan area of Iraq by Ali et al. in 2019. IFT dropped from 31.8 to 2.016 mN/m, and RF increased from 46.96 to 66.24% at 2000 ppm of nanocomposites. Additionally, the presence of nanocomposites caused the relative permeability intersection to move to the right and the rock's wettability to transition from oil to water24. The industry finds zinc oxide nanoparticles appealing due to their low toxicity and biocompatibility25,26. ZnO nanoparticles have impact on wettability and IFT in the interactions between oil, brine, and rock. In the presence of ZnO, various trends in IFT change have been noted. Soleimani et al.27 found that ZnO nanofluid flooding increased IFT, but Zaid et al.28 revealed that IFT decreased when in contact with ZnO nanoparticles. Rezk et al.29 also confirmed that the primary causes of an observed 8% incremental oil recovery by ZnO nanofluid flooding are IFT reduction and wettability alteration. ZnO nanoparticles at the oil/brine interface have been shown by Ogolo et al.30 to boost oil recovery to 50%. When Adil et al.31 looked at how the ZnO concentration affected the recovery factor, they found that the best conditions were at 0.1% and 55.7 nm nanoparticle size, which led to a 10.2% increase in recovery. High ZnO adsorption on calcite sheets was reported by Soleimani et al.32, leading to changes in wettability and an 11.8% increase in oil recovery with flooding of 0.3 weight percent ZnO nanofluid.

Researchers have recently devised a novel method termed "nanocomposites-assisted CEOR applications" to boost the effectiveness of nanoparticles like ZnO. The concept underlying nanocomposites involved combining various solid materials to enhance their functionality at the nanoscale over stand-alone applications. Using nanocomposites resulted in efficient mechanisms such as wettability modification, capillary pressure decrease, and the creation of more stable nanofluids. Recently, our team synthesized different nanoparticles for CEOR applications at reservoir conditions. It was found that nanoparticles that contain ZnO in combination with other nanoparticles such as SiO2, zirconia, nickel, and alumina are effective in reducing the capillary pressure in porous media and controlling the asphaltene adsorption on rock surfaces33,34. Jafarbeigi et al.33 showed that a combination of ZnO-alumina nanoparticles has an effective influence on increased oil recovery, wettability modification, and IFT reduction. At 300 ppm, IFT and CA decreased from (27.24 mN/m, 161°) to (11.00 mN/m, 31°). Ahmadi et al.34 used alumina-ZnO-urea nanocomposites for improving SWAG tests as a new EOR method at reservoir conditions. It was observed that, at the SWAG ratio of 1:1, and 40 °C, oil recovery was increased from 55.9 to 83.1% through the injection of 80 ppm nanofluid. Ahmadi et al.35 also showed that cerium nanoparticles (cerium-zeolite-zirconia) increased the recovery factor from 42.5 to 72% during nanocomposites-assisted WAG tests due to their high total surface area (331.67 m2/g). Recently, Mehrooz et al.36 used different concentrations of cerium oxide nanoparticles and observed that with 0.01, 0.1, 0.25 and 0.5 wt.% nanofluid, the oil recovery increased to 25%, 38%, 43% and 45%, respectively.

In this study, ZnO nanoparticles were modified with cerium to improve the performance of the nanofluid in changing the interface properties. Different characterization tests such as XRD, BET, EDX, SEM, TEM, DLS, and FT-IR were used to optimize the nanocomposites concentration (OPC) by using Zeta potential and CA testing in reservoir settings which were not considered yet based on our knowledge. After selecting an OPC, the oil displacements were investigated between ZnO-Ce and ZnO. All experiments were obtained at reservoir conditions.

Materials and methodology

Material

A sandstone reservoir in Iran provided the crude oil and core. The density, API, and crude oil viscosity at a reservoir pressure of 1800 Psi and temperature of 60 °C are 0.846 cm/g, 28, and 9.9 cP, respectively. Core porosity, core permeability, and GOR were found to be 22.5%, 27.45 mD, 240 scf/STB, and 232, in that order. Figure 1 displays the SARA (saturate-aromatic-resin-asphaltene) test findings.

Figure 1
figure 1

Compositional specifications of the oil.

Na2CO3 (99.9%), Ce (NO3)3.6H2O (98.5%), and Zn (NO3)2.6H2O (99%) were obtained from Merck company. All the purchased materials were used at a high level of qualifications.

Methodology

Preparation of ZnO-Ce nanocomposites

The ZnO-Ce nanocomposites (95%Zn / 5%Ce) were prepared using the co-precipitation technique. 75 mL of Na2CO3 was added once 14.9 g of Zn (NO3) 2.6H2O and 1.2 g of Ce (NO3)3.6H2O had been dissolved in 100 mL of DW (distilled water). The solution was mixed at 70 °C for 2 h, filtered, washed, and dried at 80 °C for 12 h. A calcination process was conducted as the final step at 400 °C for 2 h to produce the nanocomposites.

Fluid properties measurements

Since both the ZnO-cerium and ZnO nanoparticles were in powder form, 50,000 ppm formation brine and DW were used for preparing the nanofluids. Different concentrations including 25, 50, 75, 100, 125, and 150 ppm were designed to study the effect of the concentration on the nanofluid properties. In each concentration, the prepared fluid was stirred for 20 min. The zeta potential was measured using the Malvern Zetasizer Nano ZS ZEN3600 to confirm the nanofluid. The HPHT Vinci setup, as seen in Fig. 2, was used to measure the interfacial tension, and contact angle. For flooding with oil and water/nanofluid, there are two distinct pumps. Before closing the main cell, the trapped air was evacuated and the cell was filled with water (or nanofluid). The reservoir's temperature was kept at 60 °C and its pressure at 1800 Psi with the help of a heating jacket and water pump. A camera was used to take a picture of the oil droplet inside the water/nanofluid after it was released from the needle in Fig. 2 into the main cell. The data collected was then analyzed to determine the IFT. A sandstone sheet was put up to measure the contact angle. The same method and conditions were used to measure the contact angle of an oil droplet on the rock in the presence of water or nanofluid at 1800 Psi and 60 °C. ZnO and ZnO-cerium nanocomposites were present during IFT and CA experiments at 25, 50, 75, 100, 125, and 150 ppm at 1800 Psi and 60 °C. In this study, all experiments were conducted three times, and average values were given.

Figure 2
figure 2

HPHT contact angle and interfacial tension set-up.

Coreflooding experiment

Figure 3 shows a schematics of Vinci core flooding apparatus for injecting nanocomposites into the sandstone core samples at 1800 Psi and 60 °C. Brine, crude oil, and nanofluid (ZnO-Ce or ZnO) were accumulated at three different transfer vessels. An oven was used for setting a uniform and constant temperature of 60 °C. Other main parts of the set-up were a sample collector at outlet for obtaining samples volume and calculating RF, overburden pump for removing air between rubber sleeve and sandstone core, core holder, and different pressure and differential pressure (DP) gauges. The sandstone core was vacuumed and saturated with crude oil, then aged at 1800 Psi and 60 °C for three weeks. The aged core was put in a core holder at 2000psi overburden pressure. 50,000 ppm brine was used for making nanofluid at optimum concentration of 100 ppm, and it was injected during water flooding for obtaining both nanocomposites effects on EOR at same reservoir conditions, 2000 Psi and 60 °C. Ultimate oil recovery, DP, and cumulative water volume were measured and reported.

Figure 3
figure 3

The core flooding set-up for the nanocomposites flooding process.

Results and discussion

Chemical composition, surface morphology, and nanocomposites' characteristics

Figure 4 shows the XRD pattern of the prepared zinc oxide-cerium nanoparticle. A peak at 2θ = 29.2° shows the presence of zinc oxide-cerium (111 crystal facet) as a new phase37, and the following values are in conformity with the standard pattern of hexagonal wurtzite ZnO with JCPDS No. 36–1451: 30.15°, 33.95°, 37.16°, 47.21°, 56.92°, 63.21°, 67.1°, 68.13°, 69.12°, and 77.28°. Because Ce3+ has a wider ionic radius than Zn2+, most of the Ce ions are unable to be integrated into the ZnO lattice and are instead distributed as Ce2O3 and CeO2 on the ZnO surface38. Figure 5 compares the FTIR of zinc oxide-cerium nanocomposites to that of pure zinc oxide. Zn–O vibration is seen at wavelengths of 549 cm−1 and 553 cm−139. The O–H group was also found in the 3180–3690 cm−1 range. Organic pollutants such as C‒O‒C, C=O, and C‒H were discovered at the 1000‒1100, 1300‒1650, and 2900‒3000 cm−1 bands, respectively, which is similar to what Rajbongshi et al.40 found. According to He et al.38, Zn–O and Ce–O correspond with one another, but Ce and N did not exhibit any peaks because of the little amount of dopants.

Figure 4
figure 4

ZnO-cerium nanocomposite and ZnO XRD.

Figure 5
figure 5

ZnO-cerium nanocomposites FTIR.

Figures 6 and 7 show the nanocomposites SEM and EDX results, respectively. Based on the SEM tests, the nanocomposites are sphere-like, with a particle size of 20‒50 nm. The spectrum of EDX tests shows the presence of cerium, oxygen, and Zn. The Ce:Zn weight ratio was measured as 3.95:37.18.

Figure 6
figure 6

ZnO-cerium nanocomposites SEM nanocomposites at two different magnification (5kX and 60 kX).

Figure 7
figure 7

ZnO-cerium nanocomposites EDX.

The ZnO-cerium nanocomposites' TEM data are displayed in Fig. 8a. The size was less than 50 nm and the shape was semi-spherical, consistent with the SEM data. The hydrodynamic size of the Zn-Ce oxide NPs was then evaluated by dynamic light scattering (DLS) measurements, where a distribution from 25 to 50 nm was observed (Fig. 8b). This value is entirely consistent with the results obtained from it the TEM analysis.

Figure 8
figure 8

(a) TEM image and (b) DLS of Zn-Ce oxide NPs.

The N2 adsorption–desorption isotherms of ZnO and ZnO-Ce samples using the Brunauer–Emmett–Teller (BET) method are shown in Fig. 9. The BET surface area, mean pore diameter, and pore volume are displayed in Table 1. The ZnO and ZnO-Ce samples have specific surface areas of 46.16 and 48.05 m2/g, respectively. The ZnO-Ce nanocomposites' pore volume rose when cerium was added to the ZnO. Following the addition of Ce to ZnO, the calcination process led to a gas release that increased the specific surface area. The effectiveness of ZnO-Ce as an EOR agent is impacted by this characteristic.

Figure 9
figure 9

N2 adsorption–desorption by ZnO and ZnO-Ce samples.

Table 1 Properties of ZnO and ZnO-Ce nanocomposites' textures.

Nanofluid specifications

The IFT, pH, density, viscosity, zeta potential (Z-P), and viscosity of nanofluid at different concentrations were measured as shown in Table 2.

Table 2 Nanofluid properties at different ZnO-cerium nanocomposites concentrations.

Figure 10 demonstrates the amount of wettability and zeta potential at different nanofluid concentrations. The absolute quantity of zeta potential tests showed a balanced between the electrostatic repulsive and attractive forces41,42,43. Hence, the zeta potential of ˃ ± 30 mV shows high repulsive forces between nanoparticles and a stable nanofluid. The most negative zeta potential value was observed at 100 ppm, which was -44.36 mV. The maximum reduction in CA and a shift to a more water-wet state were also observed at the same concentration. Hence, 100 ppm was selected as the most compelling case for the oil displacement test. Based on the findings presented in Table 2, the optimum concentration of ZnO was observed at 100 ppm with consideration of the CA and zeta potential tests, and this was selected as a base case to be compared to our new approach.

Figure 10
figure 10

Selecting an optimum nanocomposites concentration according to CA and stability tests.

Displacement tests

Figure 11 showsthe recovery factor achieved by injecting the nanocomposites at OPC. ZnO-cerium nanocomposites had higher recovery than the base case (pure ZnO), and the RF% increased from 37.11% to 71.40% at 60 °C and 1800 Psi. The main reason can be found in Table 2. According to the results, the nanocomposites were more stable and effective in altering the IFT and wettability at all concentrations. For example, at OPC, [IFT (mN/m), CA (°), Z-P (mV)] are (22.51, 40.83, − 44.36) and (30.50, 50.21, − 31.05) for nanocomposites and ZnO nanoparticles, respectively.

Figure 11
figure 11

Comparison of RF in the presence of N-composites and ZnO nanoparticles.

Figure 12 shows the cumulative water production of nanocomposites at 100 ppm, 1800 Psi, and 60 °C. Based on the graph, the water breakthrough was delayed by the modified nanocomposites flooding. This delay shows the change in macroscopic sweep efficiency and a more invasion to the smaller pores. Hence, the application of ZnO-Ce nanofluid results in more uniform flow compared to ZnO nanofluid.

Figure 12
figure 12

Comparing the total amount of water produced when ZnO nanoparticles and N-composites are present.

Wettability alteration, and zeta potential were two main factors for getting higher tertiary oil recovery when nanocomposites are present. As said at OPC = 100 ppm, contact angle for ZnO-Cewas lower compared to pure ZnO, and ZnO-Ce was more stable in compared to ZnO. Figure 13a, b were shown effects of wettability alteration in adsorption of oil in nanocomposites surface, separation of nanocomposites, and adsorbing on the surface of the rock, and switching, correspondingly, from oil-to-water-wettability. Another main mechanisms for obtaining higher efficiency of ZnO-Ce was obtaining higher IFT reduction in compared to pure ZnO. Finally, lower absolute permeability reduction were observed in the presence of ZnO-Ce (9.2%) in compared to pure ZnO (19.2%). Since all conditions were same, higher incremental oil recovery was logical due to above two mechanisms.

Figure 13
figure 13

Main nanocomposites mechanisms a) adsorption of oil in nanocomposites surface, b) adsorbing nanocomposites on the surface of the rock.

Conclusion

This study examined the characteristics of ZnO-Cerium nanocomposites with ZnO nanoparticles using XRD, BET, EDX, SEM, TEM, DLS, and FT-IR. The addition of cerium to the Zinc oxide increased the pore volume of the Zinc-Cerium nanocomposites. The calcination procedure that followed adding Ce to ZnO increased the specific surface area by causing a gas release. The IFT, CA, and Z-P experiments were used to determine the ideal concentration of nanocomposites to have the most impact on the interactions between rock, oil, and brine. At 100 ppm, the most stable nanofluid was developed which altered the wettability and viscosity the most. Moreover, same static tests were performed for ZnO nanoparticles, and based on the results, ZnO-Cerium IFT and CA reduction are better impacted by nanocomposites, and better stability compared to ZnO nanoparticles. Based on the core flooding tests at 1800 Psi, 60 °C, and OPC = 100 ppm. The recovery factor improved to 71.40% from 37.11%. Due to adding cerium in nanocomposites. Moreover, the water breakthrough was delayed by the modified nanocomposites flooding in compared to ZnO nanoparticles.