Keywords

A lot of research and practice at home and abroad show that CO2 flooding can effectively improve reservoir development effect and enhance oil recovery [1,2,3]. The reservoir of ultra-low permeability reservoir has dense core and poor physical properties. Therefore, the CO2 flooding test needs to study the effect of CO2 flooding first. The purpose of this research is to clarify the CO2 flooding effect of ultra-low permeability sandstone through the experiment of real sandstone CO2 micro-flooding, and to provide guidance for mine testing.

1 Experimental Overview

1.1 Experimental Device

According to the specific content of this study, we have designed a real sandstone CO2 micro-displacement experimental device (atmospheric pressure) (Fig. 1) ,and real sandstone CO2 micro-displacement experimental device (high pressure) (Fig. 2).

Fig. 1.
figure 1

Real sandstone CO2 micro-displacement experimental device diagram (atmospheric pressure)

Fig. 2.
figure 2

Real sandstone CO2 micro-displacement experimental device diagram (high pressure)

1.2 Experimental Condition

The formation pressure of the reservoir where the core is located is 15.8 MPa, comprehensive water cut is 35.0%, reservoir porosity is 8.3% and permeability is 0.27 mD. It is a typical ultra-low porosity with ultra-low permeability reservoir. The water type of formation water is CaCl2, the total salinity is 35.42 g/L, the viscosity of formation crude oil is 0.73 mPa·s, the original gas-oil ratio is 85 m3/t, the reservoir temperature is 84 °C, the MMP (minimum miscible pressure) of formation crude oil is 16.1 MPa, and the MMP of surface crude oil is 19.3 MPa.

This experiment is matched with simulated formation water. The water type is CaCl2 and the total salinity is 35.0 g/L. The oil used is degassed crude oil (high pressure condition) on the reservoir surface and simulated crude oil (atmospheric pressure condition) prepared by the laboratory. The highest temperature and displacement pressure of the experiment are 70 °C and 17.9 MPa, which fully ensure that the experimental conditions are close to the real state.

1.3 Experimental Steps

Model Preparation.

The core is extracted, dried, sliced and wear down, make a real sandstone micro-model.

Evacuation and Saturated the Core for Water.

This process is to simulate the state of reservoir without oil and gas entering.

Saturated the Core for Oil.

This process simulates the process of oil and gas entering reservoir.

Water Flooding (or CO2 Flooding).

The real sandstone model of saturated oil directly to CO2 flooding (or direct water flooding), increasing pressure, the occurrence status and percolation characteristics of CO2 (or water) in the displacement process were observed. For experiments requiring alternating displacement, repeat this step.

Pressure Relief.

After maintaining the maximum displacement pressure for a certain period of time, gradually reduce the displacement pressure, continue to observe and analyze the seepage path of CO2, and use image processing software to statistics the final displacement efficiency.

The detailed experimental procedure of real sandstone CO2 flooding micro-experiment is shown in Fig. 3 [4].

Fig. 3.
figure 3

Microscopic experimental steps of CO2 flooding in real sandstone. Note: CO2 flooding includes miscible flooding and immiscible flooding.

2 Experimental Results

2.1 Single Displacement Experiment

Water flooding, CO2 immiscible flooding and CO2 miscible flooding are carried out, and the sandstone used is taken from the same core. The local horizon map of water flooding experiment shows that, the direction of water flooding line is not uniform, the displacement is not complete, and the residual oil is in large clusters [5] (Fig. 4).

Fig. 4.
figure 4

Local horizon map of water flooding experiment (Saturated for Water → Saturated for Oil→ Flooding End). Note: In the experimental photos and all the photos in this paper, the blue is simulated formation water (injected water), the light yellow, yellowish brown and dark brown are crude oil. The direction of fluid displacement is from left to right. This note applies to all pictures in the full text.

The CO2 immiscible oil displacement line direction is uniform, and the oil displacement is thorough. The main types of residual oil are small clusters and blind hole (Fig. 5).

Fig. 5.
figure 5

Local horizon map of CO2 immiscible oil displacement experiment (Saturated for Water → Saturated for Oil→ Flooding End)

When CO2 is miscible/nearly miscible with crude oil, the seepage speed of fluid in pore throat is slow, and the two contacts fully, most of CO2 is pale yellow, the type of residual oil in the small throat is mainly oil film, and there is almost no residual oil in local pore throat (Fig. 6).

Fig. 6.
figure 6

Local horizon map of CO2 miscible oil displacement experiment (Saturated for Water → Saturated for Oil→ Flooding End)

It is generally believed that using CO2 as oil displacement agent can improve oil displacement effect very well.

2.2 Alternate Flooding Experiments

Firstly, the water flooding experiment, when the rock is only residual oil, injection of CO2, after the completion of CO2 immiscible flooding, the main types of residual oil are cluster and blind end, and the effect of oil displacement is improved by gas injection (Fig. 7).

Fig. 7.
figure 7

Local horizon map of flooding end (water flooding end→CO2 immiscible oil displacement end)

Firstly, the water flooding experiment, when the rock is only residual oil, injection of CO2, after the completion of CO2 miscible flooding. Because water flooding has displaced most of the crude oil in pore throat, it is difficult for CO2 gas to miscible with crude oil. After the miscible flooding of CO2, the residual oil type is mainly oil film (Fig. 8).

Fig. 8.
figure 8

Local horizon map of flooding end (water flooding end→CO2 miscible oil displacement end)

Firstly, the CO2 immiscible flooding experiment is carried out, when only residual oil exists in the core, injection of water. Because CO2 gas has the characteristics of high diffusion coefficient, easy compression and low viscosity, it is difficult for CO2 gas to “continuously” distribute in reservoir pore throat, resulting in local residual oil enrichment. After water injection, the injected water can not only squeeze the CO2 into smaller pore throats to displace crude oil, but also displace the island-like residual oil in the large pore channels, thus improving the oil displacement effect (Fig. 9).

Fig. 9.
figure 9

Local horizon map of flooding end (CO2 immiscible oil displacement end → water flooding end)

Firstly, the CO2 miscible flooding experiment is carried out, when only residual oil exists in the core, injection of water. The injected water is interacted by various fluids in the pore throat. Flow and fingering phenomenon are easy to occur. Injected water can displace some of the remaining oil which was not affected in the early stage of CO2 immiscible flooding and improve micro-displacement efficiency. The type of residual oil is blind end and small cluster (Fig. 10).

Fig. 10.
figure 10

Local horizon map of flooding end (CO2 miscible oil displacement end → water flooding end)

2.3 Statistics of Oil Displacement Efficiency

Statistics of displacement efficiency of different displacement modes show that compared with water flooding, the other displacement modes have higher displacement efficiency, which shows that CO2 flooding has a strong advantage in improving displacement efficiency in ultra-low permeability reservoirs [6, 7] (Fig. 11).

Fig. 11.
figure 11

Contrast Diagram of Oil Displacement Efficiency of Different Displacement Modes

In two groups of experiments of water flooding to CO2 flooding, the average displacement efficiency after water flooding is 48.1% and 44.9%, the displacement efficiency of CO2 immiscible/miscible flooding is 60.3% and 67.5%, oil displacement efficiency increased by 12.2% and 22.5%. It is considered that the CO2 miscible flooding after water flooding can greatly improve the oil displacement effect of reservoirs (Fig. 12).

Fig. 12.
figure 12

Statistical Chart of Oil Displacement Efficiency (water flooding→CO2 flooding)

In two groups of experiments of CO2 flooding to water flooding, the average displacement efficiency after CO2 immiscible/miscible is 57.6% and 76.1%, after water flooding, the average oil displacement efficiency is 73.7% and 83.5%, oil displacement efficiency increased by 16.0% and 7.3%. The displacement mode of water flooding after CO2 miscible flooding is a reasonable way to improve oil displacement efficiency in extra low permeability reservoirs (Fig. 13).

Fig. 13.
figure 13

Statistical Chart of Oil Displacement Efficiency (CO2 flooding →water flooding)

3 Conclusion

On the premise of fully considering the difference of samples, through the analysis and summary of the experimental results, the important understanding that can provide guidance for mineral experiment is obtained: Different displacement modes lead to different swept area of the corresponding displacement agent and the occurrence state of residual oil, which leads to different micro-displacement efficiency. Compared with water flooding, CO2 flooding can greatly improve micro-displacement efficiency. In the alternative displacement mode, the conversion of CO2 miscible flooding after water flooding can greatly improve the oil displacement effect of reservoir. For the water flooding after CO2 flooding, the injection water can greatly increase the sweep area and improve the micro-displacement efficiency of reservoir.