Development of operating methods and enhanced oil recovery (EOR) at low-permeability oil reservoirs are required to address the challenge of declining oil production and a transition to the high water-cut period [1, 2]. Gas flooding has unique advantages due to the gas chemical properties, i.e., small molecules, large intermolecular distances, low density, low viscosity, and low flow resistance with compressibility. It is already widely used for EOR in addition to chemical and steam flooding [3]. It has minimal environmental impacts. CO2 gas is the second least expensive flooding fluid after H2O and has been used in EOR for many years. CO2 injection has been used as a commercial EOR process since the 1970s [4]. Currently, greater than 20,000 tons of CO2 per day are delivered for EOR. In America, CO2 flooding enabled crude oil production to be increased with the future efficiency of the method estimated at 4-47 billion barrels of oil [6,7,8].

Several CO2 EOR projects have recently emerged in China under the support of the government. Basic laboratory research and pilot tests of a model process were conducted. It was shown that the low viscosity of CO2 causes it to channel and finger toward the production well and to bypass large amounts of oil during oil recovery with an advancing oil—water front. This effect is especially evident in high heterogeneity reservoirs [9, 10]. CO2 gas appears in the produced liquid to different degrees and dissolves, changes the solution pH, and causes chemical reactions that promote corrosion.

Corrosion has held back the development and broad application of CO2 flooding technology. Gathering facilities are most susceptible to corrosion in practice. Consequently, gathering facility areas were selected for the studies. The research results will be helpful for understanding the corrosion mechanism, developing methods for protecting the facility, and promoting the mature application of CO2 flooding in low-permeability oilfields.

Figure 1 shows a scheme for gathering EOR products from CO2 flooding (at Daqing oilfield, China).

Fig. 1.
figure 1

Scheme for gathering oil-recovery products from CO2 flooding.

Oil from a group of production wells is sent through a pipeline to the manifold. The resulting mixture of oil, gas, and water is transported through metering devices and fed into the separator for preliminary phase separation. The oil mixture flows from the separator into the dehydration station for purification. A tracing band is wound around production wellheads to prevent freezing and blockage due to escaping CO2 and the sharp temperature and pressure changes caused by it. Polyurethane foam is used for insulation of the oil-mixture gathering and separating pipelines. The phase separator in which heating, buffering, gas separation, and free water sedimentation occur is the main gathering facility. Considering the relatively high construction costs and operating pressures from 30 to 45 psi, carbon steel Fe-360 A is usually used to fabricate the gathering facility.

Wells with CO2 flooding were chosen for the study. Samples of the oil—water mixture and gas were taken at the wellhead. The gas composition was analyzed by GC (7890A chromatograph, Agilent Technologies); the liquid composition, by ion chromatography (ICS-1100, Dionex). The number of bacteria was determined using serial dilutions in broth. Corrosion was determined using coupons (50 × 25 × 2 mm) of carbon steel Fe-360 A, i.e., the same material as the gathering facilities. The gas-phase, oil—water-mixture, and aqueous-phase areas in the separator were determined. Corrosion coupons were suspended on the bracket in each area perpendicular to the flow direction. Two brackets with samples were placed in the heating and settling sections, respectively (Fig. 2). Coupons were prepared by soaking in Me2CO for 20 min followed by ultrasonic cleaning, soaking in anhydrous alcohol for 5 min, drying, weighing, and numbering.

Fig. 2.
figure 2

Experimental setup for evaluating corrosion behavior.

After eight months, the brackets were removed. The coupon surfaces were cleaned of greasy deposits using an organic solvent. Then, corrosion products were rinsed off with acid. The coupons were dried and weighed. The corrosion rate was determined from the weight loss. The morphologies of the corrosion coupons were studied on an S-3400N scanning electron microscope (SEM, Hitachi Ltd.). The compositions of the corrosion products were analyzed using energy-dispersive x-ray (EDX) spectroscopy on an EMAX spectroscope (Hitachi Ltd.). X-ray diffraction (XRD) analysis used a TD3500 instrument (Dandong Tongda Science and Technology Co., Ltd.). The following corrosion mechanism was proposed based on the results.

The mixture parameters at the wellhead were temperature, 38°C; average salinity, 4301.48 mg/L; pH, 7.13; and HCO3 and Cl concentrations, 1741.16 and 915.7 mg/L, respectively. Sulfate-reducing bacteria (SRB) were also detected. Besides, the average contents of CO2 and H2S in the associated gas were 16.75 and 2.16%, respectively, because the wells had gas channels. Therefore, the chemical composition and properties of the mixture undoubtedly created corrosive conditions.

The corrosion rate during the experiment was calculated using the equation

$$ CR=\frac{87.6w}{\rho At} $$

where CR is the corrosion rate (mm/yr); w, weight loss (mg); ρ, density (g/mm3); A, experimental coupon area (cm2); and t, immersion time (h).

Figure 3 shows experimental corrosion rates for different gathering-facility areas. It can be seen that the average corrosion rates in the gathering facility were much higher than the limiting allowable value of 0.076 mm/yr except for the gas-phase area in the heating section and the oil—water-mixture area in the settling section.

Fig. 3.
figure 3

Coupon corrosion rate in gathering facility: and □, heating and settling sections, respectively; dashed line shows limiting allowable corrosion rate.

Figure 4 shows the morphologies of experimental coupons from different areas. It can be seen that corrosion occurred mainly in the oil—water-mixture area of the heating section and was dominated by pitting corrosion. Relatively slight uniform corrosion appeared on the coupon surface in the gas-phase area and was attributed to incomplete phase separation of the oil—gas—water mixture in the heating section and associated gas in the gas phase. Correspondingly, the oil—water mixture contained large amounts of residual water that was not separated into the aqueous phase so that corrosion was facilitated. Corrosion appeared faster in the gas- and aqueous-phase areas in the separator settling section and was also dominated by pitting corrosion. Coupons placed in the oil—water-mixture area had only slight corrosion because the produced liquid was fully separated in the settling section after heating. The CO2 escaped to the gas-phase area and dominated the corrosion mechanism in the presence of water so that corrosion pits emerged. Coupon surfaces were in contact mainly with the oil phase in the oil—water-mixture area after separation of free water. This naturally restrained corrosion. The corrosion characteristics in the aqueous-phase area were similar to those in the heating section although the corrosion rate in the gas phase increased significantly. Further studies of the morphological characteristics confirmed the quantitative analyses of the corrosion rate.

Fig. 4.
figure 4

Surface morphologies of corrosion coupons in heating (left) and settling sections (right) (100Ч magnification): a, b, c) gas-phase, oil—water-mixture, and aqueous-phase areas, respectively.

Analytical results showed that the corrosion products in all gathering facility areas were similar. The elemental composition was analyzed by EDX and detected C, O, Fe, S, and Ca (Fig. 5). The surface morphology revealed powder precipitation surrounded by crystals (Fig. 6). The outer appearance suggested that the corrosion products consisted mainly of Fe2O3 with small amounts of FeS. Quantitative XRD analysis showed that the Fe2O3 content reached 70% (Fig. 7). The analytical data indicated that the corrosion behavior was determined by the presence of CO2.

Fig. 5.
figure 5

Energy-dispersive x-ray analysis of corrosion products in aqueous- (a) and gas-phase areas (b) of the heating section.

Fig. 6.
figure 6

Surface morphologies of corrosion products in the aqueous- (a) and gas-phase areas (b) of the heating section (500 × magnification).

Fig. 7.
figure 7

X-ray diffraction analysis of corrosion products.

The CO2 corrosion mechanism was affected by several factors including the temperature, pH value, flow rate, and CO2 pressure. It was reported that the corrosion rate and pitting severity increased with decreasing pH and increasing CO2 pressure [11, 12]. Generally, the main reaction was dissolution of CO2 in water to form carbonic acid (H2CO3). At the same time, Fe2+ diffused into the solution to form FeCO3 as the corrosion product when the Fe2+ and CO32– concentrations exceeded the solubility product of FeCO3. The chemical reactions were as follows.

CO2 is sparingly soluble in water and produces H2CO3:

$$ {\displaystyle \begin{array}{c}{\mathrm{CO}}_2(gas)\to {\mathrm{CO}}_2(water)\\ {}{\mathrm{CO}}_2(water)+{\mathrm{H}}_2\mathrm{O}\to {\mathrm{H}}_2{\mathrm{CO}}_3\end{array}} $$

H2CO3 dissociates partially in two steps to form bicarbonate (HCO3) and carbonate (CO32–) ions:

$$ {\mathrm{H}}_2{\mathrm{CO}}_3\to {\mathrm{H}\mathrm{CO}}_3^{-}+{\mathrm{H}}^{+} $$
$$ {\mathrm{H}\mathrm{CO}}_3^{-}\to {{\mathrm{CO}}_3}^{2-}+{\mathrm{H}}^{+} $$

Solid iron carbonate is formed:

$$ {\mathrm{Fe}}^{2+}+{{\mathrm{CO}}_3}^{2-}\to {\mathrm{Fe}\mathrm{CO}}_3 $$

Several electrochemical reactions occur during the CO2 corrosion process. Adsorption of H2CO3 on a steel surface is followed by reduction of H+:

$$ 2{\mathrm{H}}^{+}+2e\to {\mathrm{H}}_2 $$

Iron oxidation occurs simultaneously:

$$ \mathrm{Fe}\to {\mathrm{Fe}}^{2+}+2{e}^{-} $$

As a rule, FeCO3 formation plays an important role in the corrosion behavior because the FeCO3 layer prevents mass transfer of the corrosive species and protects the steel surface from the corrosive environment. In this sense, the presence of the FeCO3 layer should enable the CO2 corrosion rate to be controlled. However, the large number of SRB in the produced liquid also cause additional electrochemical corrosion behaviors and promoted corrosion of the steel surface despite the layer of deposited FeCO3:

$$ {\displaystyle \begin{array}{c}{{\mathrm{S}\mathrm{O}}_4}^{2-}\underset{SRB}{\to }8\mathrm{H}+{\mathrm{S}}^{2-}+4{\mathrm{H}}_2\mathrm{O}\\ {}2{\mathrm{H}}^{+}+{\mathrm{S}}^{2-}\to {\mathrm{H}}_2\mathrm{S}\\ {}{\mathrm{Fe}}^{2+}+{\mathrm{S}}^{2-}\to \mathrm{FeS}\end{array}} $$

Furthermore, differences in the ion concentrations activated local galvanic corrosion after the formation of corrosion pits of different depths and origins. High concentrations of Cl in the produced liquid caused destructive pitting corrosion and led to stress cracking corrosion behavior of the facility structures. In addition, CO2 not only contributed directly to the main electrochemical reaction but also was involved in hydrogen reduction on contact of carbon steel Fe-360 A with H2S dissolved in water.

Thus, the complex characteristics of the produced liquid with CO2 were inherent causes of corrosion and scaling in the gathering facility. The selection of facility materials and the limited budget for oilfield development were external causes. The oil—gas—water separator was used as an example to show that the degree of gas channeling, CO2 escape time, and separation performance of water were responsible for differences in the corrosion behavior.

Pitting corrosion with the formation mainly of Fe2O3 and FeS was the main corrosion behavior of steel Fe-360 A in the presence of CO2. The corrosion kinetics and mechanism depended on combined effects of CO2 and SRB in the produced mixture.