Paper No. 5623 Study of Siderite Solubility under Extreme High Temperature and Pressure in 1 M NaCl Solution Chao Yan, Paula Guraieb, Jin Huang and Ross C. Tomson Brine Chemistry Solutions, LLC 8285 El Rio Street, Suite 100 Houston, TX, 77054 ABSTRACT With the continued development of offshore production in ultra-deepwater (UDW), more and more wells are exposed to extremely high pressure and temperature (xHPHT) under anoxic condition. In order to better predict scale formation, scale solubility under these extreme conditions need to be accurate. Knowledge of the thermodynamic and kinetic properties of this mineral under xHPHT conditions is important for the solubility studies. Research to expand the amount of data and models for such minerals at these conditions will reduce offshore production risk and improve human safety in ultradeepwater production. A novel flow-through apparatus has been developed to perform scale solubility, dissolution and precipitation studies of various minerals under high pressure (up to 24,000 psig), high temperature (up to 250 °C), and high total dissolved solids (TDS, up to 360,000 mg/L). This research focused on the solubility of siderite under strictly anoxic (<<1 ppb O2) xHPHT conditions. This study increased our understanding of the formation of passive layers (Fe3O4 and FeCO3) and their phase transitions as temperature increases, as has been observed in corrosion research. In this work, effects of reaction conditions, including temperature and pressure have been investigated. Key words: solubility product, siderite, saturation index, scale prediction, corrosion, deepwater production, ultra high pressure and high temperature (xHPHT), oil and gas industry, strictly anoxic INTRODUCTION As the fourth most abundant metal on earth, iron is commonly found in a variety of rock and soil minerals as Fe2+ and Fe3+. Ferrous carbonate is the main source of iron (II) in nature under anoxic conditions. The dissolution of naturally formed ferrous carbonate may contribute to the high iron concentration in the connate water. Iron concentration measured in produced water might be from various sources including corrosion and dissolution of naturally occurred siderite as well as corrosion ©2015 by NACE International. Requests for permission to publish this manuscript in any form, in part or in whole, must be in writing to NACE International, Publications Division, 15835 Park Ten Place, Houston, Texas 77084. The material presented and the views expressed in this paper are solely those of the author(s) and are not necessarily endorsed by the Association. 1 products (Fe3O4 and FeCO3). With the continued development of offshore production in ultra-deepwater (UDW) Gulf of Mexico (GoM), more and more wells are exposed to extremely high temperature and pressure (xHPHT) under anoxic conditions. A greater understanding of siderite dissolution and formation under these conditions is needed to better understand the source of iron in produced waters. In addition, FeCO3 is also a major source of scale in production systems, which can cause serious problems. 1 If the connate water with high iron concentration is mixed with produced water, scaling issues may occur. For example, a potential mechanism for part of the production decline in the Prudhoe Bay field is siderite scale deposition.2 Therefore, to better predict scale formation, scale solubility under these conditions must be as accurate as possible. Siderite (FeCO3) is the most common corrosion product at intermediate temperatures (60-150 °C), forming a passive layer to protect the metal surface and preventing further corrosion.3-6 However, under high temperature conditions (> 150 °C), magnetite appears to be the dominant deposit on oil and gas production pipes and facilities, especially on carbon steel.7-9 It has been suggested that the formation of ferrous carbonate may be a necessary intermediate step to obtain a protective magnetite layer.10 A solubility study of siderite will benefit not only understanding of FeCO3 scale formation, but also the dissolution processes of passive layers for corrosion studies under extreme conditions. Even though various models have been developed to predict FeCO3 solubility, few of them can make prediction under xHPHT. More importantly, very few experimental data has been reported to validate the predictions. Solubility of siderite has been studied at different temperatures, ionic strength, electrolytes and CO2 partial pressure by various researchers, as listed in Table 1.11-23 Most of the experimental work has been done below 100 °C. However, even under ambient conditions, solubility product of siderite has ± 0.3 saturation index (SI) unit difference between the reported values from various literature sources. More interestingly, the way of preparing siderite crystals (wet vs. dry) also gives the pKsp values ± 0.3 SI unit difference. The author can only locate one publication that studied the siderite solubility from 100 °C to 250 °C.22 However, this study was under ionic strength of 0.1 M NaCl and saturated pressures at these temperatures. Moreover, the effect of ionic strength up to 5 M NaCl on siderite solubility has been studied only at room temperature by Silva et al..18 In addition, the effect of the partial pressure of CO2 on the dissolution of siderite has also been investigated.23 However, limited research on the effect of high temperature, high pressure and high ionic strength on solubility of siderite has been performed. The emphasis of this work is on the solubility of siderite at high temperature (up to 250 °C) and high pressure (up to 24,000 psig) in 1 M NaCl solution under a constant CO2 partial pressure and strictly anoxic conditions (<< 1 ppb O2). ©2015 by NACE International. Requests for permission to publish this manuscript in any form, in part or in whole, must be in writing to NACE International, Publications Division, 15835 Park Ten Place, Houston, Texas 77084. The material presented and the views expressed in this paper are solely those of the author(s) and are not necessarily endorsed by the Association. 2 Table 1 Summary of siderite solubility product pKsp reports T (°C) P (psig) I (M) Solution pKsp (siderite) References 30 14.7 0.01 NaCl 10.46 17 14.7 0.1 NaClO4 10.12 Smith11 Singer et al.12 22.5 14.7 0.1 NaClO4 10.22 25 14.7 0.1 NaClO4 10.24 30 20 14.7 14.7 0.1 0.002 NaClO4 water 10.25 10.40 50 30 40 50 60 70 80 25 25 43 62 83 94 25 25 25 25 25 25 50 75 100 150 200 250 16.5 15.3 15.8 16.5 17.6 19.2 21.6 14.7 14.7 15.8 17.6 21.6 26.5 14.7 14.7 14.7 14.7 14.7 14.7 16.5 20.3 29.4 83.7 240.0 590.7 1 0.002 0.002 0.002 0.002 0.002 0.002 1 0.002 0.002 0.002 0.002 0.002 0.002 0.002 0.002 0.002 1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 NaClO4 water water water water water water NaClO4 water water water water water water water water water NaCl NaCl NaCl NaCl NaCl NaCl NaCl NaCl 11.20 11.11 11.27 11.88 12.13 12.31 12.57 10.80 10.77 10.94 11.03 11.25 11.42 10.93 11.03 11.03 10.43 9.04 10.93 11.14 11.58 11.91 12.81 13.56 14.62 Bardy et al.13 Reiterer et al.14 Braun16 Bruno et al.15 Greenberg et al.17 Ptacek et al.19 Ptacek et al.20 Jensen et al., (dry crystal)21 Jensen et al., (wet crystal)21 Silva et al.18 P. Bénézeth et al.22 EXPERIMENTAL Flow-through Apparatus In this research, by using customized flow-through apparatus (Figure 1), the solubility of FeCO3 has been investigated. All wetted parts are made of Polytetrafluoroethylene (PTFE) lined UNS N10276* to ©2015 by NACE International. Requests for permission to publish this manuscript in any form, in part or in whole, must be in writing to NACE International, Publications Division, 15835 Park Ten Place, Houston, Texas 77084. The material presented and the views expressed in this paper are solely those of the author(s) and are not necessarily endorsed by the Association. 3 prevent corrosion at these conditions in order to minimize Fe concentration from the background. A high pressure continuous feed pump with maximum pressure 25,000 psig is used to continuously deliver feeding solutions up to 24,000 psig at constant flow rate. An air actuated back pressure regulator was connected at the end of the system to maintain constant pressure throughout the system. A polytetrafluoroethylene (PTFE) lined UNS N10276 column was used to pack siderite particles. A titanium (Ti) frit was placed at each end of the column to prevent the small particles from flowing out. Another pump is used to introduce a chelating agent before temperature and pressure drops to prevent Fe2+ re-precipitation as temperature and pressure decrease to ambient conditions. Flow rate for all the experiments are adjusted from 0.03 to 0.1 ml/min, the retention time for feed solution in the packed column is from 35 to 181 minutes, which allows feed solution to equilibrate at desired temperatures and pressures. All tubing and fittings are rated to a pressure of at least 30,000 psig. The total volume of the system including the tubing, fittings and the reactor column was approximately 12 ml. Temperature was controlled by a GC oven. Cooling Stage Column Sampling Pump Back Pressure Regulator Oven Pump (chelating agent) Figure 1. Flow-through apparatus for mineral solubility study. Preparation of Siderite Particles and Feed Solutions FeCO3 particles were prepared in 1 M NaCl solution. The dissolved oxygen (DO) was removed from the 1 M NaCl solution. The concentration of DO was measured << 1 ppb, indicating a strictly anoxic condition for FeCO3 formation. Approximately 35 g of ferrous ammonium sulfate hexahydrate (99+% from Acros organics) was added into the 200 ml bottle and 16 g of sodium bicarbonate (99% from LabChemโ ) was added into the 500 ml bottle with continuous CO2 sparging. Both solutions were heated in a 70 °C water bath. Then the ferrous solution was manually poured into the bicarbonate solution to produce a white to light grey buff solid, ferrous carbonate. The precipitates were settled and washed several times with deoxygenated water to remove sodium and ammonium sulfate. Particles were then dried (as shown in Figure 2) and packed into the column in a N2 filled glove bag. Solids were characterized by scanning electronic microscope (SEM) and X-Ray diffraction (XRD) to check the morphology and confirm the structure of FeCO3. In Figure 3, an XRD spectrum of synthesized FeCO3 particles is shown to confirm that the powder is single phase siderite. There are no other peaks in the spectrum indicating that only siderite was produced. In Figure 4, SEM image shows spherical shaped particles with single particle size from 0.6 µm to 1.3 µm. Some agglomeration occurred and the aggregates are up to 2.1 µm. Particle size distribution is narrow with an average size of approximately 0.9 µm (Figure 4, insert). * Unified Numbering System for Metals and Alloys (UNS) โ Trade name ©2015 by NACE International. Requests for permission to publish this manuscript in any form, in part or in whole, must be in writing to NACE International, Publications Division, 15835 Park Ten Place, Houston, Texas 77084. The material presented and the views expressed in this paper are solely those of the author(s) and are not necessarily endorsed by the Association. 4 Figure 2. Picture of white to light gray siderite solids synthetized. PDF-00-012-0531-FeCO3 Exp-FeCO3 450 Intensity (count) 400 350 300 250 200 150 100 50 0 20 30 40 50 60 70 80 2ษต Figure 3. XRD spectrum of dried siderite after washing. Black line shows the experimental data. Red circles show the standard rhombohedral structure pattern of siderite (PDF# 00-012-0531). ©2015 by NACE International. Requests for permission to publish this manuscript in any form, in part or in whole, must be in writing to NACE International, Publications Division, 15835 Park Ten Place, Houston, Texas 77084. The material presented and the views expressed in this paper are solely those of the author(s) and are not necessarily endorsed by the Association. 5 40 Particle number 35 30 25 20 15 10 5 0 0.59 0.74 0.88 1.03 1.18 1.32 Particle size (µm) Figure 4. SEM image of synthesized FeCO3 with particle size from 0.6 µm to 1.3 µm. Feed solution containing 1 M NaCl, 10.6 mg/L Fe2+ (Fe(NH4)2(SO4)2·6H2O, 99+%, Acros) and 103 mg/L HCO3- (NaHCO3, ACS grade, LabChem Inc.) was used for flow-through solubility study. Solution was vigorously sparged with 100% CO2 under 1 atm in a pressure vessel to remove dissolved oxygen. The vessel was then pressurized to ~ 4 atm (60 psig) to promote dissolution of FeCO3 solids. Feed solution was continuously pumped into the siderite packed column until continuous liquid flow was observed in the effluent to make sure there were no air bubbles trapped in the system. Then the pressure was adjusted to the target pressure, followed by adjustment of temperature. Effluent samples were then collected in Ar purged sample tubes at targeted flow rates. The volume of collected effluent was measured to calculate the actual flow rate. Effluent was analyzed immediately after sample collection using HACH method for ferrous iron concentration and total alkalinity. Inductively coupled plasma atomic emission spectroscopy (ICP-OES) was also used to measure total iron concentration for validation. RESULTS AND DISCUSSION The assumed reaction can be expressed as: ๐น๐๐ถ๐3,(๐ ) โ ๐น๐ 2+ + ๐ถ๐32โ The saturation index (SI) defined as the logarithm of the ion activity product divided by the solubility product of siderite as shown in equation 1, ๐๐น๐2+ ๐๐ถ๐2โ ๐๐ผ๐น๐๐ถ๐3 = ๐๐๐10 ( 3 ๐พ๐ ๐,๐น๐๐ถ๐3 ๐๐น๐2+ ๐พ๐น๐2+ ๐๐ถ๐2โ ๐พ๐ถ๐2โ ) = ๐๐๐10 ( 3 ๐พ๐ ๐,๐น๐๐ถ๐3 3 ) (1) where ๐๐น๐ 2+ is the measured Fe2+ molar concentration, ๐๐ถ๐32โ is molar concentrations of CO32- which can be calculated from measured total alkalinity, ๐พ๐น๐ 2+ and ๐พ๐ถ๐32โ are activity coefficients of the species ©2015 by NACE International. Requests for permission to publish this manuscript in any form, in part or in whole, must be in writing to NACE International, Publications Division, 15835 Park Ten Place, Houston, Texas 77084. The material presented and the views expressed in this paper are solely those of the author(s) and are not necessarily endorsed by the Association. 6 calculated by using Pitzer24-26 theory based ScaleSoftPitzerโ under different temperatures and pressures (Table 2). When equilibrium is reached, SI of FeCO3 should be zero, i.e. ๐พ๐ ๐,๐น๐๐ถ๐3 = ๐๐น๐ 2+ ๐พ๐น๐ 2+ ๐๐ถ๐32โ ๐พ๐ถ๐32โ (2) Table 2 Calculated activity coefficients in 1 M NaCl T (°C) P (psig) 150 150 150 150 250 250 250 250 5534 11240 18680 24000 4856 9345 18780 23390 ฮณ(Fe2+) 0.068 0.079 0.092 0.103 0.014 0.019 0.028 0.033 ฮณ(CO32-) 0.019 0.022 0.024 0.025 0.0022 0.0031 0.0052 0.0053 Solubility of FeCO3 was measured up to 250°C, 24,000 psig and 1 M NaCl. Experimental results including the temperature (150 °C and 250 °C), pressure (from ~5,000 psig to 24,000 psig), pH (at ambient condition) as well as the measured Fe2+ and HCO3- concentrations are shown in Table 3. Also in that table, Ksp values calculated using experimental data (pKsp) and predicted (pKsp*) are listed as well and the SI values of FeCO3 were calculated. The SI values at 150 °C and lower pressures have good agreement with the predicted values with variation up to 0.1 SI unit. On the other hand, these values varied from 0.22 to 0.41 SI units under 150 °C with high pressures (> 20,000 psig) and 250 °C. Table 3 Experimental and theoretical results for siderite solubility experiments under xHPHT in 1 M NaCl Exp # 1 2 3 4 5 6 7 8 a โ log[Alkalinity]a pH measured 2+ a T (°C ) P (psig) log[Fe ] meas measured at at 25 °C 25 °C 150 5534 5.16 -2.562 -2.267 150 11240 5.31 -2.441 -2.113 150 18680 5.5 -2.321 -1.940 150 24000 5.68 -2.131 -1.756 250 4856 4.82 -3.016 -2.671 250 9345 5.18 -2.498 -2.229 250 18780 5.37 -2.363 -2.045 250 23390 5.56 -2.226 -1.934 [CO32-] calca x10 7 6.72 12.57 24.57 56.66 5.58 12.62 29.59 48.21 pKsp pKsp* (from pKsp - pKsp* (from exp) prediction) 11.64 11.07 10.54 9.93 13.65 13.02 11.74 11.28 11.59 10.97 10.17 9.64 13.24 12.68 11.52 10.95 Molar concentration of species in effluent Trade name ©2015 by NACE International. Requests for permission to publish this manuscript in any form, in part or in whole, must be in writing to NACE International, Publications Division, 15835 Park Ten Place, Houston, Texas 77084. The material presented and the views expressed in this paper are solely those of the author(s) and are not necessarily endorsed by the Association. 7 0.05 0.1 0.37 0.29 0.41 0.34 0.22 0.33 The pressure dependence of pKsp values at 150 °C and 250 °C are shown in Figure 5 and 6 respectively. At both temperatures, pKsp values from both experimental data (blue circles) and prediction (red diamonds) decrease with increased pressure. The regression of both experimental data (blue solid line) and prediction (red dotted line) suggest a linear relationship between pKsp and pressure (R-squared value is 0.9924 at 150 °C and 0.9973 at 250 °C respectively). 13 150 °C 12 y = -8.9582E-05x + 1.2127E+01 R² = 9.9235E-01 pKsp (FeCO3) 11 150 °C, 83.7 psig, 1M NaCl 10 experimental Predicted calculated from this study calculated from prediction Benezeth et al. Linear (experimental) Linear (Predicted) 9 8 R² = 0.9997 7 0 5000 10000 15000 20000 25000 Pressure (psig) Figure 5. pKsp values of FeCO3 at 150 °C and different pressures in 1 M NaCl. Blue dotsexperimental data, blue solid line-curve fitting of experimental data, green dot-calculated pKsp value at 150 °C and 83.7 psig from curve fitting of experimental data, red diamonds-predicted values, red dotted line-curve fitting of predicted values, pink diamond-calculated pKsp value at 150 °C and 83.7 psig from curve fitting of predicted values. 15 250 250 °C,°C 590.3 psig 14 y = -1.2860E-04x + 1.4230E+01 R² = 9.9731E-01 pKsp (FeCO3) 13 250 °C, 590.3 psig, 1M NaCl 12 experimental Predicted calculated from this study calculated from prediction Benezeth et al. Linear (experimental) Linear (Predicted) 11 10 R² = 1 9 0 5000 10000 15000 20000 25000 Pressure (psig) ©2015 by NACE International. Requests for permission to publish this manuscript in any form, in part or in whole, must be in writing to NACE International, Publications Division, 15835 Park Ten Place, Houston, Texas 77084. The material presented and the views expressed in this paper are solely those of the author(s) and are not necessarily endorsed by the Association. 8 Figure 6. pKsp values of FeCO3 at 250 °C and different pressures in 1 M NaCl. Blue dotsexperimental data, blue solid line-curve fitting of experimental data, green dot-calculated pKsp value at 250 °C and 590.3 psig from curve fitting of experimental data, red diamonds-predicted values, red dotted line-curve fitting of predicted values, pink diamond-calculated pKsp value at 250 °C and 590.3 psig from curve fitting of predicted values. In order to validate pKsp values under high pressure and their change with pressure, some extrapolation and calculations have been made because no other experimental data under high pressure and 1 M NaCl is available. In Figure 5, pKsp value (12.12, green dot) at 150 °C and its saturated pressure 83.7 psig was calculated by using curve fitting equation 3, ๐๐พ๐ ๐ = โ8.9582 × 10โ5 ๐ + 12.127 (3) where P is the pressure at 150 °C in psig. At 250 °C and 590.3 psig, pKsp value (14.17, green dot) was calculated by using curve fitting equation 4, ๐๐พ๐ ๐ = โ1.2860 × 10โ4 ๐ + 14.230 (4) where P is the pressure at 250 °C in psig. Thus, in Figure 7, the above pKsp values at 150 °C and 250 °C were plotted as green dots and curve fitted with linear function (solid green line), based on the assumption that pKsp values will decrease linearly as temperature increases. It is consistent with the published experimental data from Bénézeth et al.22 (blue crosses, curve fitted with blue dotted line), Greenberg et al.17 (orange squares, curve fitted with orange dotted line), Braun et al. 16 (purple pluses, curve fitted with purple dotted line) as well as the predicted pKsp values (red diamonds, curve fitted with red dotted line). ©2015 by NACE International. Requests for permission to publish this manuscript in any form, in part or in whole, must be in writing to NACE International, Publications Division, 15835 Park Ten Place, Houston, Texas 77084. The material presented and the views expressed in this paper are solely those of the author(s) and are not necessarily endorsed by the Association. 9 this study-Ksp in 1 M NaCl calculated from this study predicted Ksp in 1 M NaCl Silva-Ksp in 1 M NaCl Benezeth-Ksp in 0.1 M NaCl Tomson-Ksp in 0.002 M IS Braun-Ksp in 0.002 M IS Linear (this study-Ksp in 1 M NaCl) Linear (predicted Ksp in 1 M NaCl) Linear (Benezeth-Ksp in 0.1 M NaCl) Linear (Tomson-Ksp in 0.002 M IS) Linear (Braun-Ksp in 0.002 M IS) 16 R² = 0.9932 15 pKsp (FeCO3) 14 R² = 0.9997 R² = 0.9632 13 12 y = 2.0500E-02x + 9.0450E+00 R² = 1.0000E+00 11 R² = 0.9742 10 9 8 0 50 100 150 200 250 300 T (°C) Figure 7. pKsp values of FeCO3 at different temperatures under water vapor pressure in solutions with various ionic strength. Green dots-calculated pKsp values from experimental data, green solid line-curve fitting of experimental data, pink dot-calculated pKsp value at 25 °C and 14.7 psia from curve fitting of experimental data, red diamonds-predicted values, red dotted line-curve fitting of predicted values, black triangle-calculated pKsp value at 25 °C and 14.7 psia from Silvaโs model18, blue crosses-experimental data from Bénézeth et al.22, blue dotted linecurve fitting of experimental data from Bénézeth et al.22, orange square-experimental data from Greenberg et al.17, orange dotted line-curve fitting of experimental data from Greenberg et al.17, purple plus-experimental data from Braun et al.16, purple dotted line-curve fitting of experimental data from Braun et al..16 Therefore pKsp value (9.56, pink dot) at 25 °C, 14.7 psia in 1 M NaCl can be calculated from curve fitting equation 5, ๐๐พ๐ ๐ = โ2.05 × 10โ2 ๐ + 9.045 (5) where T is the temperature in °C. The black triangle in Figure 7 is the pKsp value (9.039) calculated from equation 6, โ๐๐พ๐ ๐ = โ10.9 + 2.518 ๐ผ 0.5 โ 0.657 ๐ผ (6) where ๐ผ is the ionic strength at ambient condition, the model created by Silva et al. to calculated pKsp value at ambient condition in solutions with different ionic strength.18 The calculated pKsp value from this study has 0.52 SI unit difference from the calculated value from Silva et al.. 18 It is a reasonable result and proves that the pKsp values under xHPHT and their changes with pressure are very accurate under these extreme conditions. ©2015 by NACE International. Requests for permission to publish this manuscript in any form, in part or in whole, must be in writing to NACE International, Publications Division, 15835 Park Ten Place, Houston, Texas 77084. The material presented and the views expressed in this paper are solely those of the author(s) and are not necessarily endorsed by the Association. 10 The solid samples were analyzed by SEM and XRD. After the experiments, the solid changed color from gray to brick red, and the phase of hematite (Fe2O3, blue dots) associated with siderite (red squares) were detected by XRD (Figure 8). The transition of these two phases is not defined. It could be during the experiment at high temperature. Compared with previous characterization of initial siderite particles, particle size of siderite after experiments increased with better crystallinity. Well crystallized hematite particles with bipyramide shape and particle size of 0.5-1 µm (Figure 9, in red circles) were observed as well as small particles of siderite. Magnetite phase is not clearly observed (green triangles in Figure 8). 1200 exp 1000 FeCO3-00-0012-0531 Fe2O3-01-077-9925 Intensity 800 Fe3O4-00-019-0629 600 400 200 0 20 30 40 50 60 70 80 2 theta Figure 8. XRD of solid sample after 250 °C experiment. Black line-experimental data, red squares-siderite phase, blue dots-hematite phase, green triangles-magnetite phase. Figure 9. SEM of FeCO3 and hematite particles after 250 °C experiment. Red circles show the bipyramid shape of hematite. ©2015 by NACE International. Requests for permission to publish this manuscript in any form, in part or in whole, must be in writing to NACE International, Publications Division, 15835 Park Ten Place, Houston, Texas 77084. The material presented and the views expressed in this paper are solely those of the author(s) and are not necessarily endorsed by the Association. 11 CONCLUSIONS This study evaluates the solubility of siderite at extreme high temperature and pressure in 1 M NaCl solution. From comparison between the predicted pKsp values and from the experimental data, there is confidence that the experimental method used is able to reliably simulate the extreme temperature (up to 250 °C), pressure (up to 24,000 psig) and strictly anoxic (<< 1 ppb dissolved oxygen) conditions encountered in ultra-deep water production. This study expands the current experimental data set for siderite solubility in 1 M NaCl solution under high pressure. Experimental values have a maximum difference of 0.41 SI unit from the predicted values; which is very accurate at these xHTHP conditions. Due to the limited data available, the results from this study were used to calculate pKsp value under ambient condition in 1 M NaCl so that the derived results can be compared with published experimental data. The derived pKsp value has 0.52 SI unit difference from previous literature, which also validate the experimental data and the change with pressure. Solids after entire experiments were characterized by XRD and SEM. The appearance of hematite phase associated with siderite in the solid sample was observed. ACKNOWLEDGEMENTS Funding for the projects is provided through the โUltra-Deepwater and Unconventional Natural Gas and Other Petroleum Resources Research and Development Programโ authorized by the Energy Policy Act of 2005. This programโfunded from lease bonuses and royalties paid by industry to produce oil and gas on federal landsโis designed to assess and mitigate risk enhancing the environmental sustainability of oil and gas exploration and production activities. RPSEA is under contract with the U.S. Department of Energyโs National Energy Technology Laboratory to administer three areas of research. RPSEA is a 501(c)(3) nonprofit consortium with more than 180 members, including 24 of the nation's premier research universities, five national laboratories, other major research institutions, large and small energy producers and energy consumers. The mission of RPSEA, headquartered in Sugar Land, Texas, is to provide a stewardship role in ensuring the focused research, development and deployment of safe and environmentally responsible technology that can effectively deliver hydrocarbons from domestic resources to the citizens of the United States. Additional information can be found at www.rpsea.org. The advice from Prof. Mason B. Tomson, Civil and Environmental Engineering department at Rice University, on the conduct of this research is gratefully acknowledged. REFERENCES 1. A. Kan, and M.B. Tomson, "Scale prediction for oil and gas production," SPE Journal 17.2 (2012): pp.362-378. 2. B.G. Kriel, C.A. Lacey and R.H. Lane. โThe performance of scale inhibitors in the inhibition of iron carbonate scale,โ SPE J., SPE-27390, 1994, 465-471. 3. M.L. Johnson, and M.B. Tomson. "Ferrous carbonate precipitation kinetics and its impact CO2 corrosion," CORROSION 91, paper no. 268, (Houston, TX:NACE International, 1991). 4. S. Nesic, "Integrated CO2 corrosion-multiphase flow model," SPE International Symposium on Oilfield Corrosion, 2004. 5. W. Sun, S. Papavinasam, and S. Nesic. "Kinetics of iron sulfide and mixed iron sulfide/carbonate scale precipitation in CO2/H2S corrosion," CORROSION/06, paper no. 644, (Houston, TX: NACE International, 2006). 6. M.B. Tomson, and M.L. Johnson. "How ferrous carbonate kinetics impacts oilfield corrosion," SPE International Symposium on Oilfield Chemistry, 1991. ©2015 by NACE International. Requests for permission to publish this manuscript in any form, in part or in whole, must be in writing to NACE International, Publications Division, 15835 Park Ten Place, Houston, Texas 77084. The material presented and the views expressed in this paper are solely those of the author(s) and are not necessarily endorsed by the Association. 12 7. J. Huang, P. Guraieb, E. Contreras, C. Yan, M.B. Tomson and R.C. Tomson. โCorrosion Behavior of Deepwater Oil Production Tubing Materials under Extremely High Temperature and High Pressure,โ OTC 2014, OTC-25193 8. P.R. Tremaine and J.C. LeBlanc. โThe solubility of magnetite and the hydrolysis and oxidation of Fe2+ in water to 300 °C,โ Journal of Solution Chemistry, Vol. 9, No.6, 1980, 415-441. 9. P.R. Tremaine, R.V. Massow and G.R. Shierman. โA calculation of Gibbs free energies for ferrous ions and the solubility of magnetite in H2O and D2O to 300 °C,โ Thermachimica Acta. 19, 1977, 287300. 10. H. Sontheimer, W. Kolle and V.L. Snoeyink. โThe siderite model of the formation of corrosion resistant scales,โ J. AWWA. 1981, 73, 572-579. 11. H.J. Smith. โOn equilibrium in the system ferrous carbonate, carbon dioxide, and water,โ J. Am. Chem. Soc. 1918, 40, 879โ883. 12. P.C. Singer, W. Stumm. โThe solubility of ferrous iron in carbonate-bearing waters,โ J. Am. Water Works Assoc. 1970, 62, 198โ202. 13. J. Bardy and C. Péré. โDétermination expérimentale du coefficient de solubilité du carbonate ferreux en milieux aqueux,โ Trib. CEBEDEAU 1976, 29 (387), 75โ81. 14. F. Reiterer, W. Johannes and H. Gamsjäger. โSemimicro determination of solubility constants: copper (II) carbonate and iron (II) carbonate,โ Mikrochim. Acta 1981, 1, 63โ72. 15. J. Bruno, P. Wersin and W. Stumm. โOn the influence of carbonate in mineral dissolution: II. The solubility of FeCO3(s) at 25 °C and 1 atm total pressure,โ Geochim. Cosmochim. Acta 1992, 56, 1149โ1155. 16. R. D. Braun. โSolubility of iron (II) carbonate at temperatures between 30 and 80 °C,โ Talanta 1991, 38, 205โ211. 17. J. Greenberg and M.B. Tomson. โPrecipitation and dissolution kinetics and equilibria of aqueous ferrous carbonate vs temperature,โ Appl. Geochem. 1992, 7, 185โ190. 18. C.A.R. Silva, X. Liu and F.J. Millero. โSolubility of siderite (FeCO3) in NaCl solutions,โ J. Solution Chem. 2002, 31, 97โ108. 19. C.J. Ptacek and E.J. Reardon, โSolubility of siderite (FeCO3) in concentrated NaCl and Na2SO4 solutions at 25 °C,โ WaterโRock Interaction, Proc. Int. Symp., 1992, 7th, pp. 181โ183. 20. C.J. Ptacek and D.W. Blowes. โInfluence of siderite on the pore-water chemistry of inactive minetailings impoundments,โ In: Alpers, C.N., Blowes, D.W. (Eds.), Environmental Geochemistry of Sulfide Oxidation, 1994. American Chemical Society, Washington, DC, pp. 172โ189. 21. D.L. Jensen, J.K. Boddum, J.C. Tjell and T.H. Christensen. โThe solubility of rhodochrosite (MnCO3) and siderite (FeCO3) in anaerobic aquatic environments,โ Appl. Geochem. 2002, 17, 503โ511. 22. P. Bénézeth, J.L. Dandurand and J.C. Harrichoury. โSolubility product of siderite (FeCO3) as a function of temperature (25-250 °C),โ Chemcial Geology, 265, 2009, 3-12. ©2015 by NACE International. Requests for permission to publish this manuscript in any form, in part or in whole, must be in writing to NACE International, Publications Division, 15835 Park Ten Place, Houston, Texas 77084. The material presented and the views expressed in this paper are solely those of the author(s) and are not necessarily endorsed by the Association. 13 23. S.V. Golubev, P. Bénézeth, J. Schott, J.L. Dandurand and A. Castillo. โSiderite dissolution kinetics in acidic aqueous solutions from 25 to 100 °C and 0 to 50 atm pCO2.โ Chemical Geology, 265, 2009, 13-19. 24. G.N. Lewis and M. Randall. โThermodynamics,โ Revised by K.S. Pitzer; L. Brewer McGraw-Hill, New York 377 (1961): 84. 25. K.S. Pitzer. "Thermodynamics of electrolytes. I. Theoretical basis and general equations," The Journal of Physical Chemistry 77.2 (1973): 268-277. 26. C.J. Peiper and K.S. Pitzer. "Thermodynamics of aqueous carbonate solutions including mixtures of sodium carbonate, bicarbonate, and chloride," The Journal of Chemical Thermodynamics 14.7 (1982): 613-638. ©2015 by NACE International. Requests for permission to publish this manuscript in any form, in part or in whole, must be in writing to NACE International, Publications Division, 15835 Park Ten Place, Houston, Texas 77084. The material presented and the views expressed in this paper are solely those of the author(s) and are not necessarily endorsed by the Association. 14
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