The disclosure relates to methods for determining an amount of seawater, an amount of aquifer water, and an amount of original reservoir water in a produced water sample using oxygen and hydrogen isotope ratios. An 18O/16 O ratio (δ18O) and a D/H ratio (δD) are measured for a seawater sample, an aquifer water sample, and an original reservoir water sample and are used to make a mixing model. δ18O and δD are measured in a produced water sample and the mixing model can be used to determine the amounts of each constituent in the produced water sample.
Seawater and/or aquifer water can be used for drilling and enhanced oil recovery operations. Reservoirs can contain seawater from power injectors, aquifer water from gravity injections and residual reservoir connate water. Distinguishing between produced waters and in-situ water formation can be difficult due to the injection of aquifer waters and/or seawater. Often, chemical analyses alone have not been successful in distinguishing water sources.
The disclosure relates to methods for determining an amount of seawater, an amount of aquifer water, and an amount of original reservoir water in a produced water sample using oxygen and hydrogen isotope ratios. An 18O/16 O ratio (δ18O) and a D/H ratio (δD) are measured for a seawater sample, an aquifer water sample, and an original reservoir water sample and are used to make a mixing model. δ18O and δD are measured in a produced water sample and the mixing model can be used to determine the amounts of each constituent (seawater, aquifer water and/or original reservoir water) in the produced water sample.
The methods of the disclosure can be used in various beneficial ways, either individually or in combination. As an example, the methods of the disclosure can enable the determination of the source of produced water and the effect of seawater and aquifer water on original in-situ waters. As another example, the methods of the disclosure can be used to make operational decisions enabling time and cost savings during drilling and production operations. As a further example, the methods of the disclosure can be used to identify breakthrough of injection water, monitor water flooding and predict potential scaling problems caused by mixing of incompatible waters. As an additional example, the methods of the disclosure can be used in reservoir health monitoring, water wettability estimations and assessing the success of farcing operations.
Alternatively or additionally, the methods of the disclosure can be used to analyze a mixture of waters with different salinity (e.g. low salinity aquifer water, moderate salinity seawater and/or high salinity reservoir water) which, in general, cannot be distinguished by chemical analysis. In some embodiments, the methods of the disclosure can be compatible with chemical reactions caused by mixing of incompatible waters and chemicals such as scale inhibitors, which may alter the composition of produced water.
Optionally, the methods of the disclosure employ the isotope composition of oxygen (18O/16O) and hydrogen (D/H) in original reservoir water, aquifer water and injected seawater as each water has distinct geochemistry. Oxygen and hydrogen isotopes can be measured with relatively high accuracy and are generally stable over production timescales.
In a first aspect the disclosure provides a method, including: measuring an 18O/16O ratio (δ18O) and an 2H/1H ratio (δD) for each of a seawater sample, an aquifer water sample, and an original reservoir water sample; measuring δ18O and a δD in a produced water sample; using the measured δ18O and δD for the aquifer water sample, the seawater sample and the original reservoir water sample to make a model; and using the model to determine an amount of seawater, an amount of aquifer water, and an amount of original reservoir water in the produced water sample. The produced water sample includes the seawater, the aquifer water, and/or the original reservoir water.
In some embodiments, the model is for a well or formation (t) and is made using:
V
Aδ18OXSeawater(t)+VBδ18Oy Aquifer water(t)+VCδ18OZReservoir water(t)=Vdδ18OP(t);
and
V
A
δD
XSeawater(t)+VBδDy Aquifer water(t)+VCδDZReservoir water(t)=VdδDP(t);
wherein:
In some embodiments: the model includes first, second and third endpoints; VA, VB and VC correspond to relative volume percentages of the seawater sample, the aquifer water sample, and the original reservoir water sample, respectively; the first endpoint corresponds to VA=1, VB=0 and VC=0; the second endpoint corresponds to VA=0; VB=1 and VC=0; and the third endpoint corresponds to VA=0, VB=0 and VC=1.
In some embodiments: the model includes first, second and third outer lines that connect the endpoints to define a triangle; the first outer line corresponds to VA being equal to zero while varying VB and VC; the second outer line corresponds to VB being equal to zero while varying VA and VC; and the third outer line corresponds to VC being equal to zero while varying VA and VB.
In some embodiments: the model includes grid lines that connect the outer lines; and each grid line corresponds to one member selected from the group consisting of VA, VB and VC being at a constant value between 0 and 1 and varying the other two members selected from the group consisting of VA, VB and VC.
In some embodiments: each endpoint corresponds to a mixture including only one member selected from the group consisting of the seawater sample, the aquifer water sample, and the original reservoir water sample; each outer line corresponds to a mixture including two members selected from the group consisting of the seawater sample, the aquifer water sample, and the original reservoir water sample; and each grid line corresponds to a mixture including the seawater sample, the aquifer water sample, and the original reservoir water sample.
In some embodiments: a produced water sample including only one member selected from the group consisting of the seawater sample, the aquifer water sample, and the original reservoir water sample plots close to its corresponding endpoint; a produced water sample including only two members selected from the group consisting of the seawater sample, the aquifer water sample, and the original reservoir water sample plots along the outer lines at a position corresponding to an amount of each of the two members; and a produced water sample including the seawater sample, the aquifer water sample, and the original reservoir water sample plots in at a position within the triangle corresponding to an amount of each of the seawater sample, the aquifer water sample, and the original reservoir water sample.
In some embodiments: the model includes endpoints that correspond to mixtures including only one member selected from the group consisting of the seawater sample, the aquifer water sample, and the original reservoir water sample; the model includes outer lines connecting the endpoints that correspond to mixtures including only two members selected from the group consisting of the seawater sample, the aquifer water sample, and the original reservoir water sample; the outer lines define a triangle; and the model includes grid lines that connect the outer lines that correspond to mixtures including the seawater sample, the aquifer water sample, and the original reservoir water sample.
In some embodiments: a produced water sample including only one member selected from the group consisting of the seawater sample, the aquifer water sample, and the original reservoir water sample plots close to the corresponding endpoint; a produced water sample including two members selected from the group consisting of the seawater sample, the aquifer water sample, and the original reservoir water sample plots along the outer lines at a position corresponding to an amount of each of the two members; and a produced water sample including the seawater sample, the aquifer water sample, and the original reservoir water sample plots at a position within the triangle corresponding to an amount of each of the seawater sample, the aquifer water sample, and the original reservoir water sample.
In some embodiments, the seawater has a δD of −5 to 30.
In some embodiments, the seawater has a δ18O of −5 to 7.
In some embodiments, the aquifer water has δD of −50 to −5.
In some embodiments, the aquifer water has a δ18O of −10 to 3.
In some embodiments, the original reservoir water has a δD of −40 to 8.
In some embodiments, the original reservoir water has a δ18O of −2 to 8.
In some embodiments, the produced water is from a production well in fluid communication with an underground reservoir.
In some embodiments, the produced water is from a flowback operation.
In some embodiments, the seawater is injected into the underground reservoir.
In some embodiments, the aquifer water is injected into the underground reservoir.
In some embodiments, an amount of 16O, an amount of 18O, an amount of 1H and/or an amount of 2H is measured using at least one of mass spectrometry and wavelength-scanned cavity ring-down spectroscopy.
Oxygen and hydrogen isotope ratios can be reported relative to Vienna Standard Mean Ocean Water (VSMOW) using the delta notation:
where 18O/16O and D/H (2H/1H) are atomic abundance ratios.
Mixing proportions of oxygen and hydrogen isotopes for a well or formation (t) with three mixing components and relative volume fractions VA, VB and VC yield the equations:
V
Aδ18OSeawater XSeawater(t)+VBδ18OAquifer water y Aquifer water(t)+VCδ18OReservoir water ZReservoir water(t)=VDδ18OP(t) (1)
and
V
A
δD
XSeawater(t)+VBδDy Aquifer water(t)+VCδDZReservoir water(t)=VDδDP(t) (2)
wherein: δ18OXSeawater, δ18Oy Aquifer water, and δ18OZReservoir water are the oxygen isotope ratios in in the seawater, aquifer water and original reservoir water, respectively; δDXSeawater, δDy Aquifer water, and δDZReservoir water are the hydrogen isotope ratios in in the seawater, aquifer water and original reservoir water, respectively; VA, VB and VC are the relative volume fractions of the seawater, aquifer water and original reservoir water respectively; VD is the mixing proportion used in the model; and δ18OP and δDP are the oxygen and hydrogen isotope ratios in the produced water sample. Typically, the value of VD is 1.
In the methods of the disclosure, the oxygen and hydrogen isotope ratios for seawater, aquifer water and original reservoir water are available, e.g., measured or otherwise determined or provided. Once obtained, the values can be used to construct the model. Such a model is depicted in
Generally, the model contains three endpoints, where each endpoint corresponds to one of the three components (the seawater, the aquifer water and the original reservoir water). In
The model additionally contains outer lines connecting the endpoints that correspond to mixtures of two of the components. The outer lines can be obtained by setting one of VA, VB and VC to 0 and varying the other two parameters. The model can further contain grid lines that connect the outer lines that correspond to mixtures of the three components. The grid lines can be obtained by holding one of VA, VB and VC at a constant value between 0 and 1 and varying the other two components.
Generally, a produced water sample containing only one of the components will plot close to the corresponding endpoint. A produced water sample containing only two of the components will plot along the outer lines at a position corresponding to an amount of each of the two components. A produced water sample containing all three of the components will plot in the center of the triangle at a position corresponding to an amount of each of the three components.
Generally, isotope concentrations in a water sample can be measured using any appropriate technique. As an example, in certain embodiments, the amount of 16O, 18O D (2H) and/or H (1H) is measured using a wavelength-scanned cavity ring-down spectroscopy (WS-CRDS). As another example, in certain embodiments, the amount of 16O, 18O, D and/or H can be measured using mass spectrometry.
In certain embodiments, the δ18O of the seawater, the aquifer water and/or the original reservoir water depends on the geographical location of the water. In certain embodiments, the seawater has a δ18O of at least −5 (e.g., at least −4, at least −3, at least −2, at least −1, at least 0, at least 1, at least 2, at least 3, at least 4, at least 5) and at most 7 (e.g., at most 6, at most 5, at most 4, at most 3, at most 2, at most 1, at most 0, at most −1, at most −2, at most −3). In certain embodiments, the aquifer water has a δ18O of at least −10 (e.g., at least −9, at least −8, at least −7, at least −6, at least −5) and at most −3 (e.g., at most −4, at most −5, at most −6, at most −7, at most −8). In certain embodiments, the original reservoir water has a δ18O of at least −2 (e.g., at least −1, at least 0, at least 1, at least 2, at least 3, at least 4, at least 5, at least 6) and at most 8 (e.g., at most 7, at most 6, at most 5, at most 4, at most 3, at most 2, at most 1, at most 0).
In some embodiments, the δD of the seawater, the aquifer water and/or the original reservoir water depends on the geographical location of the water. In some embodiments, the seawater has a δD of at least −5 (e.g., at least −4, at least −3, at least −2, at least −1, at least 0, at least 5, at least 10, at least 15, at least 25) and at most 30 (e.g., at most 29, at most 28, at most 27, at most 26, at most 25, at most 20, at most 15, at most 10, at most 5, at most 0). In some embodiments, the aquifer water has a δD of at least −50 (e.g., at least −49, at least −48, at least −47, at least −46, at least −45, at least −40, at least −35, at least −30, at least −25, at least −20, at least −15, at least −10) and at most −5 (e.g., at most −6, at most −7, at most −8, at most −9, at most −10, at most −15, at most −20, at most −25, at most −30, at most −35, at most −40, at most −45). In some embodiments, the original reservoir water has a δD of at least −40 (e.g., at least −39, at least −38, at least −37, at least −36, at least −35, at least −30, at least −25, at least −20, at least −15, at least −10, at least −5, at least 0, at least 5) and at most 8 (e.g., at most 7, at most 6, at most 5, at most 0, at most −5, at most −10, at most −15, at most −20, at most −25, at most −30, at most −35).
δ18O and δD were measured for samples of seawater, aquifer water and original reservoir water. δ18O and δD were measured using both wavelength-scanned cavity ring-down spectroscopy mass spectrometry.
δ18O and δD were measured using a Picarro L2130-i Laser Cavity Ring-Down Spectroscopy (CRDS) instrument. 5 μl of sample was injected into a vaporizer a total of 8 times. The temperature and pressure were kept constant at 110° C. and 3.5 psig inside the line to ensure total and instantaneous vaporization of the water without isotopic fractionation.
For mass spectrometry measurements, 5 ml aliquots of sample were placed in 25 ml glass vials, attached to a vacuum manifold and immersed in a water bath regulated to 18.0±0.2° C. The manifold was used to remove air and add 0.7-0.9 bars of hydrogen gas (for hydrogen isotope measurements) or carbon dioxide (for oxygen isotope measurements). Isotopic equilibration between hydrogen gas and water was achieved after 60-90 minutes with the aid of 2 mg of Pt catalyst (as described in Horita, 1988). Isotopic equilibration between carbon dioxide and water was achieved overnight without the use of a catalyst. The equilibrated gases were passed over acetone slush (−90-−96° C.) to remove water vapor. The gases were then introduced into a dual-inlet Finnigan-MAT Delta S stable isotope ratio mass spectrometer using automated valves. Water standards (USGS-48, USGS-47, USGS-48, USGS-50, PRIMARY VSMOW STANDARD, and three other lab made standards) were used to calibrate the isotope ratios and report them relative to standard mean ocean water (SMOW) using delta notation. Reproducibilities, estimated by pooling standard deviations for replicate analyses of standards were ±0.13‰ for δ18O and ±1.6‰ for δD.
The oxygen and hydrogen isotope ratios for the seawater, aquifer and original reservoir water samples measured are presented in table 1.
The values of VA, VB and VC were each set to 1 while the other two were set to 0 in equations 2 and 3 to provide the values for the endpoints of the model, as shown in table 2.
The outer lines and grid lines of the model were calculated by varying the values of VA, VB and VC in equations 3 and 4. Table 3 shows the values of δ18O and δD used to make the outer lines and the grid lines.
The mixing model is shown in
The mixing model generated in Example 1 was used to determine the composition of produced water samples. δ18O and δD of 128 produced water samples from five different wells in the same field and reservoir taken during different field operations were determined using the methods described in Example 1.
Produced water samples “A” plot very closed to the injected seawater source end-member, suggesting that the produced waters was composed almost entirely of injected seawater (90% injected seawater water).
Produced water samples “B” were composed of nearly 60% original reservoir water, less than 20% of injected seawater and slightly more than 20% fresh aquifer water source.
Produced water samples “BB” were divided into two clusters. Some samples contained more than 70% injected seawater. The other set of samples plotted in the middle of the model, indicating that they were distributed between the three sources. This suggests that the well had periods of seawater and fresh water injection into the reservoir causing samples to possess mixtures of all sources of water.
Produced water samples “C” also had mixtures of the water sources. The samples had about 50% fresh aquifer water source, less than 20% injected seawater source and 30% original reservoir water source. This suggests that the produced water samples were mostly aquifer water used during drilling operation. It also indicates that during the flowback operation, small quantities of original reservoir water flowed and mixed with the aquifer water.
Produced water samples “D” plotted near the aquifer water endpoint and along the outer line between aquifer water and original reservoir water, suggesting a mix of 20% original reservoir water and 80% injected seawater.
The mixing model was successfully applied to produced water to help predict and estimate the source of produced water and the effect of seawater and/or aquifer water on the original reservoir water. This information can help make quick field operation decisions, thereby saving time and reducing costs in drilling and production operations.