CN109884109A - An evaluation method for shale pore water adsorption, free amount and distribution - Google Patents

An evaluation method for shale pore water adsorption, free amount and distribution Download PDF

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CN109884109A
CN109884109A CN201910219913.5A CN201910219913A CN109884109A CN 109884109 A CN109884109 A CN 109884109A CN 201910219913 A CN201910219913 A CN 201910219913A CN 109884109 A CN109884109 A CN 109884109A
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water
value
shale
adsorption
free
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李俊乾
李文镖
卢双舫
张鹏飞
王思远
冯文俊
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China University of Petroleum East China
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Abstract

本发明涉及页岩孔隙水赋存及其定量评价技术领域,公开了一种页岩孔隙水吸附量、游离量及其分布的评价方法,提出了描述可动水量随离心压力差的数学表达式、吸附比例方程和液体状态方程,在此基础上,联立核磁共振横向驰豫时间T2表达式,建立了基于核磁共振T2谱的页岩基质孔隙内液态水吸附量、游离量及其分布的评价方法。采用核磁共振T2谱可快速、无损的检测页岩吸附水和游离水含量及其分布,操作简便易行,准确性高,可操作性、实用性较强,便于地质推广应用。

The invention relates to the technical field of shale pore water occurrence and quantitative evaluation, discloses an evaluation method of shale pore water adsorption amount, free amount and distribution thereof, and proposes a mathematical expression describing movable water amount with centrifugal pressure difference , adsorption proportional equation and liquid state equation. On this basis, the NMR transverse relaxation time T 2 expression was simultaneously established to establish the liquid water adsorption amount, free amount and its value in the pores of shale matrix based on NMR T 2 spectrum. Methods of evaluating distributions. Using nuclear magnetic resonance T 2 spectrum can quickly and non-destructively detect the content and distribution of shale adsorbed water and free water.

Description

A kind of shale hole water adsorption amount, free amount and its evaluation method of distribution
Technical field
The present invention relates to shale pore water preservation and its quantitative assessment technical fields, and in particular to a kind of shale pore water suction Attached amount, free amount and its evaluation method of distribution.
Background technique
Shale gas mainly the free gas with preservation in intrinsic fracture and matrix hole-crack and is adsorbed in organic matter/clay Based on the adsorbed gas of particle surface, wherein adsorbed gas can account for 30-60%;Containing a small amount of solution gas, can be ignored.Adsorbed gas and free gas As the material base of shale gas exploitation, their content in situ and its migration (flowing) process is by the shale reservoir property of water-bearing Significantly affect, and then affect shale gas yield, constrain the high-efficiency mining of shale gas.Production practices also show initial aqueous Saturate shale air content is low, well yield is low (such as China Zhaotong block);The low shale gassiness of initial water saturation Amount is high, there are obvious superpressure, well yield height (such as China Changning-Weiyuan, rich and smooth-Yongchuan block).Therefore, the aqueous situation of shale It is a key factor for influencing shale gas high-efficiency mining.
Before shale gas exploitation, need to be transformed reservoir the exploitation for being just able to achieve and having an economic benefit.North America at present The remodeling method generally used with the country is horizontal well drilling completion combination large hydraulic fracturing.It is domestic generally to use oil base drilling well Liquid, but aqueous fracturing fluid is used in fracturing reform, the scale of " thousand side's sand of all places water " is needed during entire reservoir reconstruction, and The row of returning leads very low.A large amount of fracturing fluid (water content > 90%) is stranded in stratum.Due to the characteristic of shale Abnormal low water saturation Shale hole capillary imbibition power is considerably increased, after fracturing fluid touches rock surface, the water self-priming under capillary force immediately Into shale matrix, leads to water saturation increase in shale near nearly well band or fracture surface, forms water phase blocking in duct, It is serious to reduce gas phase permeability.Therefore, in addition to the influence of shale reservoir connate water, the injection of outside fluid exacerbates shale reservoir Aqueous complexity and its influence degree to shale gas exploitation.
Although hydraulic fracturing transformation significantly extends, linked up shale reservoir Fracture System, matrix pores are involved journey Degree is still very limited, and therefore, can a large amount of residual gas effectively be employed in shale matrix pores, will greatly be controlled by matrix The regularity of distribution of water in hole.But it is current mainly to pass through initial water saturation, irreducible water saturation, movable water saturation both at home and abroad The macroparameters such as degree evaluate the shale property of water-bearing.In view of the complexity, multiple dimensioned property and strong heterogeneity of shale microstructure, Matrix pores water adsorption amount, free amount and its micro Distribution are evaluated, realistic meaning is had more for shale gas high-efficiency mining.It is domestic Outer scholar has carried out many pilot studies for the adsorption/desorption that steam condition (relative pressure) is lauched, and then evaluates water and exist The intrapore regularity of distribution of shale/mineral;And for the regularity of distribution of the liquid water in hole in shale formation, due to lacking reason By evaluation model, corresponding experimental study is also very deficient.
Shale pore water, which can be divided into, adsorbs water and free water, and hardly flowable on absorption water theory, free water is theoretically It is flowable.But free water is influenced by shale pore throat microstructure, in external condition (such as centrifugal force, displacement pressure, rock matrix Stress) under flowable part be moveable water;Not flowable part is hollow billet irreducible water.Hollow billet irreducible water is with external condition Change, moveable water can be converted into.Therefore the movable water of theoretical maximum is equal to free water content.The present invention considers shale matrix pores The occurrence status of interior liquid water and the flowability of different conditions pore water are based on nuclear magnetic resonance T2Spectrum, proposes a kind of shale Liquid water adsorption amount, free amount and its evaluation method of distribution in matrix pores.
Summary of the invention
Based on problem above, the present invention provides a kind of shale hole water adsorption amount, free amount and its evaluation method of distribution, It establishes based on nuclear magnetic resonance T2Liquid water adsorption amount, free amount and its evaluation method of distribution in the shale matrix pores of spectrum, Easy to operation, accuracy is high, and operability, practicability are stronger, promotes and applies convenient for geology.
In order to solve the above technical problems, the present invention provides a kind of shale hole water adsorption amount, free amount and its distributions Evaluation method includes the following steps:
Step 1: shale column rock core is dried, measurement shale core quality in the dry state and page The NMR signal of rock rock core;
Step 2: under the conditions of certain temperature, by the shale core saturated water under drying regime, shale core saturation is tested Water QtWith the NMR signal of shale core under saturated-water phase;
Step 3: watery according to being saturated in the NMR signal of shale core under drying regime in step 1 and step 2 The NMR signal of shale core under state, by going substrate inverting to obtain the nuclear magnetic resonance T of shale core pore water2Spectrum;Page Nuclear magnetic resonance spin spinrelaxation T in rock rock core hole2Calculation formula are as follows:
Wherein, T2For spin spinrelaxation, ms;ρ is surface relaxivity, nm/ms;SwFor the specific surface area containing water voids, Vw For the volume containing water voids;
Step 4: test is centrifuged in the shale core of saturated water in step 2, it is poor to obtain different centrifugal pressures Movable water content Q under △ P-conditionm, establish the functional relation between movable water and centrifugal pressure difference:
Wherein, QmFor movable water, mg/g;QfFor water of dissociating, i.e., maximum movable water, mg/g;△ P is centrifugal pressure Difference, MPa;△PLCorresponding centrifugal pressure is poor when reaching the half of maximum movable water for movable water, MPa;
The data that centrifuge test obtains are substituted into functional relation and the progress between movable water and centrifugal pressure difference Fitting, obtains free water content Qf;According to absorption water content, free water content, the ratio of adsorption r of centrifuge test is calculateda:
Wherein, water content Q is adsorbedaThen pass through formula Qa=Qt-QfIt calculates;
Step 5: using the specific surface area S containing water voids of low temperature nitrogen adsorption/desorption method test shale corew, use The volume V containing water voids of weight in wet base method and low temperature nitrogen adsorption/desorption method integration test shale corew;For the page of saturated water Rock rock core, in absorption water account for the mass ratio of total Water and may be expressed as:
Wherein, H is average adsorption thickness, nm;ρ1And ρ2It is absorption water and free water averag density, g/cm respectively3
Simultaneous formula (3) and (4) can must describe the equation of state for liquids of liquid occurrence status:
Wherein, τ is correction coefficient, for parallel planar hole, value 1, Vw/SwWith Qf/QaBetween it is in a linear relationship when, τ Close to 1;
Step 6: it is based on nuclear magnetic resonance T2Spectrum, simultaneous equation of state for liquids calculate each T2Corresponding absorption water contains when value Amount and free water content, and absorption water saturation, free water saturation are respectively with T2The distribution of value;Calculation process are as follows:
Simultaneous formula (1) and (4) can obtain:
Based on nuclear magnetic resonance T2Spectrum, in conjunction with formula (6), can calculate nuclear magnetic resonance T2Each T in spectrum2It is worth corresponding absorption Ratio indicates are as follows:
Wherein, T2iFor nuclear magnetic resonance T2Compose upper i-th of T2Value;raiFor T2iIt is worth corresponding ratio of adsorption, score;0<rai≤ 1, as calculated value raiWhen > 1, r is takenai=1;
Nuclear magnetic resonance T2Each T in spectrum2It is worth corresponding absorption water signal amplitude (Mai) are as follows:
Mai=Mirai (8)
Wherein, MiFor i-th of T2It is worth corresponding resultant signal amplitude (mass normalisation, similarly hereinafter);MaiFor i-th of T2Value corresponds to Absorption water signal amplitude (mass normalisation, similarly hereinafter);
Based on formula (8), the absorption water that can calculate shale core accounts for the mass ratio of total Water:
Wherein, ra(T2) it is based on nuclear magnetic resonance T2The mass ratio that absorption water in the shale core calculated accounts for total Water is composed, point Number;MtiFor nuclear magnetic resonance T2Compose upper i-th of T2It is worth corresponding absorption water signal amplitude;N is nuclear magnetic resonance T2Compose inverting points;
Determine best surface relaxation rate, constraint equation are as follows:
δ=| ra(T2)-ra| (10)
δ value when different surfaces Relaxivity values is analyzed, when the suction of the nuclear magnetic resonance ratio of adsorption calculated and centrifugal process test When the absolute value δ of attached proportional difference is equal to 0 or infinitely approaches 0, best surface Relaxivity values can be obtained.
Best Relaxivity values are substituted into formula (8), each T can be obtained2It is worth corresponding absorption water signal amplitude (Mai).Meanwhile Free water signal amplitude (M can be obtainedfi), are as follows:
Mfi=Mti-Mai (11)
Wherein, MfiFor i-th of T2It is worth corresponding absorption water signal amplitude;
According to the linear relationship between signal amplitude and water content, each T can be calculated2When value corresponding absorption water content and Free water content, and with T2The distribution of value.Relationship between signal amplitude and water content may be expressed as:
Y=kx (12)
Wherein, y represents the water content of unit mass shale core, mg/g;X represents the signal width of unit mass shale core Degree;K is fitting coefficient;
Then adsorb water content and distribution calculation formula are as follows:
Qai=kMai (13)
Wherein, QaiFor i-th of T2It is worth corresponding absorption water content, mg/g;
Free water content and distribution calculation formula are as follows:
Qfi=kMfi (14)
Wherein, QfiFor i-th of T2It is worth corresponding free water content, mg/g;
Water saturation is adsorbed with T2The distribution calculation formula of value are as follows:
Wherein, φaiFor i-th of T2It is worth corresponding absorption water saturation, %;
Water saturation of dissociating is with T2The distribution calculation formula of value are as follows:
φfi=1- φai (16)
Wherein, φfiFor i-th of T2It is worth corresponding absorption water saturation, %.
Further, shale core is saturated 24~48h of distilled water at 20 °C in step 1.
Further, shale core drying condition is dried for 24 hours under the conditions of being 110 DEG C in step 1.
Compared with prior art, the beneficial effects of the present invention are: based on shale core pore water occurrence status and flowable Property feature, in conjunction with nuclear magnetic resonance T2Spectral structure, establish shale matrix pores water adsorption amount under laboratory condition, free amount and Its evaluation method being distributed, easy to operation, accuracy is high, and operability, practicability are stronger, promotes and applies convenient for geology.
Detailed description of the invention
Fig. 1 is the relational graph of movable water and centrifugal pressure difference in embodiment 2;
Fig. 2 is V in embodiment 2w/SwWith Qf/QaBetween relational graph;
Fig. 3 be embodiment 2 in nuclear magnetic resonance calculate with centrifuge test obtain ratio of adsorption difference absolute value δ with The variation diagram of Surface Relaxation rate;
Fig. 4 be embodiment 2 in rock core S1 absorption water and free water content with T2The distribution map of value;
Fig. 5 be embodiment 2 in rock core S2 absorption water and free water content with T2The distribution map of value;
Fig. 6 be embodiment 2 in rock core S3 absorption water and free water content with T2The distribution map of value;
Fig. 7 be embodiment 2 in rock core S4 absorption water and free water content with T2The distribution map of value;
Fig. 8 be embodiment 2 in rock core S5 absorption water and free water content with T2The distribution map of value;
Fig. 9 be embodiment 2 in rock core S6 absorption water and free water content with T2The distribution map of value;
Figure 10 is shale water content and signal amplitude relational graph in embodiment 2;
Figure 11 is the absorption water of rock core S1 in embodiment 2 and free water saturation with T2The distribution map of value;
Figure 12 is the absorption water of rock core S2 in embodiment 2 and free water saturation with T2The distribution map of value;
Figure 13 is the absorption water of rock core S3 in embodiment 2 and free water saturation with T2The distribution map of value;
Figure 14 is the absorption water of rock core S4 in embodiment 2 and free water saturation with T2The distribution map of value;
Figure 15 is the absorption water of rock core S5 in embodiment 2 and free water saturation with T2The distribution map of value;
Figure 16 is the absorption water of rock core S6 in embodiment 2 and free water saturation with T2The distribution map of value.
Specific embodiment
To make the objectives, technical solutions, and advantages of the present invention clearer, below with reference to embodiment and attached drawing, to this Invention is described in further detail, and exemplary embodiment of the invention and its explanation for explaining only the invention, are not made For limitation of the invention.
Embodiment 1:
A kind of shale hole water adsorption amount, free amount and its evaluation method of distribution, include the following steps:
Step 1: shale column rock core is dried, measurement shale core quality in the dry state and page The NMR signal of rock rock core;
Step 2: under the conditions of certain temperature, by the shale core saturated water under drying regime, shale core saturation is tested Water QtWith the NMR signal of shale core under saturated-water phase;
Step 3: watery according to being saturated in the NMR signal of shale core under drying regime in step 1 and step 2 The NMR signal of shale core under state, by going substrate inverting to obtain the nuclear magnetic resonance T of shale core pore water2Spectrum;Page Nuclear magnetic resonance spin spinrelaxation T in rock rock core hole2Calculation formula are as follows:
Wherein, T2For spin spinrelaxation, ms;ρ is surface relaxivity, nm/ms;SwFor the specific surface area containing water voids, Vw For the volume containing water voids;
Step 4: test is centrifuged in the shale core of saturated water in step 2, it is poor to obtain different centrifugal pressures Movable water content Q under △ P-conditionm, establish the functional relation between movable water and centrifugal pressure difference:
Wherein, QmFor movable water, mg/g;QfFor water of dissociating, i.e., maximum movable water, mg/g;△ P is centrifugal pressure Difference, MPa;△PLCorresponding centrifugal pressure is poor when reaching the half of maximum movable water for movable water, MPa;
The data that centrifuge test obtains are substituted into functional relation and the progress between movable water and centrifugal pressure difference Fitting, obtains free water content Qf;According to absorption water content, free water content, the ratio of adsorption r of centrifuge test is calculateda:
Wherein, water content Q is adsorbedaThen pass through formula Qa=Qt-QfIt calculates;
Step 5: using the specific surface area S containing water voids of low temperature nitrogen adsorption/desorption method test shale corew, use The volume V containing water voids of weight in wet base method and low temperature nitrogen adsorption/desorption method integration test shale corew;For the page of saturated water Rock rock core, in absorption water account for the mass ratio of total Water and may be expressed as:
Wherein, H is average adsorption thickness, nm;ρ1And ρ2It is absorption water and free water averag density, g/cm respectively3
Simultaneous formula (3) and (4) can must describe the equation of state for liquids of liquid occurrence status:
Wherein, τ is correction coefficient, for parallel planar hole, value 1, Vw/SwWith Qf/QaBetween it is in a linear relationship when, τ Close to 1;
Step 6: it is based on nuclear magnetic resonance T2Spectrum, simultaneous equation of state for liquids calculate each T2Corresponding absorption water contains when value Amount and free water content, and absorption water saturation, free water saturation are respectively with T2The distribution of value;Calculation process are as follows:
Simultaneous formula (1) and (4) can obtain:
Based on nuclear magnetic resonance T2Spectrum, in conjunction with formula (6), can calculate nuclear magnetic resonance T2Each T in spectrum2It is worth corresponding absorption Ratio indicates are as follows:
Wherein, T2iFor nuclear magnetic resonance T2Compose upper i-th of T2Value;raiFor T2iIt is worth corresponding ratio of adsorption, score;0<rai≤ 1, as calculated value raiWhen > 1, r is takenai=1;
Nuclear magnetic resonance T2Each T in spectrum2It is worth corresponding absorption water signal amplitude (Mai) are as follows:
Mai=Mirai (8)
Wherein, MiFor i-th of T2It is worth corresponding resultant signal amplitude (mass normalisation, similarly hereinafter);MaiFor i-th of T2Value corresponds to Absorption water signal amplitude (mass normalisation, similarly hereinafter);
Based on formula (8), the absorption water that can calculate shale core accounts for the mass ratio of total Water:
Wherein, ra(T2) it is based on nuclear magnetic resonance T2The mass ratio that absorption water in the shale core calculated accounts for total Water is composed, point Number;MtiFor nuclear magnetic resonance T2Compose upper i-th of T2It is worth corresponding absorption water signal amplitude;N is nuclear magnetic resonance T2Compose inverting points;
Determine best surface relaxation rate, constraint equation are as follows:
δ=| ra(T2)-ra| (10)
δ value when different surfaces Relaxivity values is analyzed, when the suction of the nuclear magnetic resonance ratio of adsorption calculated and centrifugal process test When the absolute value δ of attached proportional difference is equal to 0 or infinitely approaches 0, best surface Relaxivity values can be obtained.
Best Relaxivity values are substituted into formula (8), each T can be obtained2It is worth corresponding absorption water signal amplitude (Mai).Meanwhile Free water signal amplitude (M can be obtainedfi), are as follows:
Mfi=Mti-Mai (11)
Wherein, MfiFor i-th of T2It is worth corresponding absorption water signal amplitude;
According to the linear relationship between signal amplitude and water content, each T can be calculated2When value corresponding absorption water content and Free water content, and with T2The distribution of value.Relationship between signal amplitude and water content may be expressed as:
Y=kx (12)
Wherein, y represents the water content of unit mass shale core, mg/g;X represents the signal width of unit mass shale core Degree;K is fitting coefficient;
Then adsorb water content and distribution calculation formula are as follows:
Qai=kMai (13)
Wherein, QaiFor i-th of T2It is worth corresponding absorption water content, mg/g;
Free water content and distribution calculation formula are as follows:
Qfi=kMfi (14)
Wherein, QfiFor i-th of T2It is worth corresponding free water content, mg/g;
Water saturation is adsorbed with T2The distribution calculation formula of value are as follows:
Wherein, φaiFor i-th of T2It is worth corresponding absorption water saturation, %;
Water saturation of dissociating is with T2The distribution calculation formula of value are as follows:
φfi=1- φai (16)
Wherein, φfiFor i-th of T2It is worth corresponding absorption water saturation, %.
Embodiment 2:
On the basis of embodiment 1, by taking five peak group of south China marine facies-Longma small stream group, 6 shale column rock cores as an example:
Step 1: carrying out that shale core is dry for 24 hours under the conditions of 110 DEG C first, test dry shale core quality and The NMR signal of shale core;
Step 2: being saturated distilled water for 24 hours at 20 °C, and the quality of test saturation shale core calculates saturated water amount For Qt(being shown in Table 1);Meanwhile testing the NMR signal of saturation shale core;
Step 3: watery according to being saturated in the NMR signal of shale core under drying regime in step 1 and step 2 The NMR signal of shale core under state, by going substrate inverting to obtain the nuclear magnetic resonance T of shale core pore water2Spectrum;
Step 4: being directed to 6 shale cores, carries out the centrifuge separation test under different centrifugal pressure differences respectively, uses Formula (2) fitting centrifugation data are as shown in Figure 1, obtain free water content QfIt is shown in Table 1;According to formula Qa=Qt-QfCalculate absorption water Content QaIt is shown in Table 1;
Step 5: low temperature nitrogen adsorption/desorption and weight in wet base method are used, the volume V containing water voids of shale core is testedwWith Specific surface area S containing water voidsw
Step 6: it is based on nuclear magnetic resonance T2Spectrum, simultaneous equation of state for liquids calculate each T2Corresponding absorption water contains when value Amount and free water content, and absorption water saturation, free water saturation are respectively with T2The distribution of value, specific calculation process is such as Under:
According to formula (5), V is establishedw/SwWith Qf/QaBetween linear functional relation as shown in Fig. 2, may be expressed as: y= 0.9972x+0.6475;
According to the V of acquisitionw/SwWith Qf/QaBetween linear functional relation, in conjunction with free water density p under the conditions of 20 DEG C2For 0.9982g/cm3, the equal density p of adsorption levels can be calculated1For 1.5402g/cm3, average adsorption thickness H is 0.6475nm;
In conjunction with nuclear magnetic resonance T2Spectrum substitutes into formula (7)~(9) using different Surface Relaxation rate values;When calculated result is full It is best surface relaxation rate ρ (being shown in Table 1) when δ value in sufficient formula (10) is equal to 0.
1 shale core water content centrifuge test of table and nuclear magnetic resonance spectroscopy tables of data
The absolute value (i.e. δ value) for the ratio of adsorption difference that the ratio of adsorption and centrifuge test that nuclear magnetic resonance calculates obtain Variation tendency with different surfaces relaxation rate is as shown in Figure 3;
Obtained best Relaxivity values are substituted into formula (7) and formula (11), absorption water signal amplitude can be calculated separately out, dissociated Water signal amplitude and with T2The distribution of value is as shown in Fig. 4~9;
The relationship established between signal amplitude and water content is as shown in Figure 10, may be expressed as: y=0.0293x;
According to the relationship between signal amplitude and water content, using formula (13) and (14), calculate separately out absorption water and Free water content and with T2The distribution of value is as shown in Fig. 4~9;
According to formula (15), absorption water saturation is calculated with T2Figure 11~16 are shown in the distribution of value;
According to formula (16), free water saturation is calculated with T2Figure 11~16 are shown in the distribution of value.
It as above is the embodiment of the present invention.Design parameter in above-described embodiment and embodiment is merely to understand table Invention verification process is stated, the scope of patent protection being not intended to limit the invention, scope of patent protection of the invention is still with it It is all to change with equivalent structure made by specification and accompanying drawing content of the invention subject to claims, it should all similarly wrap Containing within the scope of the present invention.

Claims (3)

1.一种页岩孔隙水吸附量、游离量及其分布的评价方法,其特征在于,包括如下步骤:1. an evaluation method of shale pore water adsorption capacity, free amount and distribution thereof, is characterized in that, comprises the steps: 步骤一:将页岩柱状岩心进行干燥处理,测量页岩岩心在干燥状态下的质量和页岩岩心的核磁共振信号;Step 1: Dry the shale columnar core, measure the quality of the shale core in the dry state and the nuclear magnetic resonance signal of the shale core; 步骤二:在一定温度条件下,将干燥状态下的页岩岩心饱和水,测试页岩岩心饱和水量Qt和饱和水状态下页岩岩心的核磁共振信号;Step 2: Under a certain temperature condition, the shale core in the dry state is saturated with water, and the saturated water quantity Qt of the shale core and the nuclear magnetic resonance signal of the shale core in the saturated water state are tested; 步骤三:根据步骤一中干燥状态下页岩岩心的核磁共振信号和步骤二中饱和水状态下页岩岩心的核磁共振信号,通过去基底反演获得页岩岩心孔隙水的核磁共振T2谱;页岩岩心孔隙中核磁共振横向驰豫时间T2的计算公式为:Step 3: According to the nuclear magnetic resonance signal of the shale core in the dry state in the first step and the nuclear magnetic resonance signal of the shale core in the saturated water state in the second step, obtain the nuclear magnetic resonance T 2 spectrum of the pore water of the shale core through debasing inversion ; The formula for calculating the NMR transverse relaxation time T 2 in the pores of the shale core is: 其中,T2为横向驰豫时间,ms;ρ为表面弛豫率,nm/ms;Sw为含水孔隙的比表面积,Vw为含水孔隙的体积;Among them, T 2 is the transverse relaxation time, ms; ρ is the surface relaxation rate, nm/ms; S w is the specific surface area of the water-containing pores, and V w is the volume of the water-containing pores; 步骤四:将步骤二中饱和水的页岩岩心进行离心分离试验,获得不同离心压力差△P条件下的可动水含量Qm,建立可动水量与离心压力差之间的函数关系:Step 4: Perform the centrifugal separation test on the water-saturated shale core in Step 2 to obtain the movable water content Q m under the conditions of different centrifugal pressure differences ΔP, and establish the functional relationship between the movable water amount and the centrifugal pressure difference: 其中,Qm为可动水量,mg/g;Qf为游离水量,即最大可动水量,mg/g;△P为离心压力差,MPa;△PL为可动水量达到最大可动水量的一半时对应的离心压力差,MPa;Among them, Q m is the movable water volume, mg/g; Q f is the free water volume, that is, the maximum movable water volume, mg/g; △P is the centrifugal pressure difference, MPa; △P L is the maximum movable water volume The centrifugal pressure difference corresponding to half of , MPa; 将离心分离试验获得的数据代入可动水量与离心压力差之间的函数关系并进行拟合,得到游离水含量Qf;根据吸附水含量、游离水含量,计算离心分离试验的吸附比例raSubstitute the data obtained in the centrifugal separation test into the functional relationship between the movable water amount and the centrifugal pressure difference and perform fitting to obtain the free water content Q f ; according to the adsorption water content and free water content, calculate the adsorption ratio ra of the centrifugal separation test : 其中,吸附水含量Qa则通过公式Qa=Qt-Qf计算;Among them, the adsorbed water content Q a is calculated by the formula Q a =Q t -Q f ; 步骤五:采用低温氮气吸附/解吸法测试页岩岩心的含水孔隙的比表面积Sw,采用湿重法和低温氮气吸附/解吸法测试页岩岩心的含水孔隙的体积Vw;对于饱和水的页岩岩心,其内的吸附水占总水量的质量比可表示为:Step 5: The specific surface area S w of the water-containing pores of the shale core is tested by the low-temperature nitrogen adsorption/desorption method, and the volume Vw of the water-containing pores of the shale core is tested by the wet weight method and the low-temperature nitrogen adsorption/desorption method; The mass ratio of the adsorbed water in the shale core to the total water can be expressed as: 其中,H是平均吸附厚度,nm;ρ1和ρ2分别是吸附水和游离水平均密度,g/cm3where H is the average adsorption thickness, nm; ρ 1 and ρ 2 are the average density of adsorbed water and free water, respectively, g/cm 3 ; 联立公式(3)和(4),可得描述液体赋存状态的液体状态方程:By combining formulas (3) and (4), the liquid state equation describing the liquid state can be obtained: 其中,τ是校正系数,对于平行板状孔,其值为1,Vw/Sw与Qf/Qa之间呈线性关系时,τ接近于1;Among them, τ is the correction coefficient. For parallel plate holes, its value is 1. When there is a linear relationship between V w /S w and Q f /Q a , τ is close to 1; 步骤六:基于核磁共振T2谱,联立液体状态方程,计算每个T2值时对应的吸附水含量和游离水含量,以及吸附水饱和度、游离水饱和度分别随T2值的分布;计算流程为:Step 6: Based on the nuclear magnetic resonance T 2 spectrum and the equation of state of the liquid simultaneously, calculate the corresponding adsorbed water content and free water content at each T 2 value, as well as the distribution of adsorbed water saturation and free water saturation with T 2 value respectively ; the calculation process is: 联立公式(1)和(4)可得:Simultaneous formulas (1) and (4) can be obtained: 基于核磁共振T2谱,结合公式(6),可计算出核磁共振T2谱上每个T2值对应的吸附比例,表示为:Based on the NMR T 2 spectrum, combined with formula (6), the adsorption ratio corresponding to each T 2 value on the NMR T 2 spectrum can be calculated, which is expressed as: 其中,T2i为核磁共振T2谱上第i个T2值;rai为T2i值对应的吸附比例,分数;0<rai≤1,当计算值rai>1时,取rai=1;Among them, T 2i is the i-th T 2 value on the nuclear magnetic resonance T 2 spectrum; ra ai is the adsorption ratio corresponding to the T 2i value, fraction; 0<r ai ≤1, when the calculated value rai >1, take rai =1; 核磁共振T2谱上每个T2值对应的吸附水信号幅度(Mai)为:The adsorbed water signal amplitude (M ai ) corresponding to each T 2 value on the NMR T 2 spectrum is: Mai=Mirai (8)M ai =M i r ai (8) 其中,Mi为第i个T2值对应的总信号幅度(质量归一化,下同);Mai为第i个T2值对应的吸附水信号幅度(质量归一化,下同);Among them, M i is the total signal amplitude (mass normalization, the same below) corresponding to the ith T 2 value; M ai is the adsorbed water signal amplitude (mass normalization, the same below) corresponding to the ith T 2 value ; 基于公式(8),可计算页岩岩心的吸附水占总水量的质量比:Based on formula (8), the mass ratio of the adsorbed water in the shale core to the total water can be calculated: 其中,ra(T2)是基于核磁共振T2谱计算的页岩岩心中吸附水占总水量的质量比,分数;Mti为核磁共振T2谱上第i个T2值对应的吸附水信号幅度;n为核磁共振T2谱反演点数;Among them, ra (T 2 ) is the mass ratio, fraction, of the adsorbed water in the shale core to the total water calculated based on the NMR T 2 spectrum; M ti is the adsorption corresponding to the i-th T 2 value on the NMR T 2 spectrum Amplitude of water signal; n is the number of inversion points of nuclear magnetic resonance T 2 spectrum; 确定最佳表面驰豫率,其约束方程为:To determine the optimal surface relaxation rate, the constraint equation is: δ=|ra(T2)-ra| (10)δ=|r a (T 2 )-r a | (10) 分析不同表面驰豫率值时的δ值,当核磁共振计算的吸附比例与离心法测试的吸附比例差值的绝对值δ等于0或无限逼近0时,可得最佳表面驰豫率值。Analyzing the δ value of different surface relaxation rate values, when the absolute value δ of the difference between the adsorption ratio calculated by NMR and the adsorption ratio measured by the centrifugal method is equal to 0 or infinitely approaching 0, the optimal surface relaxation rate value can be obtained. 将最佳驰豫率值代入公式(8),可得每个T2值对应的吸附水信号幅度(Mai)。同时,可得游离水信号幅度(Mfi),为:Substituting the optimal value of relaxation rate into formula (8), the amplitude (M ai ) of the adsorbed water signal corresponding to each T 2 value can be obtained. At the same time, the free water signal amplitude (M fi ) can be obtained as: Mfi=Mti-Mai (11)M fi =M ti -M ai (11) 其中,Mfi为第i个T2值对应的吸附水信号幅度;Among them, M fi is the signal amplitude of adsorbed water corresponding to the i-th T 2 value; 根据信号幅度与含水量之间的线性关系,可计算每个T2值时对应的吸附水含量和游离水含量,以及随T2值的分布。信号幅度与含水量之间的关系可表示为:Based on the linear relationship between the signal amplitude and the water content, the corresponding adsorbed water content and free water content at each T 2 value can be calculated, as well as the distribution with the T 2 value. The relationship between signal amplitude and water content can be expressed as: y=kx (12)y=kx (12) 其中,y代表单位质量页岩岩心的含水量,mg/g;x代表单位质量页岩岩心的信号幅度;k为拟合系数;Among them, y represents the water content of the shale core per unit mass, mg/g; x represents the signal amplitude of the shale core per unit mass; k is the fitting coefficient; 则吸附水含量及分布计算公式为:Then the calculation formula of adsorbed water content and distribution is: Qai=kMai (13)Q ai = kM ai (13) 其中,Qai为第i个T2值对应的吸附水含量,mg/g;Wherein, Q ai is the adsorbed water content corresponding to the i-th T 2 value, mg/g; 游离水含量及分布计算公式为:The calculation formula of free water content and distribution is: Qfi=kMfi (14)Q fi =kM fi (14) 其中,Qfi为第i个T2值对应的游离水含量,mg/g;Wherein, Q fi is the free water content corresponding to the i-th T 2 value, mg/g; 吸附水饱和度随T2值的分布计算公式为:The calculation formula for the distribution of adsorbed water saturation with T 2 value is: 其中,φai为第i个T2值对应的吸附水饱和度,%;Among them, φ ai is the adsorption water saturation corresponding to the i-th T 2 value, %; 游离水饱和度随T2值的分布计算公式为:The calculation formula for the distribution of free water saturation with T 2 value is: φfi=1-φai (16)φ fi = 1-φ ai (16) 其中,φfi为第i个T2值对应的吸附水饱和度,%。Among them, φ fi is the adsorption water saturation corresponding to the i-th T 2 value, %. 2.根据权利要求1所述的页岩孔隙水吸附量、游离量及其分布的评价方法,其特征在于,步骤一中页岩岩心在20℃条件下饱和蒸馏水24~48h。2. The method for evaluating shale pore water adsorption capacity, free amount and distribution thereof according to claim 1, characterized in that in step 1, the shale core is saturated with distilled water at 20°C for 24-48 hours. 3.根据权利要求1-5任意一项所述的页岩孔隙水吸附量、游离量及其分布的评价方法,其特征在于,步骤一中页岩岩心干燥条件为110℃条件下进行干燥24h。3. The method for evaluating shale pore water adsorption amount, free amount and distribution thereof according to any one of claims 1 to 5, characterized in that in step 1, the drying conditions for shale cores are drying at 110°C for 24h .
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