METHOD FOR INTELLIGENTLY DETERMINING HYDRATE DRILLING AND PRODUCTION RISKS BASED ON FUZZY JUDGMENT
20200240243 ยท 2020-07-30
Inventors
- Haitao LI (Chengdu City, CN)
- Na WEI (Chengdu City, CN)
- JINZHOU ZHAO (CHENGDU CITY, CN)
- Luling LI (Chengdu City, CN)
- Zhenjun CUI (Chengdu City, CN)
- Lin JIANG (Chengdu City, CN)
- Wantong SUN (Chengdu City, CN)
- Luyue YANG (Chengdu City, CN)
- Xi LI (Chengdu City, CN)
- Yinghe HONG (Chengdu City, CN)
- Yu QIAO (Chengdu City, CN)
Cpc classification
E21B49/00
FIXED CONSTRUCTIONS
E21B2200/22
FIXED CONSTRUCTIONS
E21B41/0099
FIXED CONSTRUCTIONS
E21B49/08
FIXED CONSTRUCTIONS
E21B44/00
FIXED CONSTRUCTIONS
International classification
E21B41/00
FIXED CONSTRUCTIONS
E21B49/08
FIXED CONSTRUCTIONS
E21B49/00
FIXED CONSTRUCTIONS
Abstract
A method for intelligently determining hydrate drilling and production risks based on fuzzy judgment. First classifying monitoring parameters in a hydrate drilling and production process into layers from top to bottom: a target layer, a primary evaluation factor layer and a secondary evaluation factor layer; then calculating relative weight values of each primary evaluation factor and each secondary evaluation factor contained therein; then connecting in series the relative weight values of the primary evaluation factors with the relative weight values of the secondary evaluation factors to obtain an overall weight value of the secondary evaluation factors; repeating the foregoing steps; finally constructing the overall weight value of each secondary evaluation factor of each risk into a column vector to obtain a comprehensive determining weight matrix of hydrate drilling and production risks, and determining the risks in the hydrate drilling and production process by combining monitoring parameter change vectors.
Claims
1. A method for intelligently determining hydrate drilling and production risks based on fuzzy judgment, comprising the following steps in sequence: step 1: building a hierarchical structure model based on monitoring parameters in a hydrate drilling and production process, classifying into layers from top to bottom, which comprise a target layer, a primary evaluation factor layer and a secondary evaluation factor layer, wherein the target layer is composed of 8 risks which are formation gas production, borehole instability, hydrate production, drill string fracture, H.sub.2S production, sticking, bit balling and piercing-caused leakage of a drilling tool respectively; the primary evaluation factor layer is composed of 3 monitoring parameters types which are an injection parameter, a drilling parameter and a return parameter respectively; the secondary evaluation factor layer is composed of 11 monitoring parameters, which are injection fluid pressure, injection fluid flow, hanging load, drilling time, torque, rotational speed, total hydrocarbon value, hydrogen sulfide concentration, return fluid flow, return fluid pressure and return fluid temperature respectively, to construct a hierarchical structure model; step 2: constructing a determining matrix based on a selected risk in the target layer, first using a nine-scale method to compare primary evaluation factors of the primary evaluation factor layer and determine a scale value, then establishing a primary evaluation factor determining matrix based on the determined scale value, and then based on each primary evaluation factor of the primary evaluation factor layer respectively, establishing a secondary evaluation factor determining matrix for secondary evaluation factors of the secondary evaluation factor layer contained in each primary evaluation factor, wherein the determining matrixes of the primary evaluation factors and the secondary evaluation factors are expressed with {tilde under (A)}:
r.sub.i=(a.sub.i1a.sub.i2a.sub.i3 . . . a.sub.im).sup.1/m a relative fuzzy weight value of the i-th evaluation factor is:
w.sub.i=r.sub.i(r.sub.1+r.sub.2+r.sub.3+ . . . +r.sub.m).sup.1; step 4: converting the relative fuzzy weight value of the i-th evaluation factor into an explicit value expressing the relative weight fuzzy weight value w.sub.i of the i-th evaluation factor in the form of a triangular fuzzy number, wherein w.sub.i=(R.sub.i, M.sub.i, L.sub.i), L.sub.i is left extension of the triangular fuzzy number, R.sub.i is right extension of the triangular fuzzy number, and M.sub.i is a median of the triangular fuzzy number; converting the relative weight fuzzy weight value of the i-th evaluation factor into an explicit weight value DF.sub.i of the i-th evaluation factor:
w.sub.Ti=w.sub.1iw.sub.2i w.sub.1i is the relative weight value of the primary evaluation factor corresponding to the i-th secondary evaluation factor, and w.sub.2i is the relative weight value of the i-th secondary evaluation factor; respectively calculating a relative weight value of each primary evaluation factor of the remaining risks in the target layer, a relative weight value of each secondary evaluation factor contained in each primary evaluation factor and overall weight values of the secondary evaluation factors, constructing the overall weight values of the secondary evaluation factors of each risk into column vectors in the same order, and constructing a comprehensive determining weight matrix after the column vectors are arranged in sequence, namely a comprehensive determining weight matrix A.sub.T of hydrate drilling and production risks, wherein A.sub.T is shown as follows:
B=(b.sub.1b.sub.2. . . b.sub.m); step 8: obtaining a judgment result of hydrate drilling and production risks
2. The method for intelligently determining hydrate drilling and production risks based on fuzzy judgment according to claim 1, wherein the scale values of each primary evaluation factor and each secondary evaluation factor in step 2 are determined by the nine-scale method; when the monitoring parameter i corresponding to the selected risk is compared with the monitoring parameter j, the scale value is determined according to a response intensity of the monitoring parameter i and the monitoring parameter j to the risk, and the scale value is quantitatively expressed by the triangular fuzzy number
3. The method for intelligently determining hydrate drilling and production risks based on fuzzy judgment according to claim 1, wherein the comprehensive determining matrix {tilde under (A)}.sub.M in step 3 is as follows:
Description
BRIEF DESCRIPTION OF THE DRAWINGS
[0043]
[0044]
[0045]
DETAILED DESCRIPTION
[0046] The following further describes the present invention in detail with reference to the accompanying drawings and embodiments.
Embodiment 1
[0047] A method for intelligently determining hydrate drilling and production risks based on fuzzy judgment specifically includes the following steps.
[0048] A hierarchical structure model is built.
[0049] As shown in
[0050] A determining matrix is constructed.
[0051] With formation gas production an example, a sub-region is constructed according to each primary evaluation factor of this risk and the next evaluation factor layer dominated by this primary evaluation factor, and a determining matrix is established for this sub-region (see Table 1): based on the formation gas production in the target layer (namely a first layer), the nine-scale method is first used to compare primary evaluation factors of the primary evaluation factor layer (namely a second layer) and determine a scale value, then a primary evaluation factor determining matrix of the formation gas production is established based on the determined scale value, and then based on each primary evaluation factor of the primary evaluation factor layer respectively, a secondary evaluation factor determining matrix of the formation gas production is established for secondary evaluation factors of the secondary evaluation factor layer (namely a third layer) contained in each primary evaluation factor. Scale values of each primary evaluation factor and each secondary evaluation factor are determined by using the nine-scale method to construct an evaluation matrix A as follows:
TABLE-US-00001 TABLE 1 Evaluation scale table of a nine-scale method Scale value Meaning (1, 1, 1) Factors i and j are of equal importance. (1, 2, 3) The factor i is slightly more important than the factor j. (3, 4, 5) Compared with the factor j, the factor i is of great importance. (5, 6, 7) Compared with the factor j, the factor i is very important. (7, 8, 9) Compared with the factor j, the factor i is absolutely important.
[0052] A comprehensive determining matrix is established and a fuzzy weight value is calculated.
[0053] The established comprehensive determining matrix is as follows:
[0054] A geometric mean of each primary evaluation factor (monitoring parameter type) of the comprehensive determining matrix is solved:
r.sub.1=[(10.260.17),(10.310.21),(10.40.29)].sup.1/3=(0.354,0.402,0.488)
r.sub.2=[(3.610.53),(4.510.65),(5.411)].sup.1/3=(1.240,1.430,1.754)
r.sub.3=[(41.41);(521),(62.61)].sup.1/3=(1.776,2.154,2.499).sub..
[0055] The sum of the geometric mean is:
r=r.sub.1+r.sub.2+r.sub.3=(3.37,3.987,4.741)
[0056] The relative fuzzy weight value of each primary evaluation factor calculated by formula (5) is as follows:
[0057] The relative fuzzy weight value of each evaluation factor is converted by formula (6) into an explicit value of the evaluation factor as follows:
[0058] Similarly, the following can be obtained: DF.sub.2=0.38, and DF.sub.3=0.552.
[0059] The explicit weight value is normalized by formula (7) as follows:
[0060] Similarly, the following can be obtained: w.sub.2=0.366, and w.sub.3=0.531.
[0061] Calculation results of relative weight values of the foregoing primary evaluation factor layer (monitoring parameter type) of formation gas production are summarized as shown in Table 2.
TABLE-US-00002 TABLE 2 Summary table of calculation results of relative weight of the primary evaluation factor layer (monitoring parameter type) of formation gas production Injection parameter Drilling parameter Return parameter Geometric mean r.sub.i (0.354, 0.402, 0.488) (1.24, 1.43, 1.754) (1.766, 2.154, 2.499) Fuzzy weight w.sub.i (0.075, 0.101, 0.145) (0.262, 0.359, 0.521) (0.375, 0.54, 0.742) Explicit normalized 0.103 0.366 0.531 weight w.sub.i
[0062] The weight calculation of the secondary evaluation factor layer is carried out in sequence, and then series connection is carried out between various layers, and finally the risk weight value of formation gas production is obtained as shown in Table 3.
TABLE-US-00003 TABLE 3 Summary table of risk weight of formation gas production Relative weight Relative weight Secondary Primary value of the Secondary value of the evaluation evaluation primary evaluation evaluation secondary evaluation factor Overall Target factor factor factor factor weight value Formation Injection 0.103 Injection fluid 1 0.103 gas parameter pressure production Injection fluid 0 0 flow Drilling 0.366 Hanging load 0.548 0.201 parameter Drilling time 0.452 0.165 Torque 0 0 Rotational speed 0 0 Return 0.531 Total 0.625 0.332 parameter hydrocarbon value Hydrogen sulfide 0 0 concentration Return fluid flow 0.126 0.067 Return fluid 0.249 0.132 pressure Return fluid 0 0 temperature
[0063] Finally, the comprehensive determining weight matrix of hydrate drilling risks is obtained as follows:
[0064] Columns of the comprehensive determining weight matrix sequentially represent eight risk types which are formation gas production, borehole instability, hydrate production, drill string fracture, H.sub.2S production, sticking, bit balling and piercing-caused leakage of a drilling tool. In each column, overall weight values of injection fluid pressure, injection fluid flow, hanging load, drilling time, torque, rotational speed, total hydrocarbon value, hydrogen sulfide concentration, return fluid flow, return fluid pressure and return fluid temperature are represented sequentially.
[0065] A well A is a deep water well located in the South China Sea. Take the well A as an example for trial calculation. Basic data of this well is as follows:
TABLE-US-00004 Parameter name Data Parameter name Data Water depth (m) 1000 Geothermal gradient ( C./m) 0.025 Well depth (m) 5100 Submarine temperature ( C.) 4 Inlet temperature ( C.) 22 Outer diameter of drill string 127 (mm) Diameter of choke 76.2 Inner diameter of riser (mm) 472 manifold (mm) Drilling fluid density 1.3 Thermal conductivity of 2.25 (g/cm.sup.3) formation ( W/(m .Math. C.)) Displacement (L/s) 30 Thermal conductivity of 1.5 drilling fluid (W/(m .Math. C.)) Bit size (mm) 215.9 Specific heat of drilling fluid 1675 (J/(kg .Math. C.)) Bit pressure (kN) 40 Rotational speed (rad/min) 40 50
[0066] Downhole anomalies occurred when the well was drilled to a depth of 4833.7 m. Theoretical values of various monitoring parameters at 4833.7 m were calculated through the model. During the construction process, an on-site monitoring device acquired measured values of various monitoring parameters at the well section at a depth of 4833.7 m. Table 4 shows the theoretical values and the measured values corresponding to various monitoring parameters when the well was drilled to a depth of 4833.7 m.
[0067] b.sub.i is a relative change rate of the i-th monitoring parameter (namely the i-th evaluation factor); S.sub.i is a variation of a value of the i-th monitoring parameter; S.sub.ic is a measured value of the i-th monitoring parameter; S.sub.iL is a theoretical value of the i-th monitoring parameter; H.sub.i and is a reasonable change range of the value of the i-th monitoring parameter.
TABLE-US-00005 TABLE 4 Comparison table of model calculation values and field measured values at a drill depth of 4833.7 m Monitoring parameter Injection fluid Injection Hanging Drilling Rotational pressure fluid flow load time Torque speed Parameter (MPa) (m.sup.3/min) (kN) (min/m) (kN .Math. m) (rad/min) Theoretical 15.296 1.80 1745 5.5 11.85 50 value Measured 13.85 1.824 1653.55 6.3 6.82 50 value Monitoring parameter Total Hydrogen sulfide Return Return fluid Outlet Parameter hydrocarbon value concentration fluid flow pressure temperature value type (%) (ppm) (m.sup.3/min) (kPa) ( C.) Theoretical 4.06 0 1.80 14.57 22 value Measured 3.35 0 1.862 14.55 22 value
[0068] The relative change rate of each monitoring parameter was calculated and the monitoring parameter change vector was constructed by using the obtained monitoring parameter related data at the well depth of 4833.7 m (as shown in Table 4). The finally obtained judgment result is as follows:
Z=BA.sub.T=(0.604 0 0 0 71.572 0 0 27.824)
[0069] The foregoing results correspond to the risk types to draw a histogram of risk occurrence probability (as shown in
[0070] The foregoing descriptions are only preferred implementations of the present invention. It should be noted that for a person of ordinary skill in the art, several improvements and modifications may further be made without departing from the principle of the present invention. These improvements and modifications also fall within the protection scope of the present invention.