Groundwater inrush in mines directly threatens safe coal production. Aquifer yield plays a crucial role during water inrush. Significant accidents occur in areas where aquifer yields are strong. The yield of an aquifer is influenced by many things and, in this study, five for which data are easily acquired were selected as evaluation indices for coal-seam floor aquifer yield. They comprise specific yield, permeability, drilling fluid consumption, aquifer thickness, and fault and fold distribution. Based on these indices, a comprehensive model for evaluating water yield was constructed. Using the Ordovician limestone aquifer below the coal floor of Danhou coal mine, Hebei province, China, as an example, index data relating to aquifer yield were collected and the index weight determined. A geographic information system was used to prepare a thematic map for each driving factor and, subsequently, to superimpose them. Comprehensive water yield evaluation indexes were obtained and, finally, a zonal map of different water yield properties was developed for the research area.

Water hazards in mines threaten coal production safety in several countries. A good example is the highly confined Ordovician limestone aquifer in North China, where karst has developed intensively and aquifer yield distribution is highly anisotropic. The abundance of structures and the impacts of coal mining in the area are likely to lead to water inrush incidents. In recent years, several serious and severe water inrushes have occurred in North China, resulting in casualties and enormous financial losses.

Aquifer yield plays a crucial role with respect to water inflow in mines, and large water inrush accidents only occur in areas where yields are high. If aquifer yields are low, even in areas where pressures are high or where fault zones link aquifers, significant water inrush accidents cannot happen. Only a clear understanding of aquifer yield can help to reduce water hazards in mines. Consequently, many studies have been carried out into aquifer yields. Meyer & Winstanley (2003) predicted groundwater yield for the Cambrian–Ordovician aquifer in northeastern Illinois using uncertainty parameters in inferred conceptual models. Zhao & Chang (2007) divided a middle Ordovician aquifer in the Handan-Fengfeng mining area into four different yield zones according to the degree of development of karst. Bwalya (2011) estimated the specific yield of an aquifer in Idaho, USA, by alternative linearization of water table kinematic conditions. Wang et al. (2012) evaluated the yield of limestone in the Upper Taiyuan Formation in the Cheji coal mine, on the basis of specific yield. Peng et al. (2014) predicted the yield of a sandstone aquifer at the base of the upper Shihezi formation, in the Permian of the Wolong Lake coal mine, using fuzzy clustering, and comprehensive prediction. Their predictions were based on the characteristics of the lithologic and geological structure. After selecting evaluation indices, Liu et al. (2014) used a probabilistic neural network to predict the yield of the sandstone aquifer in the coal seam roof at the Xieqiao coal mine.

Although recent research into the yield of aquifers in coal mines has produced significant achievements, there are drawbacks including incomplete evaluation indices, difficulty in extracting index data and insufficient graphic representation. Because of this, this research into the Ordovician limestone aquifer of the Danhou coal mine in Hebei, China, was based on evaluation indices for coal-seam floor aquifer yield. These indices were used to build a comprehensive evaluation model for the aquifer's yield. Geographic information system (GIS) technology was integrated into the processing, storage and graphic representation of each index datum, to realize the evaluation analysis of the Ordovician aquifer. This method can effectively reflect the fact that coal-seam floor aquifer yield is influenced by many factors. At the same time, the evaluation results are objective and visible, providing a theoretical basis for aquifer yield research.

Location, etc.

The mine stands between Yongquan Zhuang and Nanliu Zhuang villages, in Yuxian county of Zhangjiakou, Hebei, China, in the southern part of the Yuxian mining area. It is 8 km from the Yuxian county border (southeast), 130 km from to Xuanhua (north), 330 km to Shijiazhuang (south), 230 km from Beijing (east), and 21 km from Guangling county Shanxi province (west). All local roads are linked, see Figure 1.
Figure 1

Transportation and location.

Figure 1

Transportation and location.

Close modal

Geology

The stratigraphic structure in this area is well developed beneath the Coal Measures strata. It includes the Sanggan group (Archaean), and the Changcheng, Jixian, Paleozoic-Cambrian and Ordovician systems of the middle-upper Algonkian. The Coal Measures strata belong to the Xiahuayuan formation in the lower-middle series of the Jurassic. There are Jiulongshan, Tiaojishan, and Houcheng formation strata of the Middle Jurassic, Zhangjiakou formation strata of the Upper Jurassic, and Tertiary and Quaternary strata overlying the Coal Measures.

Danhou mine is in the southern part of the central mining area of Yuxian, and its structural configuration is determined by the paleo-topography of the basement and the amplitude of crustal subsidence. Of the fractures developed in the mining area, three groups distributed around the edge are aligned, respectively, approximately south/north, east/west and northeast/southwest. Regional dip is quite variable, with a range between about 5 and 15°.

The aquifer

The research area can be divided, effectively, into four aquifer zones. The separate, karst-fracture confined aquifers of the Cambrian and Ordovician, the pore-fissure confined aquifer of the Jurassic, and the overlying, unconsolidated, porous Quaternary aquifer. The main aquifer threatening safety in Danhou coal mine is the Ordovician karst-fracture confined limestone, which, as the basement of the Coal Measures, underlies the coal seam floor directly. The principal lithology includes a number of limestones that are, variously: gray, dolomitic and brownish-yellow, aphanitic, and leopard-like, interlayered with thin celadon marls. Karst developed dissolution pores and corrosion fissures are accompanied by significant numbers of paleo-caverns. The aquifer's specific yield and permeability coefficient are, respectively, between about 0.02 L/s/m and 2.3 L/s/m, and 0.5 m/d and 7.2 m/d.

The research was carried out from the perspective of the representativeness of the indices and convenient data acquisition of data, and based on national regulations and previous research. Specific yield, permeability, drilling fluid consumption, aquifer thickness, and fault and fold distribution were selected as key indices for aquifer yield evaluation.

  • (1) Specific yield

    • Specific yield is the yield of a well when the pumped drawdown is 1 m (Li et al. 2014). This is information that can be obtained easily in pumping tests in coal mines, and also important evidence for determining the water yield grade in Provisions for Mine Water Control (State Administration of Work Safety Supervision 2009). The higher the specific yield, the greater the yield from the aquifer.

  • (2) Aquifer thickness

    • Thickness is the most intuitive factor influencing aquifer yield. The greater the thickness of a block, the larger the unit volume of storage, and, hence, the higher aquifer yield. Data regarding the thickness of an aquifer can be obtained from geological drilling logs in mining areas.

  • (3) Permeability coefficient

    • The permeability coefficient is a constant characterizing a rock's permeability. A high permeability coefficient implies better interconnection between aquifers, better rock permeability, and higher aquifer yield.

  • (4) Drilling fluid consumption

    • In drilling, the consumption of fluid (down-hole) can reflect the permeability of the strata, which is determined by the geological conditions. Variations in the quality and consumption of drilling fluid, indicate changes in the permeability and leakage of individual strata (Wu et al. 2009). Thus, it is an important indicator of the hydraulic properties of drilled strata and adopted as important evidence of aquifer yield.

  • (5) Fault and fold distribution

    • Generally speaking, the fracture zones of faults and the axes of folds display diverse lithologies. Fractures develop intensively and are likely to become water conducting channels, collecting surrounding groundwater and forming high yield zones. The distribution of faults and folds is, thus, an important index for judging potential aquifer yield.

The information from pumping tests, drilling and construction, as well as influencing factors, was collected and used to develop thematic contour maps of the influencing factors, using GIS software (Figures 26). A spatial attribute database was established to store geoscience information.
Figure 2

Thematic map of specific yield.

Figure 2

Thematic map of specific yield.

Close modal
Figure 3

Thematic map of permeability coefficient.

Figure 3

Thematic map of permeability coefficient.

Close modal
Figure 4

Thematic map of aquifer thickness.

Figure 4

Thematic map of aquifer thickness.

Close modal
Figure 5

Thematic map of drilling fluid consumption.

Figure 5

Thematic map of drilling fluid consumption.

Close modal
Figure 6

Thematic map of fault and fold distribution.

Figure 6

Thematic map of fault and fold distribution.

Close modal
The comprehensive evaluation index EI for water yield properties was introduced to evaluate aquifer yields. It is defined as the sum of the cumulated influence of various factors affecting aquifer yield in specific cell(s) in a defined area. The comprehensive aquifer yield evaluation model can be expressed by:
formula
1
where, EI is the comprehensive aquifer yield evaluation index; Wk is the factor weight; fk(x,y) is the normalized index value; x and y are coordinates; and n is the number of influencing factors.

Wk is determined by the analytic hierarchy process (AHP) suggested by the American operational researcher Saaty (1977). It is a multifactorial decision method combining both qualitative and quantitative analysis. Its basis is the decomposition of a complex problem into several levels and factors, so that the relative importance of two indexes can be determined. After the judgment matrix has been established, the weights (degrees) of importance of different schemes are obtained by calculating its maximum eigenvalue and corresponding eigenvector (Saaty 1977, 1980). The specific steps are:

  • (1) Establishing the analytic hierarchy model

    • The major influencing factors for each research object were determined according to the basis of judgment and system analysis concerning it. The sub-factors determining each major factor were then resolved. Thus, the factors that interact are gradually acquired, and a hierarchical relationship is constructed from top to bottom.

  • (2) Constructing the judgment matrix

    • If the influences of n factors X = {x1, x2, x3xn} on factor Z are to be compared, Saaty (1980) propose establishing a pairwise comparison matrix, comparing all factors in pairs. Thus, two factors xi and xj are selected each time, and aij represents the influence ratio of xi to xj on Z. All of the results, A = (aij)n×n in the comparison, are exhibited as a matrix, called the ‘judgment matrix’. With respect to determination of aij, Saaty et al. (1980) proposed that the scales be represented by the numbers 1 to 9 and their reciprocal. The connotations of the scales 1–9 are listed in Table 1.

  • (3) Weight solution and consistency check

    • The weightings are calculated first by determining the maximum eigenvalue λmax of the judgment matrix, A, and then, using AW = λmaxW, the corresponding eigenvector, W, of λ. The values of W were normalized so that they were between 0 and 1. Establishing the judgment matrix helps to reduce interference from other factors and reflects the difference between the impacts of a pair of factors objectively. However, as with all comparisons, there is inevitably some inconsistency and so this needs to be checked. This is done by:

    • 1. Calculating the consistency index, CI
      formula
      2
    • 2. Searching for the corresponding mean random consistency index RI. For n (n = 1, 2 …, 9), the values of RI, as given by Saaty (1980), are shown in Table 2:

    • 3. Calculating the consistency ratio, CR
      formula
      3
    • When CR < 0.1, the consistency of the judgment matrix is acceptable; otherwise, modification is required. The AHP judgment matrix (Table 3) for evaluating the yield of the coal-seam floor aquifer in this area was established on the basis of the Table 1. Subsequently, the factor weights were calculated using the judgment matrix and these are shown in Table 4.

Table 1

Proportional scale and meaning

ScaleMeaning
The two elements compared have the same level of importance 
One of the two elements is slightly more important than the other 
One of the two elements is clearly more important than the other 
One of the two elements is much more important than the other 
One of the two elements is very much more important than the other 
2, 4, 6, and 8 Intermediate values between those of the adjacent judgments above 
ScaleMeaning
The two elements compared have the same level of importance 
One of the two elements is slightly more important than the other 
One of the two elements is clearly more important than the other 
One of the two elements is much more important than the other 
One of the two elements is very much more important than the other 
2, 4, 6, and 8 Intermediate values between those of the adjacent judgments above 
Table 2

The mean random consistency index, RI

N123456789
RI 0.58 0.90 1.12 1.24 1.32 1.41 1.45 
N123456789
RI 0.58 0.90 1.12 1.24 1.32 1.41 1.45 
Table 3

Judgment matrix

FactorsSpecific yieldAquifer thicknessPermeability coefficientDrilling fluid consumptionFault and fold distribution
Specific yield 
Aquifer thickness 1/2 1/2 
Permeability coefficient 1/3 1/2 1/2 
Drilling fluid consumption 1/3 1/2 1/2 
Fault and fold distribution 
FactorsSpecific yieldAquifer thicknessPermeability coefficientDrilling fluid consumptionFault and fold distribution
Specific yield 
Aquifer thickness 1/2 1/2 
Permeability coefficient 1/3 1/2 1/2 
Drilling fluid consumption 1/3 1/2 1/2 
Fault and fold distribution 

λmax = 5.05862, CI = 0.01465, CR = 0.01308 < 0.1.

Table 4

Influencing factor weights

FactorsSpecific yieldAquifer thicknessPermeability coefficientDrilling fluid consumptionFault and fold distribution
Weights 0.32068 0.18208 0.11003 0.11003 0.27718 
FactorsSpecific yieldAquifer thicknessPermeability coefficientDrilling fluid consumptionFault and fold distribution
Weights 0.32068 0.18208 0.11003 0.11003 0.27718 

As can be seen, the value of the mean random consistency index, CR, is 0.01308, which is <0.1. The judgment matrix therefore satisfies the consistency check. The influencing factor weights obtained are shown in Table 4.

There are dimensional differences because of the different physical reality represented by each index. Before calculating the comprehensive evaluation index for water yield properties, data normalization was required for all factors, to eliminate the effects of the different dimensions and make the data comparable. Normalization was carried out using Equation (4) (Zhu et al. 2013):
formula
4
where, Fi is the normalized data, and min (xi) and max (xi) are the respective minimum and maximum values of each influencing factor.
When the data had been normalized, GIS technology was used to superimpose the thematic maps of the influencing factors. This generated an information storage layer, the superimposed cell containing information on all of the influencing factors, and the comprehensive index, EI, for the water yield properties of each evaluation cell was obtained. The ‘Natural Breaks’ system included in the GIS was used to grade the EI value. This generated the 5-class classification – see Figure 7 – and a comprehensive evaluation zone for water yield properties, integrating the influence of many factors, could be constructed (Figure 8).
Figure 7

Threshold value determination by natural grading.

Figure 7

Threshold value determination by natural grading.

Close modal
Figure 8

Zones with different aquifer yield properties.

Figure 8

Zones with different aquifer yield properties.

Close modal

The red area in Figure 8 is that with high aquifer yield. This arises from the great thickness of aquifer (65 to 105 m), and its high specific yield (1.3 to 2.3 L/s/m) and permeability coefficient (5.6 to 7.2 m3/d). The orange-red area has slightly lower yields than the red area. Here, the relatively large aquifer thickness (50 to 80 m), specific yield (0.8 to 2.3 L/s/m) and permeability coefficient (4.2 to 5.7 m3/d) play dominant roles in the water yield of the southwest zone; while the water yield of the northeast zone is determined by the high permeability coefficient (5.6 to 7.27 m3/d) and consumption of drilling fluid (0.3 to 0.39 m3/d). The dark green zone denotes the low yield area arising from low values of aquifer thickness (25 to 26 m), specific yield (0.02 to 0.05 L/s/m) and permeability coefficient (0.7 to 2.5 m3/d). So, this area has the lowest water yield in the evaluation area. The lighter green zone represents a relatively low yield area arising from the relative thinness of the aquifer (27 to 40 m), and low specific yield (0.05 to 0.36 L/s/m), permeability coefficient (0.7 to 2.5 m3/d) and consumption of drilling fluid (0.14 to 0.29 m3/d). The yellow area has moderate water yield, and is the transition zone between the relatively high- and low- yielding areas. The faulted and folded areas are found mainly in the red zones, where yields are high. Value ranges of the factors in the different aquifer yield zones are shown in Table 5.

Table 5

Value ranges of factors in different aquifer yield zone

Aquifer yield propertiesSpecific yield (L/s/m)Permeability coefficient (m/d)Aquifer thickness (m)Drilling fluid consumption (m3/d)
High water yield 1.3 ∼ 2.3 5.6 ∼ 7.2 65 ∼ 105 0.2 ∼ 0.26 
Relatively high water yield 0.8 ∼ 2.3 4.2 ∼ 5.7 50 ∼ 80 0.3 ∼ 0.39 
5.6 ∼ 7.27 
Moderate water yield 0.3 ∼ 1.3 2.6 ∼ 4.1 40 ∼ 60 0.3 ∼ 0.3 
Relatively low water yield 0.05 ∼ 0.36 0.7 ∼ 2.5 27 ∼ 40 0.14 ∼ 0.29 
Low water yield 0.02 ∼ 0.05 0.5 ∼ 0.7 25 ∼ 26 0.2 ∼ 0.32 
Aquifer yield propertiesSpecific yield (L/s/m)Permeability coefficient (m/d)Aquifer thickness (m)Drilling fluid consumption (m3/d)
High water yield 1.3 ∼ 2.3 5.6 ∼ 7.2 65 ∼ 105 0.2 ∼ 0.26 
Relatively high water yield 0.8 ∼ 2.3 4.2 ∼ 5.7 50 ∼ 80 0.3 ∼ 0.39 
5.6 ∼ 7.27 
Moderate water yield 0.3 ∼ 1.3 2.6 ∼ 4.1 40 ∼ 60 0.3 ∼ 0.3 
Relatively low water yield 0.05 ∼ 0.36 0.7 ∼ 2.5 27 ∼ 40 0.14 ∼ 0.29 
Low water yield 0.02 ∼ 0.05 0.5 ∼ 0.7 25 ∼ 26 0.2 ∼ 0.32 

  • (1) By combining AHP, a comprehensive model for evaluating coal-seam floor aquifer yield properties was established. In terms of representativeness and convenience of data acquisition, five factors – specific yield, permeability coefficient, drilling fluid consumption, aquifer thickness, and fault and fold distribution – were selected to evaluate aquifer yield. The model reflected the fact that aquifer yield is influenced by many factors.

  • (2) Taking the Ordovician limestone aquifer at Danhou coal mine, Hebei, China, as the data source, GIS technology was used to develop thematic contour maps of the distribution of factors influencing aquifer yield. The thematic GIS maps for the different factors were subsequently superimposed, producing the comprehensive aquifer yield properties evaluation model discussed in this paper. The CI value for each yield property was calculated for every superimposed cell, and the research area was divided into zones with different yield characteristics, so that a map showing zones with different coal-seam floor aquifer yields could be drawn. GIS technology is helpful because it enables the storage, processing and graphic representation of relevant information, and can provide reference for aquifer yield analysis and evaluation in the future.

This research was financially supported by China National Natural Science Foundation (Grant no. 41430318, 41272276), the China National Scientific and Technical Support Program (Grant Numbers 201105060-06, 2012BAB12B03), Guizhou Province Science and Technology Agency Foundation (Qian Ke He LH Zi [2014]7617), Guizhou University Introducing Talents Research Foundation (2014-61), the Innovation Research Team Program of the Ministry of Education (IRT1085), and the State Key Laboratory of Coal Resources and Safe Mining.

Li
B.
Guo
X. M.
Xu
S.
2014
Risk assessment of coal floor groundwater bursting based on fuzzy comprehensive evaluation-comprehensive weight
.
Journal of Henan Polytechnic University (Natural Science)
1
(
1
),
6
11
.
Liu
D. M.
Lian
H. Q.
Han
Y.
2014
Study on water enrichment prediction of coal roof sandstone aquifer based on PNN
.
Coal Technology
33
(
9
),
336
338
.
Meyer
S. C.
Winstanley
D.
2003
Uncertainty of estimates of groundwater yield for the Cambrian-Ordovician Aquifer in northeastern Illinois
. In:
Proceeding of the Symposium on Groundwater Management Under Uncertainty Conference
,
June 23
,
273
283
.
Peng
T.
Xuan
L. R.
Zang
H. C.
2014
Prediction and evaluation of water abundance of sandstone aquifer in Wolonghu coal mine
.
Safety in Coal Mines
45
(
8
),
199
202
.
Saaty
T. L.
1977
A scaling method for priorities in hierarchical structures
.
Journal of Mathematical Psychology
15
(
3
),
234
281
.
Saaty
T. L.
1980
The Analytic Hierarchy Process
.
McGraw-Hill
,
New York
.
State Administration of Work Safety Supervision
2009
Provisions for Mine Water Control
.
China Coal Industry Publishing House
,
Beijing
.
Wang
X. Q.
Zhu
Y. L.
Yu
J. Z.
2012
Analysis and evaluation of water abundance of the upper Taiyuan formation limestone water in Juji coal field
.
Zhongzhou Coal
4
(
5
),
17
20
.
Wu
Q.
Wang
J. H.
Liu
D. H.
2009
A new practical methodology of the coal floor water bursting evaluation IV: the application of AHP vulnerable index method based on GIS
.
Chinese Journal of Rock Mechanics and Engineering
34
(
2
),
233
238
.
Wu
Q.
Li
B.
Liu
S. Q.
2013
Vulnerability assessment of coal floor groundwater bursting based on zoning variable weight model: a case study in the typical mining region of Kailuan
.
Journal of China Coal Society
38
(
9
),
1516
1521
.
Zhao
B. X.
Chang
M. H.
2007
Handan-Fengfeng mining area karstic aquifer characteristics and water yield property division
.
Coal Geology of China
19
(
5
),
41
47
.
Zhu
Z. K.
Xu
Z. M.
Sun
Y. J.
2013
Research on the risk evaluation methods of water inrush from coal floor based on dimensionless multi-source information fusion technique
.
Chinese Journal of Rock Mechanics and Engineering
30
(
6
),
911
916
.