Journal of Hydrology 532 (2016) 149–162
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Journal of Hydrology
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Review papers The karst permeability scale effect of Sete Lagoas, MG, Brazil ⇑ Paulo Galvão a, , Todd Halihan b, Ricardo Hirata a a University of São Paulo, Institute of Geosciences, Rua do Lago 562, São Paulo, SP 05508-080, Brazil b Oklahoma State University, Boone Pickens School of Geology, 105 Noble Research Center, Stillwater, OK 74078, USA article info summary
Article history: Collecting and interpreting permeability data in karst systems is considered complicated due to three dis- Received 25 July 2015 tinct properties of these systems. First, the distribution of high permeability features may be one- Received in revised form 30 October 2015 dimensional features difficult to detect with wells, or may be so high in the wells the upper measurement Accepted 16 November 2015 limit is encountered during aquifer testing. Secondly, turbulent flow may make the application of contin- Available online 21 November 2015 uum hydraulic principles difficult. Finally, permeability in these systems commonly increases with the This manuscript was handled by Corrado Corradini, Editor-in-Chief, with the scale of measurement. The aquifer for Sete Lagoas, Brazil, was used to evaluate a permeability combina- assistance of Barbara Mahler, Associate tion methodology testing the permeability structure across a range of spatial scales in order to develop a Editor quantitative model of hydraulically active features consistent across all scales of measurement, from matrix properties to regional-scale flow. The aquifer in this study has some wells without measurable Keywords: drawdown during pumping due to high permeability. Data indicated an increase in permeability from Karst the small- to the well-scale and a decrease from the well- to regional-scale due to the localized develop- Permeability ment of a karst bedding plane dissolution in one structurally controlled region of the aquifer. The matrix Transmissivity permeability in the region is very low and the secondary porosity is mostly filled by secondary precipi- Hydraulic conductivity tation of calcite. Based on measurement technique, the permeability data vary over many orders of mag- Scale effect nitude, while the physical size of permeable features of the aquifer are consistent across the scales of data Brazil collection. The geometry provides a quantitative understanding of the scale effects of permeability measurements. Ó 2015 Elsevier B.V. All rights reserved.
Contents
1. Introduction ...... 150 2. Site description...... 151 3. Methods ...... 151 3.1. Permeability database ...... 151 3.1.1. Small-scale: matrix data, optical microscopy analysis and permeability measurements ...... 152 3.1.2. Well-scale: aquifer test data and empirical relationship analysis ...... 152 3.1.3. Regional-scale: potentiometric data and capture zone analysis ...... 153 3.2. Permeability component data...... 153 3.2.1. Sub-horizontal fracture hydraulic apertures...... 153 3.2.2. Hydraulic conduit diameters ...... 154 3.3. Permeability combination models ...... 154 4. Results...... 154 4.1. Sete Lagoas permeability database...... 154 4.1.1. Small-scale analysis and measurements ...... 155 4.1.2. Well-scale: aquifer test data and empirical relationship analysis ...... 155 4.1.3. Regional-scale: potentiometric data and capture zone analysis ...... 157
⇑ Corresponding author. Tel.: +55 986 677 505. E-mail address: [email protected] (P. Galvão). http://dx.doi.org/10.1016/j.jhydrol.2015.11.026 0022-1694/Ó 2015 Elsevier B.V. All rights reserved. 150 P. Galvão et al. / Journal of Hydrology 532 (2016) 149–162
4.2. Permeability feature sizes from inversion ...... 158 4.2.1. Small-scale: matrix data and feature sizes ...... 158 4.2.2. Well-scale permeable feature sizes ...... 158 4.2.3. Regional-scale: overall bedding planes and karst aquifer thicknesses ...... 158 4.3. Permeability combination models ...... 158 5. Discussion...... 159 6. Conclusion ...... 161 Acknowledgments ...... 161 Appendix A. Notation ...... 161 Appendix B. Supplementary material ...... 161 References ...... 161
1. Introduction karstic conduits. Halihan et al. (2000) tested if the Király (1975) hypothesis has an underlying physical basis using a permeability Formation bulk permeability depends on the shape, amount, database for the Cretaceous carbonates from the San Antonio seg- and interconnectivity of void spaces, or permeability structure. ment of the Edwards aquifer and found the Király hypothesis was This is often quantified with testing in the form of hydraulic con- applicable for the aquifer, with nine orders of magnitude variabil- ductivity or transmissivity values, which incorporate fluid proper- ity in permeability. ties and aquifer dimensions into the measurements. Grain size Clauser (1992) analyzed a compilation of different type of crys- analyses, permeameters, aquifer tests and groundwater models talline rocks and noted the permeability can increase three orders are most commonly used to obtain permeability estimates from of magnitude from small- to well-scale, but from well- to regional- small- to regional-scales. However, the permeability values can scale, the increase would not continue. The Halihan et al. (2000) vary over orders of magnitude, depending on the geological forma- model indicated if larger fractures were present, the permeability tion. Permeability data are the fundamental property of the rock would continue to increase with scale. Many of these approaches body and most easily converted to the physical dimensions of compiled data at a range of scales, but few provide a physical basis pores, fractures, or conduits. This work will assume that fractures for the values to allow predictions for various scales. are two dimensional features and conduits are largely one dimen- Martinez-Landa and Carrera (2005) analyzed the hydraulic con- sional flow features. ductivity scale effects in fractured granite in Grimsel, Switzerland. Karstic carbonate rocks are one of the most heterogeneous and The study used different types of hydraulic tests (pulse, recovery, anisotropic of all formations found in nature, because the perme- cross-hole, and tunnel inflow measurements) for matrix- and ability structure of these formations are created by fluid flow gen- borehole-scale, and cross-hole numerical interpretations for erating a hierarchal rock structure of flow features facilitating large-scale flow. The average hydraulic conductivity increases by circulation in the downgradient direction (Mangin, 1975). Conse- orders of magnitude as the test scale grows. The zones of high quently, karst hydraulic parameters are not an independent, inher- hydraulic conductivities are hydraulically interconnected and con- ited static attribute of the rock, but are dynamic over geological trol the permeability at large scales. Other geological and hydroge- time (Huntoon, 1985). Another consideration is this structure can ological investigations related to scale effect using different type of adjust as the flow regime responds to changing hydraulic boundary permeability tests were developed in fractured rocks (Maréchal conditions. Thus, the hierarchy of permeability pathways and their et al., 2004; Illman, 2007), and sedimentary formations (Landon organization within the formation are dictated by the hydrody- et al., 2001; Kurikami et al., 2008; Chapuis, 2013). The close rela- namic characteristics of the flow system operating within the tionship between hydraulic interconnectivities in the rock hetero- recent geological past and the characteristics of older flow systems geneities and hydraulic conductivities increases average (Ewers, 1982). permeability data across the scales. The difficulties in the estimation of karst permeability are One approach to quantify the physical basis of the scale effect is amplified by flow that may be non-Darcian, which leads to the cau- via permeability combination models (PCM). The models provide tious use of continuum estimations assuming Darcian flow. estimates of the averaged permeability generated by a mixture of Depending on the dissolution feature size, some standard aquifer different permeable features in an aquifer, or the numerical effect tests may obtain no measurable drawdown as the test reaches of small-scale features on the well- or regional-scale data (Halihan the upper measurement limit. This results in lower bound estimate et al., 1998, 1999, 2000). The steady-scale geometric models esti- in the calculation of transmissivity and hydraulic conductivity val- mate the effects of different heterogeneities on formation perme- ues. These factors result in uncertainties in making permeability ability structure, assuming measurements on different scales are estimates are a key factor to understanding groundwater flow all valid for the scale the data were collected. These models are and solute transport in the subsurface (Quinlan and Ewers, 1985; modifications of equations for layered aquifers (Leonards, 1962; Rehfeldt et al., 1989). Fetter, 1994). These formations and their heterogeneity can lead to well- To predict formation values at the well-scale in a karstic forma- known permeability scale effects (Rats, 1967; Király, 1975; tion, standard aquifer tests (slug tests, time-drawdown tests and Maclay and Land, 1988; Hovorka et al., 1995; Halihan et al., step-drawdown tests) and the standard analytical equations (e.g. 1999). Scale effects are generally defined as continual increases Theis, 1935; Cooper and Jacob, 1946), assume Darcian flow and in permeability magnitude from small- to regional-scale estimates often provide reasonable fits to the data (Kresic, 2013). These esti- (Király, 1975; Schulze-Makuch et al., 1999). In the Király (1975) mates should be used with caution, due to anisotropic or potential study, made in Mesozoic fractured and karstic limestone aquifers non-Darcian conditions. The estimates may not be valid on a located in the Jura Mountains, Switzerland, it was hypothesized regional-scale, due to scale dependency. In case of regions with the increase from small- to the well-scale was caused by fractures limited pumping test data, but having specific capacity test data, and the largest permeabilities on the regional-scale were caused by an alternative method to estimate permeability utilizes empirical P. Galvão et al. / Journal of Hydrology 532 (2016) 149–162 151 relationships between transmissivity and specific capacity (Razack filled by the precipitation of calcite (Tonietto, 2010). The majority and Huntley, 1991; Mace, 1997). In cases with no measurable of groundwater migrates through dissolution features character- drawdown occurring in a well due to high permeability, a lower ized as tertiary porosity. bound estimate can be obtained using a Thiem (1906) method Results from geologic mapping and optical well logging suggest (Halihan et al., 2000). the urbanized area of Sete Lagoas (Fig. 1) is primarily located in a On the regional-scale, groundwater models can be used to graben (Galvão et al., 2015). The area is filled with limestones from obtain permeability estimates (Scanlon et al., 2001, 2003). Another Sete Lagoas Formation and overlying Cenozoic unconsolidated sed- analytical approach is using a regional capture zone analysis, iments, with portions covered by competent rocks from the Serra defined as the area of an aquifer in which all the water will be de Santa Helena Formation (slate, marble, siltstone and argillite). removed by a pumping well or wells within a certain time period The graben limits results in barrier boundaries for groundwater, (Todd, 1980; Grubb, 1993). In some cases, equations can be super- recharging and accumulating water in the aquifer. The most rele- imposed to calculate the capture zone of multiple well systems vant discontinuities for groundwater circulation are from natural (Javandel and Tsang, 1986). karst processes in a low matrix limestone. This explains the devel- This research conducted an evaluation of multi-scale perme- opment of two dominant solutionally enlarged horizontal bedding ability structure, estimating values of permeability at the small-, planes in the Sete Lagoas Formation with high permeability and well-, and regional-scale, along with hydraulic conductivity and significant storage capacity. The two bedding planes are a thick, transmissivity. These data were compared against observations of shallow continuous dissolution zone with conduits 1–8 m thick, the physical size of permeable features, as well as calculations of near the contact with the overlying unconsolidated sediments; the hydraulic dimension of fractures (hydraulic apertures) and and 10–20 m below, a thinner continuous dissolution zone with conduits (hydraulic diameters). Combining different methodolo- conduits that are 20 cm–1 m thick. The limestone dips and become gies, a quantitative hydrogeologic conceptual model was devel- thicker, reaching about 160 m thickness, and is completely covered oped, consistent across all scales of measurement. The aquifer by rocks from the Serra de Santa Helena Formation to the north- studied was the Sete Lagoas karst aquifer (Pessoa, 1996), located east. The two bedding plane conduits become thinner to the north- within the limits of the municipality of Sete Lagoas, Minas Gerais, east (Galvão et al., 2015). Brazil. This aquifer has common complications for karst systems Based on optical well logs and outcrop field observations, the with meter scale pores and some pumping tests obtaining no mea- hydrogeologic conceptual model for the aquifer includes both surable drawdown. Quantifying these parameters through differ- non-karstic and karstic bedding plane apertures. This conceptual ent scales is important because of the increasing demands on the model is based on previous work conducted for a karst risk assess- aquifer. The demands require users to have a quantitative under- ment (Galvão et al., 2015). The terms ‘‘non-karstic bedding planes” standing of how the aquifer functions so that it can be properly uti- for zones without karstification, and ‘‘solutionally enlarged bed- lized and protected. The PCM approach was utilized, comparing ding planes” for dissolution zones will be used here. small-scale permeability data calculated by a permeameter with well-scale parameters calculated by standard pumping tests and 3. Methods an estimated regional-scale value, via capture zone analysis of a multiple pumping well system. These calculations were made to The evaluation of scale effects in this research first involved test possible correlations between different ranges of scale and building a database of permeability measurements from small- to quantify variations in the permeability scale effect. While values regional-scales for the aquifer. Small-scale permeabilities were of permeability vary over many orders of magnitude, the physical measured by means of a hand-held air permeameter. Well-scale size of flow features controlling permeability measurements would evaluation utilized aquifer tests and a relationship derived remain a consistent quantifiable dataset for the aquifer. between specific capacity and transmissivity. A regional-scale esti- mate utilized potentiometric surface measurements and a capture 2. Site description zone analysis approach. Empirical calculations were utilized to invert the database val- The aquifer studied was the Sete Lagoas karst aquifer (Pessoa, ues to determine what size hydraulic features (i.e. pore diameter, 1996), located in the municipality of Sete Lagoas, Minas Gerais, fracture hydraulic aperture, or conduit hydraulic diameters) would Brazil, 70 km northwest of Belo Horizonte (Fig. 1). The city has a be required to obtain measured field values of formation perme- population greater than 200,000 over an area of 538 km2 (IBGE, abilities. These inverted values were utilized in a forward modeling 2010). The area of highest population density is located in the older PCM approach similar to Halihan et al. (1999) to test the stability of urbanized part of the city. The current water supply is almost permeability features across the scales of data. These methods will entirely groundwater from the aquifer sourced from private and be presented sequentially from the bulk permeability measure- public wells. The public supply wells are managed by the Water ments to the inverted estimate of the size of hydraulic features, Supply and Sewage Service (SAAE) [SAAE – Serviço de Abastecimento and finally the PCM forward modeling. de Água e Esgoto]. The highest pumping rates are located in areas The order of magnitude for each scale adopted, for field obser- with the greatest population density (Fig. 1). vations and analytical analysis, was based on Király (1975). These Geologically, the area is located in the São Francisco Craton, dimensions included small-scale from 10 2 to 100 m, by the size of where carbonate argillo-arenaceous sediments are emplaced giv- the rock matrix permeameter analysis; well-scale between 100 and ing origin to the Bambuí Group (Branco and Costa, 1961; 102 m, by pumping test drawdown radius of influence; and Oliveira, 1997; Schöll and Fogaça, 1973; Dardenne, 1978; regional-scale from 102 to 104 m, according to the size of the cap- Schobbenhaus, 1984; Ribeiro et al., 2003; Tuller et al., 2010). The ture zone analysis of the multiple pumping well system. hydrostratigraphic relationships for the Sete Lagoas karst aquifer and spatial distribution are given in Pessoa (1996) and Galvão et al. (2015). The aquifer, which is approximately 75 m thick, con- 3.1. Permeability database sists of Neoproterozoic limestones, composed of two members: the Pedro Leopoldo Member (at the base) and the Lagoa Santa Member For this work, small-scale measurements utilize hand samples (on the top). The primary porosity and matrix permeability can be and thin sections of aquifer matrix. This measurement scale is considered low (Moore, 1989) and the secondary porosity is mostly occasionally divided by authors into a hand-scale and a micro- 152 P. Galvão et al. / Journal of Hydrology 532 (2016) 149–162
Fig. 1. Location map in UTM coordinates of Sete Lagoas showing the municipal boundary and urbanized area, the well locations (private and public) and the geology of the study area. The highest pumping rates are located in the areas with the greatest population density.
scale, but they are combined here to represent measurements of Permeability measurements were performed on dry hand sam- carbonate matrix pore properties. Well-scale data are derived from ples of limestones sourced from the two members of the Sete aquifer tests. Wells reaching the upper measurement limit by not Lagoas Formation. The measurements were collected across dry, being able to draw down the water table are included in the anal- fresh and planar rock surface, free of dust and without any weath- ysis. While many authors utilize groundwater model data for ering effects. Measurements (24 total) were taken to determine the regional estimates (Thorkildsen and McElhaney, 1992; Halihan mean small-scale permeability, ksm, in Darcys. These measure- et al., 2000; Scanlon et al., 2001, 2003), this work utilizes an analyt- ments were converted to square meters, and then estimates of ical capture zone solution. the small-scale hydraulic conductivity, Ksm, and transmissivity, Tsm, of the entire aquifer thickness were calculated. The advantage of this non-destructive method is the rapid and reproducible 3.1.1. Small-scale: matrix data, optical microscopy analysis and results (Fossen et al., 2011). permeability measurements Field observations and optical microscopy using thin section for 3.1.2. Well-scale: aquifer test data and empirical relationship analysis the two members of the Neoproterozoic limestone rocks from the Seven long duration (48 h) transient pumping tests were con- 2 Sete Lagoas karst aquifer were made in order to describe the fea- ducted to measure the well-scale transmissivity, Tw (L /t), using tures of the matrix, such as rock mineralogy, grain size and the Theis (1935) method. Pumping rates ranged from 47 to micro-fractures. A TinyPerm II portable hand-held air permeame- 194 m3/h. For the case of a zero drawdown well test in well PT- ter, manufactured by New England Research (NER), was utilized 01, the Thiem equation (Thiem, 1906) was used for analysis, to measure the permeabilities in the matrix of these members. assuming 0.01 m (1 cm) of drawdown in the pumping well. This P. Galvão et al. / Journal of Hydrology 532 (2016) 149–162 153 well and the observation wells at distances of 25 m and 51 m were (L) is the half width of the maximum capture zone, and i (dimen- located in the central portion of the urbanized area. The test sionless) is the hydraulic gradient. 3 3 pumped PT-01 at a constant rate, Qw (L /t), of 130 m /h (Table S1 The regional discharge rate, Qr, was estimated by summing the in the electronic supplementary material (ESM)). The bedding pumping rate data values from public supply wells (data provided plane dissolution can be very large in some regions of Sete Lagoas. by SAAE and Servmar Environmental & Engineering) and private This affects the permeability values as deduced by the Darcian wells (data acquired from the SIAGAS’s database – SIAGAS, 2006) approach and implied turbulent flow. The effect would be noted extracting groundwater within the capture zone. Transmissivity, in the Theis curve, but the Theis method was applied based on Tr, was determined based on the best fit-empirical capture zone the analysis of measurements in the seven pumping tests. This in comparison to the potentiometric capture zone, using the equa- assumption would result in a potential underestimation of hydrau- tion describing the empirical edge of the capture zone for a con- lic dimensions of the conduits, but forward modeling of the upper fined aquifer: limit of pumping tests (Halihan et al., 2000) indicates these tests ¼ hiy ð Þ cannot be used to evaluate features of this size. By obtaining mea- x p 3 tan 2 Twiy surable drawdown, the hydraulically connected feature size must Qr be similar to the estimated values. where x (L) is the distance parallel to the regional hydraulic gradi- Twenty-seven time-drawdown or step-drawdown tests were ent and y (L) is the distance perpendicular to the regional hydraulic done to estimate specific capacity, S (L2/t), utilizing the SAAE’s C gradient (Todd, 1980; Grubb, 1993). A sensitivity analysis was con- supply wells. In mathematical terms, S is defined as the pumping C ducted to evaluate the variability possible in this approach. rate in the well, Q (L3/t), divided by the observed decline in w The final regional transmissivity was considered the average of hydraulic head in the well, Dh (L), from an aquifer test. In the case w both analytical values calculated. The regional-scale hydraulic con- of the step-drawdown tests, every discharge value was divided by ductivity, K (L/t), was calculated by dividing the transmissivity its respective drawdown, Dh , observed in each step, and then the r w values by the average total thickness, b (L) (estimated at mean S was calculated. The results were analyzed using an empir- total C 75 m), and then converting the values to permeability in square ical relationship derived for this karst aquifer by fitting a power meters. law function between measured specific capacity and transmissiv- All the permeability data sets were entered in a GIS database ity, based on the Razack and Huntley (1991) and Mace (1997) and georeferenced in the ArcGIS 10.1 software. The coordinate sys- methods. The goal was to estimate the most representative well- tem was Universal Transverse Mercator (UTM) projection, Zone 23, scale transmissivity, both in non-karstic and solutionally enlarged datum SAD 69, with units in meters. Data from optical well logs bedding planes, and then estimate the well-scale hydraulic con- and analytical calculation results were considered to estimate the ductivity and permeability. Information about the physical thick- regional sizes features of the dissolution zones, b (L). These values ness of bedding planes, b (L), was established with optical well r w allowed a comparison between observed physical apertures and logging and outcrop field observations (Galvão et al., 2015). inverted hydraulic apertures for the various data. A transmissivity map was constructed from the data to observe the variability at the regional scale from well scale data. T values w 3.2. Permeability component data were utilized assuming the long duration pumping test data were more accurate data than the empirical values from specific capac- The permeability data were inverted to determine the physical ity data. The values that were found in the observation wells for size of hydraulic features capable of producing the various perme- their respective pumping wells were located in the same hydroge- ability values and to test the stability of permeability feature sizes ologic setting (Table S1). across various scales of measurement. The hydraulic size of frac- tured apertures and conduit diameters were calculated under 3.1.3. Regional-scale: potentiometric data and capture zone analysis assumed laminar and turbulent flow conditions. Measurements of the water table were taken only in SAAE’s supply wells in the Sete Lagoas karst aquifer to develop a potentio- 3.2.1. Sub-horizontal fracture hydraulic apertures metric map for regional-scale permeability evaluation. The well The conversion between permeability values and the size of a casing elevation data were acquired using a SRTM image (Shuttle sub-horizontal fracture was calculated using the cubic law
Radar Topography Mission). According to Demétrio et al. (2006), (Lamb, 1932) between the intrinsic permeability of a fracture, kf 2 the accuracy in the use of this data is less than 5 m. (L ), and a hydraulic fracture aperture, bf (L): A capture zone analysis for the central high pumping rate well 2 area was performed and an assessment of the accuracy of the ana- bf k ¼ ð4Þ lytical results was estimated. Some assumptions were made, such f 12 as pumping wells in a confined aquifer with a uniform flow, under This equation was used to convert between measured perme- steady-state conditions. A capture zone area was determined, ability values and physical feature size, but is only an approxima- based on estimated flow lines in the potentiometric surface. Ana- tion. The calculations do not provide accommodation for fracture lytical equations, derived for confined aquifers by Todd (1980) plane roughness and variability in fracture geometry. and Grubb (1993) delineating the edge of the capture zone, were The hydraulic fracture aperture was calculated from transmis- 2 used to estimate the regional-scale transmissivity, Tr (L /t). sivity or conductivity data from aquifer tests using the hydraulic aperture of a single low-angle fracture equation (Halihan et al., Q r Tr;x ¼ ð1Þ 1999), b (L): 2pX i f L 1=3 Q r 12v cosðhÞ ; ¼ ð Þ Tr y 2 bf ¼ ðTw KsmbtotalÞ ð5Þ 2YLi g
2 2 where Tr,x and Tr,y (L /t) are the regional transmissivities in their where ʋ is the kinematic viscosity of the water (L /t), Tw is the well- 3 2 respective directions, Qr (L /t) is the overall pumping rate or regio- scale transmissivity (L /t) calculated by pumping test, Ksm is the nal discharge rate, XL (L) is the distance from the pumping well to small-scale hydraulic conductivity of the matrix (L/t), btotal is the 2 the downgradient edge of the capture zone (stagnation point), YL total thickness of aquifer (L), g is gravitational constant (L/t ), and 154 P. Galvão et al. / Journal of Hydrology 532 (2016) 149–162 h is the angle between the fracture and the horizontal plane. If the estimated from optical logging or outcrop evaluation, as they are fracture is horizontal, the angle is zero. idealized hydraulic dimensions, not physical ones dealing with roughness and connectivity. This set of equations allowed inver- 3.2.2. Hydraulic conduit diameters sion of the permeability database. The same concept can be used
The hydraulic conductivity of a conduit, Kc (L/t), can be related to generate forward models for evaluation of scale effects. to a conduit hydraulic diameter assuming both laminar and turbulent flow (Turcotte and Schubert, 1982; Halihan et al., 3.3. Permeability combination models 1998). The hydraulic conductivity equations can also be converted to permeability; however, hydraulic conductivity is simpler to For the permeability combination forward model approach illustrate the turbulent case. The laminar hydraulic conductivity, (PCM) to evaluate the scale effects in the karst aquifer, the analyt- K (L/t): c,lam ical models developed for small- to regional-scale were combined 2 and compared. These models are steady-state and modifications of gdc K ; ffi ð6Þ c lam 32v equations for layered aquifers. Other assumptions were used to simplify the models. The hydraulic conductivity of the matrix is For turbulent hydraulic conductivity K (L/t): c,turb much less than the hydraulic conductivity of the fracture/conduit. 4 5 7 This can be evaluated by utilizing the permeability database. The ffi : g7 dc ð Þ Kc;turb 4 706 1 7 solutionally enlarged bedding planes are continuous permeable v 7 2 features controlling the hydraulic system, where sub-vertical frac- The single horizontal conduit equation was utilized (Halihan tures do not have significant influence on permeability structure et al., 1999) to estimate the hydraulic conduit diameter, dc (L), from across the scales of measurement (Galvão et al., 2015). aquifer tests. Assuming the hydraulic conductivity of the matrix is much less than the hydraulic conductivity of the conduit, Kc: 4. Results Kcdc Kbtotal Tw K ffi ) dc ffi ) dc ffi ð8Þ btotal Kc Kc The results will be presented sequentially from the bulk perme- ability measurements, to the inverted estimate of the size of Substituting dc in Eq. (6), to estimate the laminar hydraulic con- hydraulic features, and finally the PCM results. duit diameter, dc,lam (L):