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Engineering in Chalk

Lawrence, Preene, Lawrence and Buckley ISBN 978-0-7277-6407-2 https://doi.org/10.1680/eiccf.64072.631 ICE Publishing: All rights reserved

Pumping tests for construction dewatering in chalk M Preene *1, T O L Roberts 2 and D J Hartwell 3 1 Preene Groundwater Consulting Limited, Wakefield, UK 2 WJ Groundwater Limited, Watford, UK 3 Groundwater Management Consultant, Finchampstead, UK * Corresponding Author

ABSTRACT pumping tests, where one or more are pumped at a controlled rate for an extended period of time (usually several days), can be an effective method of obtaining data for the design of construction dewatering systems. Pumping tests in chalk present par- ticular challenges, and the design of the test well and monitoring well array should take account of the hydrogeological setting of the chalk, which can include unconfined or confined , with or without overlying granular -bearing deposits. Data from the pumping tests can be used to derive hydrogeological parameters, or can be used directly in dewatering design by the superposition of method. Where there is concern about potential impacts from groundwater lowering (e.g. settlement, changes in water chemistry, depletion of groundwater-dependent features) then relevant data from constant rate pumping phases can be useful in the assessment of the magnitude and distribution of impacts that might result from the dewatering system.

1 INTRODUCTION servations during drilling; installation and monitoring of piezometers; and, variable head permeability tests Construction dewatering typically involves pumping in boreholes and piezometers – Further details are groundwater from an array of wells or sumps in or given in Chapter 5 of CIRIA Report C750 (Preene et around an excavation. The objective is to temporarily al. 2016). lower groundwater levels to allow excavation or tun- On larger projects, or where hydrogeological con- nelling below original groundwater level in stable ditions are complex, and/or where confidence is re- and workably dry conditions. quired in the seepage analysis, later phases of ground The design process for construction dewatering investigation often include a well pumping test. This systems requires an adequate understanding of hy- paper will describe best practice in the design, execu- drogeological conditions that will affect construction. tion and analysis of pumping tests for the specific Potential environmental impacts will also need to be purposes of construction dewatering in chalk. considered. The ground investigation should gather data on hydrogeological parameters, including per- meability (), which are used as 2 GEOTECHNICAL INVESTIGATION IN inputs to the seepage analysis or groundwater numer- CHALK icalitfr.63938.001.3d modelling 3 used in design to determineitfr.63938.001.3d inter 3 alia 04/02/2018 05:14:20pm 04/02/2018 05:14:20pm the required dewatering pumping rates. Routinely, The Chalk Group is a significant in the UK, ground investigations will include: groundwater ob and is widely exploited for water supply. However,

631 Engineering in Chalk

for construction projects below groundwater level, Methods relevant to chalk include rising and falling 3. Assessment of wider hydrogeological conditions. toe of the wall. However, if the cut-off wall pene- because of its diverse geotechnical and hydrogeolog- head tests in boreholes and piezometers, or packer Monitoring data from pumping tests can be ana- trates to only a few metres below excavation level, ical properties, chalk can be a very challenging mate- permeability tests in boreholes in stable chalk. The lysed to discern aquifer boundary conditions, hy- then horizontal permeability will still be the control- rial in which to work. The background to construc- parameters derived are local and may be highly in- draulic connections between strata and potential ling factor on dewatering flow rate. This is because tion dewatering in chalk is described in detail by fluenced by the presence or absence of fissures at the impacts on water dependent features (springs, the dewatering wells, even if installed internally, are Preene and Roberts (2017). The more highly weath- test horizon which may in any case be plugged with wetlands, nearby water supply wells, etc.). likely to be required to extend to at least 6m to 10 m ered, structureless forms of chalk can act like both fi- slurrified chalk during drilling. 4. Secondary objectives. The test may provide data below the excavation level. ne-grained and coarse-grained geotechnical soils and Pumping tests are one of the most effective meth- gathering opportunities not available in the earlier For the hydrogeological conditions shown in Fig- can suffer from ‘running’ conditions or ‘blows’, ods of obtaining project scale hydrogeological infor- phases of ground investigation. For example, the ure 2(b) inflows to a shallow open cut excavation where uncontrolled groundwater pressures destabilise mation. Groundwater is pumped at a controlled rate water samples from continuous pumping of a well (i.e. with no low permeability cut-off wall) in the the base and sides of an excavation. Water strikes in from a defined location (the test well) and the draw- may be more representative of groundwater overlying gravels would be controlled by the perme- percussion drilled boreholes in weathered structure- down of groundwater level is observed in surround- chemistry than samples taken from piezometers ability of the gravels. less chalk can indicate low permeability ‘putty’ chalk ing piezometers (Figure 1). Field methods are well or boreholes. Open cut excavation Unsaturated acting as a confining layer to more permeable chalk defined and standards exist for such tests (e.g. BS Note that careful selection of the test location can zone below. ISO 14686:2003; BS EN ISO 22282-4:2012). significantly reduce the marginal cost of a pumping

Conversely, less weathered structured grades may test if the test well and piezometer array can later Saturated zone act like massive fissured rocks, where inflow to ex- form part of the main works dewatering scheme. Chalk weathering Flow predominantly grade and permeability horizontal cavations occurs only along pre-existing bedding 3 DESIGN OF PUMPING TESTS IN CHALK may vary with depth planes, fissures or other geological features. 3.2 Hydrogeological conditions in chalk

Groundwater inflows can vary from minor seepages 3.1 Objectives of pumping tests Preene and Roberts (2017) identify that, in terms of (a) Unconfined chalk aquifer, no overlying high-permeability stra- to major inflows with associated risks of instability tum present (open cut excavation shown, predominantly horizontal assessing construction dewatering requirements, and inundation. In the context of a ground investigation, a pumping flow) there are three significant hydrogeological settings test is probably the most expensive field test that di- rectly informs the design of a dewatering system, and (Figure 2). Chalk may form an unconfined or con- Excavation Unsaturated Control Weir with deep zone Discharge piped away to fined aquifer. In unconfined conditions the upper part cut-off valve tank can provide high quality information. Unfortunately, Permeable stratum (e.g. beyond distance of influence River terrace deposits) Power Flow meter pumping tests occasionally give inconclusive results, of the chalk aquifer may be unsaturated, and excava-

Original GWL or results that do not adequately clarify the dewater- tions into the chalk above groundwater level may en- Structureless chalk may Saturated ing requirements. This is sometimes because the counter little or no groundwater (Figure 2(a)). Over- be present at interface zone lying water-bearing deposits can be in hydraulic Lowered GWL pumping test has not been designed appropriately to fulfil the designer’s requirements. connection with the chalk forming a combined un- There is no single template for the design and exe- confined aquifer (Figure 2(b)). When chalk acts as a Standpipe piezometer cution of a pumping test. A test for the purposes of confined aquifer, the entire thickness of the chalk is (b) Unconfined chalk aquifer, overlying high-permeability stratum assessing groundwater resources for water supply (as saturated, and the piezometric level is above the top present (excavation with deep cut-off shown, significant vertical P1 P3 P2 described in BS ISO 14686:2003) has different re- of the chalk (Figure 2(c)); overlying water-bearing flow component)

Test well quirements to a test for the purposes of construction deposits can be in hydraulic connection with the

dewatering (see Preene and Roberts 1994). In addi- chalk; the potential connection will be influenced by Initial Figure 1. Schematic section through a single well pumping test tion to the ground conditions, the permanent and the presence and vertical permeability of any struc- Low permeability Excavation piezometric confining layer with short level in (P1, P2, P3 are piezometers or monitoring wells). tureless chalk at the interface between strata. cut-off confined temporary works arrangements for the excavation or aquifer Permeable stratum may tunnel will influence the test design. The objectives be present above chalk for a pumping test intended to support construction 3.3 Influence of partial cut-offs Examination of samples, cores and borehole logs Structureless chalk may dewatering design typically include: be present at interface provides little quantitative information on hydrogeo- Where an open cut excavation (i.e. without low per- 1. Derivation of hydrogeological parameters includ- logical parameters of a chalk aquifer. Experience meability cut-off walls) is made in an unconfined ing estimates of aquifer transmissivity, permeabil- suggests that anisotropic conditions, where the hori- chalk aquifer, Figure 2(a), inflow is predominantly ity and storage coefficients. These parameters are zontal permeability is significantly greater than the controlled by the horizontal permeability of the (c) Confined chalk aquifer (excavation with short cut-off shown, used as inputs to dewatering design calculations. predominantly horizontal flow) Drawdown causes aquifer to be- vertical permeability, often predominate at construc- chalk. If a relatively deep cut-off wall is installed to 2. Well construction. Use of the same design and come locally unconfined near dewatering system tion project scale in chalk rock. target a higher permeability horizon and effectively method of construction planned for the dewater- Figure 2. Principal chalk hydrogeological settings relevant to con- A range of in-situ borehole techniques are availa- cut it off, then flow to a dewatering system is con- ing wells should confirm well yields and high- struction dewatering problems, showing interaction between cut- ble to characterise hydrogeological conditions. trolled by the vertical permeability at or below the light any concerns with the well specification. off depth and flow orientation.

632 Preene, Roberts and Hartwell

for construction projects below groundwater level, Methods relevant to chalk include rising and falling 3. Assessment of wider hydrogeological conditions. toe of the wall. However, if the cut-off wall pene- because of its diverse geotechnical and hydrogeolog- head tests in boreholes and piezometers, or packer Monitoring data from pumping tests can be ana- trates to only a few metres below excavation level, ical properties, chalk can be a very challenging mate- permeability tests in boreholes in stable chalk. The lysed to discern aquifer boundary conditions, hy- then horizontal permeability will still be the control- rial in which to work. The background to construc- parameters derived are local and may be highly in- draulic connections between strata and potential ling factor on dewatering flow rate. This is because tion dewatering in chalk is described in detail by fluenced by the presence or absence of fissures at the impacts on water dependent features (springs, the dewatering wells, even if installed internally, are Preene and Roberts (2017). The more highly weath- test horizon which may in any case be plugged with wetlands, nearby water supply wells, etc.). likely to be required to extend to at least 6m to 10 m ered, structureless forms of chalk can act like both fi- slurrified chalk during drilling. 4. Secondary objectives. The test may provide data below the excavation level. ne-grained and coarse-grained geotechnical soils and Pumping tests are one of the most effective meth- gathering opportunities not available in the earlier For the hydrogeological conditions shown in Fig- can suffer from ‘running’ conditions or ‘blows’, ods of obtaining project scale hydrogeological infor- phases of ground investigation. For example, the ure 2(b) inflows to a shallow open cut excavation where uncontrolled groundwater pressures destabilise mation. Groundwater is pumped at a controlled rate water samples from continuous pumping of a well (i.e. with no low permeability cut-off wall) in the the base and sides of an excavation. Water strikes in from a defined location (the test well) and the draw- may be more representative of groundwater overlying gravels would be controlled by the perme- percussion drilled boreholes in weathered structure- down of groundwater level is observed in surround- chemistry than samples taken from piezometers ability of the gravels. less chalk can indicate low permeability ‘putty’ chalk ing piezometers (Figure 1). Field methods are well or boreholes. Open cut excavation Unsaturated acting as a confining layer to more permeable chalk defined and standards exist for such tests (e.g. BS Note that careful selection of the test location can zone below. ISO 14686:2003; BS EN ISO 22282-4:2012). significantly reduce the marginal cost of a pumping

Conversely, less weathered structured grades may test if the test well and piezometer array can later Saturated zone act like massive fissured rocks, where inflow to ex- form part of the main works dewatering scheme. Chalk weathering Flow predominantly grade and permeability horizontal cavations occurs only along pre-existing bedding 3 DESIGN OF PUMPING TESTS IN CHALK may vary with depth planes, fissures or other geological features. 3.2 Hydrogeological conditions in chalk

Groundwater inflows can vary from minor seepages 3.1 Objectives of pumping tests Preene and Roberts (2017) identify that, in terms of (a) Unconfined chalk aquifer, no overlying high-permeability stra- to major inflows with associated risks of instability tum present (open cut excavation shown, predominantly horizontal assessing construction dewatering requirements, and inundation. In the context of a ground investigation, a pumping flow) there are three significant hydrogeological settings test is probably the most expensive field test that di- rectly informs the design of a dewatering system, and (Figure 2). Chalk may form an unconfined or con- Excavation Unsaturated Control Weir with deep zone Discharge piped away to fined aquifer. In unconfined conditions the upper part cut-off valve tank can provide high quality information. Unfortunately, Permeable stratum (e.g. beyond distance of influence River terrace deposits) Power Flow meter pumping tests occasionally give inconclusive results, of the chalk aquifer may be unsaturated, and excava-

Original GWL or results that do not adequately clarify the dewater- tions into the chalk above groundwater level may en- Structureless chalk may Saturated ing requirements. This is sometimes because the counter little or no groundwater (Figure 2(a)). Over- be present at interface zone lying water-bearing deposits can be in hydraulic Lowered GWL pumping test has not been designed appropriately to fulfil the designer’s requirements. connection with the chalk forming a combined un- There is no single template for the design and exe- confined aquifer (Figure 2(b)). When chalk acts as a Standpipe piezometer cution of a pumping test. A test for the purposes of confined aquifer, the entire thickness of the chalk is (b) Unconfined chalk aquifer, overlying high-permeability stratum assessing groundwater resources for water supply (as saturated, and the piezometric level is above the top present (excavation with deep cut-off shown, significant vertical P1 P3 P2 described in BS ISO 14686:2003) has different re- of the chalk (Figure 2(c)); overlying water-bearing flow component)

Test well quirements to a test for the purposes of construction deposits can be in hydraulic connection with the

dewatering (see Preene and Roberts 1994). In addi- chalk; the potential connection will be influenced by Initial Figure 1. Schematic section through a single well pumping test tion to the ground conditions, the permanent and the presence and vertical permeability of any struc- Low permeability Excavation piezometric confining layer with short level in (P1, P2, P3 are piezometers or monitoring wells). tureless chalk at the interface between strata. cut-off confined temporary works arrangements for the excavation or aquifer Permeable stratum may tunnel will influence the test design. The objectives be present above chalk for a pumping test intended to support construction 3.3 Influence of partial cut-offs Examination of samples, cores and borehole logs Structureless chalk may dewatering design typically include: be present at interface provides little quantitative information on hydrogeo- Where an open cut excavation (i.e. without low per- 1. Derivation of hydrogeological parameters includ- logical parameters of a chalk aquifer. Experience meability cut-off walls) is made in an unconfined ing estimates of aquifer transmissivity, permeabil- suggests that anisotropic conditions, where the hori- chalk aquifer, Figure 2(a), inflow is predominantly ity and storage coefficients. These parameters are zontal permeability is significantly greater than the controlled by the horizontal permeability of the (c) Confined chalk aquifer (excavation with short cut-off shown, used as inputs to dewatering design calculations. predominantly horizontal flow) Drawdown causes aquifer to be- vertical permeability, often predominate at construc- chalk. If a relatively deep cut-off wall is installed to 2. Well construction. Use of the same design and come locally unconfined near dewatering system tion project scale in chalk rock. target a higher permeability horizon and effectively method of construction planned for the dewater- Figure 2. Principal chalk hydrogeological settings relevant to con- A range of in-situ borehole techniques are availa- cut it off, then flow to a dewatering system is con- ing wells should confirm well yields and high- struction dewatering problems, showing interaction between cut- ble to characterise hydrogeological conditions. trolled by the vertical permeability at or below the light any concerns with the well specification. off depth and flow orientation.

633 Engineering in Chalk

Conversely, if a low permeability cut-off is installed rarely carried out, and airlift pumping is common- 3.5 Types of pumping test programme drawdowns are generated, the pumped flow rate may down to the top of the chalk, inflow would typically ly used to develop wells. reduce significantly. Where the test is for the purpos- A pumping test typically comprises a sequence of be governed by the horizontal permeability of the Test wells screened across geological boundaries es of construction dewatering design it is normal test phases, each intended to provide different infor- chalk. If the cut-off is extended deeper the vertical should generally be avoided because of difficulties in practice to allow the flow rate to reduce, and not to mation. Different projects and different hydrogeolog- permeability of the chalk will become increasingly interpretation of the data plus the potential contami- attempt to adjust the pump to keep flow rate constant. ical conditions require different test programmes, important. nation risk associated with aquifer cross connections. Also, to gain the most useful data ‘constant rate’ comprising test phases selected from Table 2, which Where a partial cut-off is present which reaches The design of the piezometer array should also be pumping tests for dewatering schemes are generally is based on the authors’ experience. below the internal well depth (as depicted in Figure appropriate to the hydrogeological setting. Where carried out at the maximum achievable flow rate. The Often the constant rate pumping test phase is most 2(b), then the seepage analysis is dependent on sev- there is an overlying permeable stratum (Figure 2(b) test well is commonly ‘over pumped’ with drawdown relevant to the design of dewatering systems. This eral factors; the horizontal permeability of the chalk and 2(c)), it is usually necessary to have separate pie- in the well at or close to pump intake. As a result, typically involves using a borehole submersible below the cut-off toe; the vertical permeability of the zometers with response zones targeted at the chalk there may be a significant seepage face so that the pump to abstract from a test well for between 2 and 7 chalk above the cut-off toe; and the individual yields and the overlying stratum. water level in the pumped well often does not pro- days; longer tests are sometimes carried out, espe- of dewatering wells installed to the proposed target The screened zone for the test well needs to target vide a useful guide to conditions in the aquifer out- cially where environmental impacts are of concern. internal well depth. the appropriate horizon. Where a partial cut-off is side the well. The pumping rate should be large enough to generate A further complication is that where permeability planned this may be the chalk below the cut-off. Where artificial recharge of groundwater is significant drawdown in the chalk outside the well. varies with depth, due to chalk weathering as in Fig- Well design must also consider the presence of planned, special test programmes involving re- Ideally, at the end of the test drawdown in piezome- ure 2(a), or due to the existence of an overlying stra- any groundwater contamination. In some settings, injection of water are required. Typically, the test is ters in the target horizon at between 10 to 30 m from tum, Figure 2(b) or (c), then the pumping test re- particularly unconfined conditions, legacy contami- started conventionally whereby water is pumped the pumped well should be of the order of 10% of the sponse will usually be dominated by the most nation can exist from former land use. Groundwater from well(s) and discharged to surface water. In later required drawdown for the proposed dewatering permeable horizon present. If the intention is to in- may be contaminated in permeable strata overlying stages the water from the pumped well(s) is diverted scheme. stall a cut-off through the high permeability horizon the chalk (e.g. River Terrace Deposits) where pre- to recharge well(s). This allows data to be gathered then data from a fully screened, test well, installed sent, in the chalk or in both strata. In such conditions, Table 2: Characteristics of different phases of pumping tests both on the capacity of the recharge wells, and the in- before the cut-off is constructed, may be of limited piezometers should have short response zones and Test type Typical Outline of typical test and test objective teraction between the pumping and recharge wells. A duration value. grout seals to reduce the risk of forming a pathway Equipment 15–60 Short period of continuous pumping. Objec- test using two pumping wells and three recharge for contamination to migrate vertically. Where con- test min tive is to confirm pumps, pipework, etc. are wells is described by Roberts and Holmes (2011). functioning, and to inform setting of pump- 3.4 Design of test well and monitoring well array tamination is present, the test programme needs care- ing rates for later phases. Short pumping test programmes (e.g. comprising ful design to avoid unnecessarily mobilising contam- yield tests or step tests only) are sometimes carried Effective pumping tests in chalk require that the Yield test 1–8 h Well pumped at nominal constant rate. Ob- ination. Also, the need for treatment of pumped water jective is to estimate well yield. out where there are restrictions on the volumes of pumping well and the array of piezometers be de- Step test 8–12 h Well pumped in step-wise fashion with in- prior to disposal should be considered. water that can be discharged from the test, or where signed appropriately for the hydrogeological condi- creasing flow rates (typically 60 to 100 min per step). Objective is to estimate well per- hydrogeological conditions are already well charac- tions (Table 1). The strength and stability of the Table 1: Typical pumping test well design for dewatering design in chalk formance, including well yield. terised, but there is uncertainty over likely well Constant 2–28 d Well pumped at nominal constant rate. Ob- chalk (as described by the CIRIA grades, see Spink yields. Short duration pumping tests can also be use- (2002)) must also be considered, as this influences Typical pumping test well con- Typical well rate pump- jective is to assess drawdown in aquifer over struction development ing test a wide area and allow derivation of hydroge- ful to assess the effectiveness of groundwater cut-off well design: Unconfined Plain well liner above groundwater Airlift devel- ological parameters and boundary conditions. walls in shafts and cofferdams.  Grade A structured chalk typically allows stable chalk aquifer, level, slotted well screen below. opment is Pumping 2–28 d Water pumped from well(s) and re-injected no overlying Formation stabilizer filter gravel common. Wells re-injection to other well(s). Objectives are same as for The basic monitoring requirements for pumping boreholes to be formed, where the lower sections permeable stra- around screen, grout seal above rarely acidised test constant rate test, plus estimating recharge tests are to record the pumped flow rate (via flowme- of wells are left unlined as an open hole (i.e. with tum (Fig 2(a)) well capacity and assessing interaction be- Unconfined Well screened in chalk only*: Airlift devel- tween abstraction and recharge wells. ters or V-notch weirs) and groundwater levels in the no well screen). This is common practice for chalk aquifer, Plain well liner to extend short dis- opment is Dewatering 5–28 d A group of wells, typically forming all or a pumped well and piezometers (via manual readings with overlying tance (3 to 5 m) below top of common. Wells wells in the confined chalk aquifer in London and trial/pilot sub-section of the proposed dewatering sys- or water level dataloggers). elsewhere (Charalambous et al., 2013). It is also permeable stra- chalk, grouted into place, with slot- rarely acidised test tem is pumped. Objective is to investigate the tum (Fig 2(b)) ted well screen below. Formation effectiveness of the full system. The piezometer array should be appropriate for the common to develop such wells by injection of stabilizer filter gravel around Cut-off 1–5 d A well within the area enclosed by a cut-off hydrogeological setting. The piezometer array will concentrated hydrochloric acid, which dissolves screen, grout seal above wall pump- wall is pumped. The objective is to investi- Confined chalk Well screened in chalk only*: Wells common- ing test gate the effectiveness of the cut-off wall. typically include instruments in the range 5m up to the drilling slurry, and cleans the bore, opening aquifer Plain well liner to extend short dis- ly acidised Note: min = minute; h = hour; d = day 100m distant from the pumped well. In confined aq- blocked fissures (Banks et al. 1993). (Fig 2(c)) tance (3 to 5 m) below top of chalk, grouted into place. Well is uifers far field monitoring out to several hundred me-  In more weathered grades of chalk (structured The term ‘constant rate’ is a misnomer. If the completed as open hole below well borehole pump is not adjusted, the flow rate will tend tres or more may be required to assess off-site ef- grades B and C, and structureless grade D) bore- liner. fects. Some piezometers should also target any high holes are more likely to be unstable and slotted Note: *Where permeable strata are present above the chalk, test wells can be to reduce slightly as the drawdown in the well chang- installed with the well screen and filter gravel through both strata, with grout es the discharge head at the pump. In some cases, for permeability strata overlying the chalk. The rate of well screens are typically installed to keep the seals above. However, pumping tests in such hybrid wells can be difficult to drawdown of groundwater levels occurs rapidly, im- bore open. Well development by acidisation is usefully analyse for dewatering design purposes. example where the aquifer is bounded, and large

634 Preene, Roberts and Hartwell

Conversely, if a low permeability cut-off is installed rarely carried out, and airlift pumping is common- 3.5 Types of pumping test programme drawdowns are generated, the pumped flow rate may down to the top of the chalk, inflow would typically ly used to develop wells. reduce significantly. Where the test is for the purpos- A pumping test typically comprises a sequence of be governed by the horizontal permeability of the Test wells screened across geological boundaries es of construction dewatering design it is normal test phases, each intended to provide different infor- chalk. If the cut-off is extended deeper the vertical should generally be avoided because of difficulties in practice to allow the flow rate to reduce, and not to mation. Different projects and different hydrogeolog- permeability of the chalk will become increasingly interpretation of the data plus the potential contami- attempt to adjust the pump to keep flow rate constant. ical conditions require different test programmes, important. nation risk associated with aquifer cross connections. Also, to gain the most useful data ‘constant rate’ comprising test phases selected from Table 2, which Where a partial cut-off is present which reaches The design of the piezometer array should also be pumping tests for dewatering schemes are generally is based on the authors’ experience. below the internal well depth (as depicted in Figure appropriate to the hydrogeological setting. Where carried out at the maximum achievable flow rate. The Often the constant rate pumping test phase is most 2(b), then the seepage analysis is dependent on sev- there is an overlying permeable stratum (Figure 2(b) test well is commonly ‘over pumped’ with drawdown relevant to the design of dewatering systems. This eral factors; the horizontal permeability of the chalk and 2(c)), it is usually necessary to have separate pie- in the well at or close to pump intake. As a result, typically involves using a borehole submersible below the cut-off toe; the vertical permeability of the zometers with response zones targeted at the chalk there may be a significant seepage face so that the pump to abstract from a test well for between 2 and 7 chalk above the cut-off toe; and the individual yields and the overlying stratum. water level in the pumped well often does not pro- days; longer tests are sometimes carried out, espe- of dewatering wells installed to the proposed target The screened zone for the test well needs to target vide a useful guide to conditions in the aquifer out- cially where environmental impacts are of concern. internal well depth. the appropriate horizon. Where a partial cut-off is side the well. The pumping rate should be large enough to generate A further complication is that where permeability planned this may be the chalk below the cut-off. Where artificial recharge of groundwater is significant drawdown in the chalk outside the well. varies with depth, due to chalk weathering as in Fig- Well design must also consider the presence of planned, special test programmes involving re- Ideally, at the end of the test drawdown in piezome- ure 2(a), or due to the existence of an overlying stra- any groundwater contamination. In some settings, injection of water are required. Typically, the test is ters in the target horizon at between 10 to 30 m from tum, Figure 2(b) or (c), then the pumping test re- particularly unconfined conditions, legacy contami- started conventionally whereby water is pumped the pumped well should be of the order of 10% of the sponse will usually be dominated by the most nation can exist from former land use. Groundwater from well(s) and discharged to surface water. In later required drawdown for the proposed dewatering permeable horizon present. If the intention is to in- may be contaminated in permeable strata overlying stages the water from the pumped well(s) is diverted scheme. stall a cut-off through the high permeability horizon the chalk (e.g. River Terrace Deposits) where pre- to recharge well(s). This allows data to be gathered then data from a fully screened, test well, installed sent, in the chalk or in both strata. In such conditions, Table 2: Characteristics of different phases of pumping tests both on the capacity of the recharge wells, and the in- before the cut-off is constructed, may be of limited piezometers should have short response zones and Test type Typical Outline of typical test and test objective teraction between the pumping and recharge wells. A duration value. grout seals to reduce the risk of forming a pathway Equipment 15–60 Short period of continuous pumping. Objec- test using two pumping wells and three recharge for contamination to migrate vertically. Where con- test min tive is to confirm pumps, pipework, etc. are wells is described by Roberts and Holmes (2011). functioning, and to inform setting of pump- 3.4 Design of test well and monitoring well array tamination is present, the test programme needs care- ing rates for later phases. Short pumping test programmes (e.g. comprising ful design to avoid unnecessarily mobilising contam- yield tests or step tests only) are sometimes carried Effective pumping tests in chalk require that the Yield test 1–8 h Well pumped at nominal constant rate. Ob- ination. Also, the need for treatment of pumped water jective is to estimate well yield. out where there are restrictions on the volumes of pumping well and the array of piezometers be de- Step test 8–12 h Well pumped in step-wise fashion with in- prior to disposal should be considered. water that can be discharged from the test, or where signed appropriately for the hydrogeological condi- creasing flow rates (typically 60 to 100 min per step). Objective is to estimate well per- hydrogeological conditions are already well charac- tions (Table 1). The strength and stability of the Table 1: Typical pumping test well design for dewatering design in chalk formance, including well yield. terised, but there is uncertainty over likely well Constant 2–28 d Well pumped at nominal constant rate. Ob- chalk (as described by the CIRIA grades, see Spink yields. Short duration pumping tests can also be use- (2002)) must also be considered, as this influences Hydrogeology Typical pumping test well con- Typical well rate pump- jective is to assess drawdown in aquifer over struction development ing test a wide area and allow derivation of hydroge- ful to assess the effectiveness of groundwater cut-off well design: Unconfined Plain well liner above groundwater Airlift devel- ological parameters and boundary conditions. walls in shafts and cofferdams.  Grade A structured chalk typically allows stable chalk aquifer, level, slotted well screen below. opment is Pumping 2–28 d Water pumped from well(s) and re-injected no overlying Formation stabilizer filter gravel common. Wells re-injection to other well(s). Objectives are same as for The basic monitoring requirements for pumping boreholes to be formed, where the lower sections permeable stra- around screen, grout seal above rarely acidised test constant rate test, plus estimating recharge tests are to record the pumped flow rate (via flowme- of wells are left unlined as an open hole (i.e. with tum (Fig 2(a)) well capacity and assessing interaction be- Unconfined Well screened in chalk only*: Airlift devel- tween abstraction and recharge wells. ters or V-notch weirs) and groundwater levels in the no well screen). This is common practice for chalk aquifer, Plain well liner to extend short dis- opment is Dewatering 5–28 d A group of wells, typically forming all or a pumped well and piezometers (via manual readings with overlying tance (3 to 5 m) below top of common. Wells wells in the confined chalk aquifer in London and trial/pilot sub-section of the proposed dewatering sys- or water level dataloggers). elsewhere (Charalambous et al., 2013). It is also permeable stra- chalk, grouted into place, with slot- rarely acidised test tem is pumped. Objective is to investigate the tum (Fig 2(b)) ted well screen below. Formation effectiveness of the full system. The piezometer array should be appropriate for the common to develop such wells by injection of stabilizer filter gravel around Cut-off 1–5 d A well within the area enclosed by a cut-off hydrogeological setting. The piezometer array will concentrated hydrochloric acid, which dissolves screen, grout seal above wall pump- wall is pumped. The objective is to investi- Confined chalk Well screened in chalk only*: Wells common- ing test gate the effectiveness of the cut-off wall. typically include instruments in the range 5m up to the drilling slurry, and cleans the bore, opening aquifer Plain well liner to extend short dis- ly acidised Note: min = minute; h = hour; d = day 100m distant from the pumped well. In confined aq- blocked fissures (Banks et al. 1993). (Fig 2(c)) tance (3 to 5 m) below top of chalk, grouted into place. Well is uifers far field monitoring out to several hundred me-  In more weathered grades of chalk (structured The term ‘constant rate’ is a misnomer. If the completed as open hole below well borehole pump is not adjusted, the flow rate will tend tres or more may be required to assess off-site ef- grades B and C, and structureless grade D) bore- liner. fects. Some piezometers should also target any high holes are more likely to be unstable and slotted Note: *Where permeable strata are present above the chalk, test wells can be to reduce slightly as the drawdown in the well chang- installed with the well screen and filter gravel through both strata, with grout es the discharge head at the pump. In some cases, for permeability strata overlying the chalk. The rate of well screens are typically installed to keep the seals above. However, pumping tests in such hybrid wells can be difficult to drawdown of groundwater levels occurs rapidly, im- bore open. Well development by acidisation is usefully analyse for dewatering design purposes. example where the aquifer is bounded, and large

635 Engineering in Chalk

mediately after pumping starts, and then gradually On projects where there are potential impacts from Preene, M. Roberts, T.O.L. and Powrie, W. 2016. Groundwater ECSMFGE, Geotechnics of Hard Soils – Weak Rocks (Anagnos- slows. Typically, very frequent readings are taken in groundwater lowering (e.g. settlement, changes in Control – Design and Practice, 2nd edition. Construction Industry topoulos, A. Pachakis, M. Tsatsanifos, C.H. (eds)), IOS Press, Research and Information Association, London, UK, CIRIA Re- Amsterdam, The Netherlands, 1461-1466 early stages of pumping, becoming gradually less water chemistry, depletion of groundwater-dependent port C750. Spink, T.W. 2002. The CIRIA Chalk description and classification frequent – guidance is given in BS ISO 14686:2003 features) then relevant data from the constant rate Roberts, T.O.L. and Holmes, G. 2011. Case study of a dewatering scheme. Quarterly Journal of Engineering Geology and Hydroge- and BS EN ISO 22282-4:2012. In coastal and estua- pumping phase can be useful in the assessment of the and recharge system in weak Chalk rock. Proceedings of the XV ology 35, 363–369. rine areas, groundwater levels may be tidal and magnitude and distribution of impacts. groundwater level readings should be frequent throughout the pumping period (typically at 15 mi- nute intervals) to record tidal variations. Additional monitoring may include: 5 CONCLUSIONS  Water quality sampling  Downhole geophysical testing which can be par- Well pumping tests are widely accepted as the most ticularly useful in unlined chalk wells where data effective method of obtaining data for the design of collected under pumped conditions can help iden- construction dewatering systems. Pumping tests in tify the major inflow horizons to the well. chalk present particular challenges.  Monitoring of nearby groundwater dependent fea- The design of the test well and monitoring well ar- tures (e.g. water supply wells, wetlands, springs, ray should take account of the hydrogeological set- streams) that may be affected. ting of the chalk, which can include unconfined or A fundamental requirement for a pumping test is confined aquifers, with or without overlying granular the need to dispose of the pumped water. For most water-bearing deposits. To gain the most useful data, pumping tests in chalk the volume is too large to pumping tests for dewatering design should be gen- store on site. The water is typically discharged to sur- erally carried out at the maximum achievable flow, face watercourses or to sewer. When planning a with the well ‘over pumped’ so that drawdown in the pumping test, checks must be made that the disposal well is at or close to pump intake. route has adequate capacity, and the necessary per- missions must be obtained from the Environment Agency (discharge to watercourses or recharge) or 6 REFERENCES from regional water companies (for discharge to sewers). Banks, D. Cosgrove, T. Harker, D, Howsam, P.J. and Thatcher J.P. 1993. Acidisation: borehole development and rehabilitation. Quar- terly Journal of Engineering Geology, 26, 109–125. BS EN ISO 22282-4:2012. Geotechnical investigation and testing. 4 USE OF PUMPING TEST DATA Geohydraulic testing. Pumping tests. British Standards Institution. BS ISO 14686:2003. Hydrometric determinations. Pumping tests for water wells. Considerations and guidelines for design, perfor- The most common use of the pumping test data mance and use. British Standards Institution. (pumped flow rates and drawdown of groundwater Charalambous, A.N., Burnet, B.R and Jones, M.A. 2013. Aspects levels) is parameter assessment using classical hy- of water well design and construction in confined Chalk overlain drogeological theory. The data are analysed either by Basal Sands in the London Basin with particular reference to sand ingress. Quarterly Journal of Engineering Geology and Hy- manually or using proprietary software, and the gra- drogeology 46, 179-188. dient of the curves is used to assess the hydrogeolog- Kruseman, G.P. and De Ridder, N.A. 1990. Analysis and Evalua- ical parameters, see Kruseman and De Ridder (1994). tion of Pumping Test Data, 2nd edition. Publication 47, Interna- Alternatively, the distance-drawdown relationships tional Institute for Land Reclamation and Improvement, Wa- geningen, The Netherlands (ISBN: 978-9-07075-420-4). observed during the test can be applied directly to Preene, M. and Roberts, T.O.L. 1994. The application of pumping dewatering design by using the cumulative draw- tests to the design of construction dewatering systems. Groundwa- down method (Preene and Roberts, 1994). This can ter Problems in Urban Areas (Wilkinson, W.B. (ed)), Institution of avoid some of the complications which arise in the Civil Engineers, Thomas Telford, London, 121–133. Preene, M. and Roberts, T.O.L. 2017. Construction dewatering in treatment of aquifer boundary conditions in the de- Chalk. Proceedings of the Institution of Civil Engineers, Geotech- sign process. nical Engineering 170, 367–390.

636 Preene, Roberts and Hartwell

mediately after pumping starts, and then gradually On projects where there are potential impacts from Preene, M. Roberts, T.O.L. and Powrie, W. 2016. Groundwater ECSMFGE, Geotechnics of Hard Soils – Weak Rocks (Anagnos- slows. Typically, very frequent readings are taken in groundwater lowering (e.g. settlement, changes in Control – Design and Practice, 2nd edition. Construction Industry topoulos, A. Pachakis, M. Tsatsanifos, C.H. (eds)), IOS Press, Research and Information Association, London, UK, CIRIA Re- Amsterdam, The Netherlands, 1461-1466 early stages of pumping, becoming gradually less water chemistry, depletion of groundwater-dependent port C750. Spink, T.W. 2002. The CIRIA Chalk description and classification frequent – guidance is given in BS ISO 14686:2003 features) then relevant data from the constant rate Roberts, T.O.L. and Holmes, G. 2011. Case study of a dewatering scheme. Quarterly Journal of Engineering Geology and Hydroge- and BS EN ISO 22282-4:2012. In coastal and estua- pumping phase can be useful in the assessment of the and recharge system in weak Chalk rock. Proceedings of the XV ology 35, 363–369. rine areas, groundwater levels may be tidal and magnitude and distribution of impacts. groundwater level readings should be frequent throughout the pumping period (typically at 15 mi- nute intervals) to record tidal variations. Additional monitoring may include: 5 CONCLUSIONS  Water quality sampling  Downhole geophysical testing which can be par- Well pumping tests are widely accepted as the most ticularly useful in unlined chalk wells where data effective method of obtaining data for the design of collected under pumped conditions can help iden- construction dewatering systems. Pumping tests in tify the major inflow horizons to the well. chalk present particular challenges.  Monitoring of nearby groundwater dependent fea- The design of the test well and monitoring well ar- tures (e.g. water supply wells, wetlands, springs, ray should take account of the hydrogeological set- streams) that may be affected. ting of the chalk, which can include unconfined or A fundamental requirement for a pumping test is confined aquifers, with or without overlying granular the need to dispose of the pumped water. For most water-bearing deposits. To gain the most useful data, pumping tests in chalk the volume is too large to pumping tests for dewatering design should be gen- store on site. The water is typically discharged to sur- erally carried out at the maximum achievable flow, face watercourses or to sewer. When planning a with the well ‘over pumped’ so that drawdown in the pumping test, checks must be made that the disposal well is at or close to pump intake. route has adequate capacity, and the necessary per- missions must be obtained from the Environment Agency (discharge to watercourses or recharge) or 6 REFERENCES from regional water companies (for discharge to sewers). Banks, D. Cosgrove, T. Harker, D, Howsam, P.J. and Thatcher J.P. 1993. Acidisation: borehole development and rehabilitation. Quar- terly Journal of Engineering Geology, 26, 109–125. BS EN ISO 22282-4:2012. Geotechnical investigation and testing. 4 USE OF PUMPING TEST DATA Geohydraulic testing. Pumping tests. British Standards Institution. BS ISO 14686:2003. Hydrometric determinations. Pumping tests for water wells. Considerations and guidelines for design, perfor- The most common use of the pumping test data mance and use. British Standards Institution. (pumped flow rates and drawdown of groundwater Charalambous, A.N., Burnet, B.R and Jones, M.A. 2013. Aspects levels) is parameter assessment using classical hy- of water well design and construction in confined Chalk overlain drogeological theory. The data are analysed either by Basal Sands in the London Basin with particular reference to sand ingress. Quarterly Journal of Engineering Geology and Hy- manually or using proprietary software, and the gra- drogeology 46, 179-188. dient of the curves is used to assess the hydrogeolog- Kruseman, G.P. and De Ridder, N.A. 1990. Analysis and Evalua- ical parameters, see Kruseman and De Ridder (1994). tion of Pumping Test Data, 2nd edition. Publication 47, Interna- Alternatively, the distance-drawdown relationships tional Institute for Land Reclamation and Improvement, Wa- geningen, The Netherlands (ISBN: 978-9-07075-420-4). observed during the test can be applied directly to Preene, M. and Roberts, T.O.L. 1994. The application of pumping dewatering design by using the cumulative draw- tests to the design of construction dewatering systems. Groundwa- down method (Preene and Roberts, 1994). This can ter Problems in Urban Areas (Wilkinson, W.B. (ed)), Institution of avoid some of the complications which arise in the Civil Engineers, Thomas Telford, London, 121–133. Preene, M. and Roberts, T.O.L. 2017. Construction dewatering in treatment of aquifer boundary conditions in the de- Chalk. Proceedings of the Institution of Civil Engineers, Geotech- sign process. nical Engineering 170, 367–390.

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