18-Geol-B3 Site Investigation · May 2018
Nivaar worked solution (AI-drafted; not reviewed by a licensed engineer)
National Exams, May 2018 — 04-Geol-B3, Site Investigation (3 hours, open book, 4 questions × 25 marks = 100 marks, essay format).
Reference texts: Clayton, Matthews & Simons, Site Investigation, 2nd ed. (Blackwell Science); Canadian Geotechnical Society, Canadian Foundation Engineering Manual (CFEM), 4th ed.; Hunt, Geotechnical Engineering Investigation Handbook, 2nd ed. (CRC Press); Dunnicliff, Geotechnical Instrumentation for Monitoring Field Performance; Freeze & Cherry, Groundwater; EGBC Geoscience Professional Practice Guidelines; ASTM D1586 (SPT), D1587/D6519 (Shelby tube), D3441/D5778 (CPT/CPTu), D2573 (field vane), D4719 (pressuremeter), D1194 (plate load), D5731 (point load index), D4630 (packer/Lugeon), D5092/D5787 (monitoring well/piezometer construction).
Question text not reproduced: the examination questions are © Engineers and Geoscientists BC. Open the official past paper (linked at the top of this page) to read the question, then follow the worked solution below.
The groundwater mechanisms, investigation factors, field-program organization and piezometer guidance below are generic to any site's groundwater characterization and do not depend on the specific project framing, so the answer restates that content, freshly worded, rather than re-deriving it from first principles.
Groundwater governs ground behaviour through several distinct physical mechanisms, not merely as a static "water level" to be recorded on a log:
A groundwater investigation must establish several distinct pieces of information, each feeding a different part of the design: the static water table elevation and its seasonal fluctuation range (excavation dewatering and buoyancy checks are governed by the worst-case high level, not a single reading); the number and continuity of aquifer units and any perched water above a low-permeability layer, easily mistaken for the true regional water table if only shallow points are monitored; the hydraulic conductivity of each unit, governing dewatering rate, seepage into excavations, and (where relevant) contaminant transport velocity; the flow direction and gradient, which needs at least three non-collinear monitoring points to compute rather than assume; any artesian or confined condition, since a confined aquifer under pressure can drive a base heave/blow-out failure if not identified before dewatering design; groundwater chemistry (sulphate/chloride content affecting concrete and steel durability, and contamination status affecting arisings disposal); and how the water regime interacts with the specific soil/rock units already identified at the site.
The field program is built around a network of monitoring wells and/or piezometers, supplemented by in-situ permeability testing. The desk study and reconnaissance first identify the likely aquifer units and expected depth to water, setting target completion depths; monitoring points are then sited to span each distinct water-bearing unit identified in the stratigraphy and to form a spatial pattern — a minimum of three non-collinear points, and more where the footprint is large or the stratigraphy is complex — so that a flow direction and gradient can actually be triangulated rather than assumed. Equipment typically required includes the drilling rig (auger, mud-rotary, or sonic, chosen to avoid cross-contaminating separate aquifers during advance), well casing and screen (slotted PVC or steel sized to the formation's grain size, with a filter-sand pack and a bentonite seal above the screen to prevent surface water short-circuiting down the annulus), a water-level indicator (electronic dip meter) for manual monitoring rounds, and, where continuous records are needed, a data logger/pressure transducer left in the well; in-situ permeability is obtained from slug tests, packer (falling-head) tests, or short pumping tests where a larger-scale conductivity estimate is required. In setting the borehole spacing and distribution, the governing factors are: adequate number and layout of points for gradient triangulation and for separately monitoring each aquifer unit; screened-interval placement matched to the specific unit being read (a well screened across two units gives a meaningless composite level); proper sealing between units so the borehole itself does not create a new vertical flow path; and a monitoring duration long enough to capture the seasonal high, not a single snapshot.
A piezometer measures pore-water pressure (and, from it, hydraulic head) at a specific, discrete point or depth, as distinct from a standard monitoring well, which is typically screened over a longer interval and reads a composite level; in stratified ground with vertical head gradients between units, a single "water table" reading from a long-screen well is not physically meaningful. Piezometers should be installed: at each distinct soil/rock unit where a discrete pore-pressure reading is needed for a stability or settlement analysis (within a potential slip surface for a cut-slope stability check, or within a compressible layer to monitor consolidation-driven pore-pressure dissipation during staged construction); above and below a low-permeability layer to detect and quantify a vertical head difference between perched and regional water; near a proposed excavation or dewatering zone to monitor drawdown response during construction; and, for longer-term monitoring of a critical structure, at multiple depths within a single borehole (a nested/multi-level installation) so the vertical head profile is captured directly rather than inferred. Standpipe (Casagrande) piezometers suit more permeable soils where response time is fast and simple manual dip readings are adequate; pneumatic or vibrating-wire piezometers are preferred in low-permeability clay, or wherever a fast response time and remote/continuous readout are needed, since a standpipe in clay can take days to equilibrate after installation.
| Item | Answer |
|---|---|
| 4(a) | Effective-stress reduction, buoyancy/uplift, seepage force/piping, softening/collapse, swelling/shrinkage, frost action, dewatering-induced consolidation, liquefaction, and chemical (sulphate/corrosion/contaminant-transport) mechanisms |
| 4(b) | Water table level and seasonal range, aquifer continuity/perched water, hydraulic conductivity, flow direction/gradient, artesian/confined conditions, chemistry, interaction with the identified soil/rock units |
| 4(c) | Desk study sets target depths; ≥3 non-collinear points per unit for gradient; rig, casing/screen, filter pack, seal, water-level indicator, data logger; slug/packer/pumping tests for K; spacing set by gradient/unit-separation needs |
| 4(d) | Discrete point/depth pore pressure (vs. composite well reading); install within slip surfaces/consolidating layers, above & below aquitards, near excavations, and as nested multi-level installations for the vertical head profile |