
Photograph captioned by Fairfax, "Judy Lawn carting liquefaction off her friends property damaged on an unstable part of Locksley Avenue in Dallington".
An abandoned residential property on Seabreeze Close in Bexley. The front yard and footpath are covered with weeds and silt from liquefaction.
A woman walks through liquefaction in Hendon Street in St Albans. The photographer comments, "Hendon St, St Albans, is very heavily silted".
Liquefaction and flooding on Chichester Street, after the September 4th earthquake. A chimney fallen into a fence in a residential property.
Damage down a residential street. The road is covered in silt from liquefaction and a portaloo can be seen in the background.
A block of flats with carparks beneath is on a noticable lean. Liquefaction silt is piled around the base of the building.
A man pushes a wheelbarrow full of liquefaction silt in Black Street in Kaiapoi. A small sinkhole is visible in the foreground.
Flooding and liquefaction surround a house in Richmond. Bricks have fallen from the walls of the house, exposing the wooden framework beneath.
Photograph captioned by BeckerFraserPhotos, "New Brighton Road".
Road cones and portaloos along Avonside Drive.
The empirical liquefaction triggering chart of Idriss and Boulanger (2008) is compared to direct measurements of the cyclic resistance of Christchurch silty sands via undisturbed and reconstituted lab specimens. Comparisons suggest that overall there is a reasonable agreement between the empirical triggering curve and the interpreted test data. However, the influence of fines on cyclic resistance appears to be over-predicted by the empirical method, particularly for non-plastic silty sands that are commonly encountered in flood over-bank deposits in Christchurch and nearby settlements
As a consequence of the 2010 – 2011 Canterbury earthquake sequence, Christchurch experienced widespread liquefaction, vertical settlement and lateral spreading. These geological processes caused extensive damage to both housing and infrastructure, and increased the need for geotechnical investigation substantially. Cone Penetration Testing (CPT) has become the most common method for liquefaction assessment in Christchurch, and issues have been identified with the soil behaviour type, liquefaction potential and vertical settlement estimates, particularly in the north-western suburbs of Christchurch where soils consist mostly of silts, clayey silts and silty clays. The CPT soil behaviour type often appears to over-estimate the fines content within a soil, while the liquefaction potential and vertical settlement are often calculated higher than those measured after the Canterbury earthquake sequence. To investigate these issues, laboratory work was carried out on three adjacent CPT/borehole pairs from the Groynes Park subdivision in northern Christchurch. Boreholes were logged according to NZGS standards, separated into stratigraphic layers, and laboratory tests were conducted on representative samples. Comparison of these results with the CPT soil behaviour types provided valuable information, where 62% of soils on average were specified by the CPT at the Groynes Park subdivision as finer than what was actually present, 20% of soils on average were specified as coarser than what was actually present, and only 18% of soils on average were correctly classified by the CPT. Hence the CPT soil behaviour type is not accurately describing the stratigraphic profile at the Groynes Park subdivision, and it is understood that this is also the case in much of northwest Christchurch where similar soils are found. The computer software CLiq, by GeoLogismiki, uses assessment parameter constants which are able to be adjusted with each CPT file, in an attempt to make each more accurate. These parameter changes can in some cases substantially alter the results for liquefaction analysis. The sensitivity of the overall assessment method, raising and lowering the water table, lowering the soil behaviour type index, Ic, liquefaction cutoff value, the layer detection option, and the weighting factor option, were analysed by comparison with a set of ‘base settings’. The investigation confirmed that liquefaction analysis results can be very sensitive to the parameters selected, and demonstrated the dependency of the soil behaviour type on the soil behaviour type index, as the tested assessment parameters made very little to no changes to the soil behaviour type plots. The soil behaviour type index, Ic, developed by Robertson and Wride (1998) has been used to define a soil’s behaviour type, which is defined according to a set of numerical boundaries. In addition to this, the liquefaction cutoff point is defined as Ic > 2.6, whereby it is assumed that any soils with an Ic value above this will not liquefy due to clay-like tendencies (Robertson and Wride, 1998). The method has been identified in this thesis as being potentially unsuitable for some areas of Christchurch as it was developed for mostly sandy soils. An alternative methodology involving adjustment of the Robertson and Wride (1998) soil behaviour type boundaries is proposed as follows: Ic < 1.31 – Gravelly sand to dense sand 1.31 < Ic < 1.90 – Sands: clean sand to silty sand 1.90 < Ic < 2.50 – Sand mixtures: silty sand to sandy silt 2.50 < Ic < 3.20 – Silt mixtures: clayey silt to silty clay 3.20 < Ic < 3.60 – Clays: silty clay to clay Ic > 3.60 – Organics soils: peats. When the soil behaviour type boundary changes were applied to 15 test sites throughout Christchurch, 67% showed an improved change of soil behaviour type, while the remaining 33% remained unchanged, because they consisted almost entirely of sand. Within these boundary changes, the liquefaction cutoff point was moved from Ic > 2.6 to Ic > 2.5 and altered the liquefaction potential and vertical settlement to more realistic ii values. This confirmed that the overall soil behaviour type boundary changes appear to solve both the soil behaviour type issues and reduce the overestimation of liquefaction potential and vertical settlement. This thesis acts as a starting point towards researching the issues discussed. In particular, future work which would be useful includes investigation of the CLiq assessment parameter adjustments, and those which would be most suitable for use in clay-rich soils such as those in Christchurch. In particular consideration of how the water table can be better assessed when perched layers of water exist, with the limitation that only one elevation can be entered into CLiq. Additionally, a useful investigation would be a comparison of the known liquefaction and settlements from the Canterbury earthquake sequence with the liquefaction and settlement potentials calculated in CLiq for equivalent shaking conditions. This would enable the difference between the two to be accurately defined, and a suitable adjustment applied. Finally, inconsistencies between the Laser-Sizer and Hydrometer should be investigated, as the Laser-Sizer under-estimated the fines content by up to one third of the Hydrometer values.
Photograph captioned by BeckerFraserPhotos, "36 Waygreen Avenue in New Brighton, now red zoned land".
Photograph captioned by BeckerFraserPhotos, "The driveway to 16 and 18 Waygreen Avenue in New Brighton. This area is now red zoned land".
Photograph captioned by BeckerFraserPhotos, "28 Waygreen Avenue in New Brighton, now red zoned land".
Photograph captioned by BeckerFraserPhotos, "34 Waygreen Avenue in New Brighton, now red zoned land".
Photograph captioned by BeckerFraserPhotos, "12A Waygreen Avenue in New Brighton, now red zoned land".
Photograph captioned by BeckerFraserPhotos, "9 Waygreen Avenue in New Brighton, now red zoned land".
Photograph captioned by BeckerFraserPhotos, "19 Waygreen Avenue in New Brighton, now red zoned land".
Photograph captioned by BeckerFraserPhotos, "38 Waygreen Avenue in New Brighton, now red zoned land".
A tilted power pole on Avonside Drive. A portaloo and road cones can be seen in the distance.
Well-validated liquefaction constitutive models are increasingly important as non-linear time history analyses become relatively more common in industry for key projects. Previous validation efforts of PM4Sand, a plasticity model specifically for liquefaction, have generally focused on centrifuge tests; however, pore pressure transducers installed at several free-field sites during the Canterbury Earthquake Sequence (CES) in Christchurch, New Zealand provide a relatively unique dataset to validate against. This study presents effective stress site response analyses performed in the finite difference software FLAC to examine the capability of PM4Sand to capture the generation of excess pore pressures during earthquakes. The characterization of the subsurface is primarily based on extensive cone penetration tests (CPT) carried out in Christchurch. Correlations based on penetration resistances are used to estimate soil parameters, such as relative density and shear wave velocity, which affect liquefaction behaviour. The resulting free-field FLAC model is used to estimate time histories of excess pore pressure, which are compared with records during several earthquakes in the CES to assess the suitability of PM4Sand.
Photograph captioned by BeckerFraserPhotos, "New Brighton Road".
Photograph captioned by BeckerFraserPhotos, "New Brighton Road".
Photograph captioned by BeckerFraserPhotos, "New Brighton Road".
Photograph captioned by BeckerFraserPhotos, "New Brighton Road".
Two ducks in the driveway of 22 Waygreen Avenue. The section is covered with weeds and silt from liquefaction and has partly flooded.
Photograph captioned by Fairfax, "Damage from the February 22nd earthquake in Christchurch. Massive liquefaction on St Martins Road in St Martins, Christchurch".
Photograph captioned by Fairfax, "Damage from the February 22nd earthquake in Christchurch. Massive liquefaction on St Martins Road in St Martins, Christchurch".
A photograph of liquefaction covering the footpath and road on Manchester Street. The photograph was taken shortly after the 22 February 2011 earthquake.