 
          2918
        
        
          Proceedings of the 18
        
        
          th
        
        
          International Conference on Soil Mechanics and Geotechnical Engineering, Paris 2013
        
        
          maximum height of 5.2m. The values of the end of primary
        
        
          settlement (
        
        
          ρ
        
        
          
            f
          
        
        
          ) and c
        
        
          
            v
          
        
        
          /
        
        
          
            H
          
        
        
          
            2
          
        
        
          
            d
          
        
        
          were determined from instrumental
        
        
          data for the two loading stages. The authors interpreted
        
        
          measurement to find equivalent
        
        
          
            c
          
        
        
          
            v
          
        
        
          values, after roughly 5
        
        
          months when at least 95% of the primary settlement was
        
        
          reached. In the third experimental fill, with a maximum hight of
        
        
          6.7, they also inferred c
        
        
          v
        
        
          values from instrumental observations.
        
        
          A third experimental fill (Pilot Embankment 3), built also in
        
        
          Area 3, with a maximum height of 6.7m, behaved in a similar
        
        
          way, with c
        
        
          
            v
          
        
        
          /
        
        
          
            H
          
        
        
          
            2
          
        
        
          
            d
          
        
        
          averaging 1.8.10
        
        
          -2
        
        
          /day; the
        
        
          
            EOP
          
        
        
          settlement
        
        
          was ~80 cm and 95% of this value was reached after ~6 month.
        
        
          Due to the relatively high
        
        
          
            OCR
          
        
        
          values of the SFL Clays, the
        
        
          
            c
          
        
        
          
            v
          
        
        
          were also high, of the order or 10
        
        
          -2
        
        
          cm
        
        
          2
        
        
          /s. As a consequence,
        
        
          there was no need to use geodrains in the Embraport site.
        
        
          This conclusion was supported by  instrumental observations
        
        
          in three experimental earth fills without geodrains and, more
        
        
          important, by the monitoring of settlements in the area where
        
        
          temporary surcharges were used. These results show that
        
        
          controversies that after arise about the use of geodrains can be
        
        
          overcome with proper characterization of soils present in the
        
        
          field and from thorough and careful interpretation of
        
        
          instrumental observations from properly instrumented trial fills.
        
        
          The paper by Ooi
        
        
          
            et al.
          
        
        
          (2013) discusses the development of
        
        
          geogrid applications in soft ground in Malaysia starting in 1984
        
        
          when a road pavement field trial was first carried out. Other
        
        
          experiences followed in the following years and in this paper
        
        
          they report another project in which geogrids with geocells were
        
        
          used. They compare the performance of three cases in which
        
        
          geogrids were used, a fabrication yard, a heavy duty working
        
        
          platform and a container yard working platform. They compare
        
        
          and assess the pavements used in them and the magnitude of
        
        
          settlement they underwent under construction and later
        
        
          operations. All the three platforms were built over soft clays 4.5
        
        
          to 10m thick and applied stresses due to heavy equipment was
        
        
          as high as 500kPa and axial loads of heavy vehicles reached
        
        
          105tonnes. Granular fill of varying thicknesses were used in all
        
        
          three working platforms. The authors state that mechanically
        
        
          stabilized soils using biaxial and triaxial geogrids with granular
        
        
          fill with or without geocell mattress performed satisfactorily in
        
        
          terms of platform settlement performances to support the
        
        
          heavily loaded platforms.
        
        
          The case history presented by Asiri and Masakasu (2013)
        
        
          deals with the design and performance of a highway
        
        
          embankment constructed in Sri Lanka over very soft soils and
        
        
          alluvial clays. The project required that settlements be limited to
        
        
          less that 15cm after three years and those residual differential
        
        
          settlements be less than 0.3%.  Soils were improved by means
        
        
          of wick drains, heavy tamping, pre loading with surcharges and
        
        
          vacuum consolidation. The soil improvement method was
        
        
          adjusted depending local geotechnical conditions. The major
        
        
          steps in ground improvement method and illustrated in Fig 3
        
        
          are: a) placing surcharge loads with or without drains for soft
        
        
          clays of shallow thickness; b) removal of peaty soil, replacing it
        
        
          rock fragments; c) applying heavy tamping or, alternatively,
        
        
          vacuum consolidation for deeper strata. Heavy tamping was
        
        
          only effective down to 3.5 to 4.0m
        
        
          Figure 3. Major steps in heavy tamping ground improvement method
        
        
          (Asiri and Masakasu , 2013)
        
        
          Vacuum consolidation was applied using band drains with a
        
        
          spacing of 1m. Primary consolidation settlements were
        
        
          compensated and secondary consolidation deformation
        
        
          minimized by applying a vacuum pressure of 70kPa. There were
        
        
          places where it was not possible to apply vacuum and in those
        
        
          cases, soil improvement was carried out by applying surcharge.
        
        
          The continuous assessment of the improvement of soft
        
        
          ground was carried with field instruments: settlement plates,
        
        
          pyrometers, a vacuum pressure monitoring unit and a water
        
        
          discharge meter. The decision to remove the surcharge was
        
        
          made on the basis of the monitoring data obtained during the
        
        
          surcharge period. The aim was to eliminate 100% of the
        
        
          primary consolidations settlement and enough secondary
        
        
          settlement.
        
        
          De Silva and Fong (2013) describe and discuss the case of
        
        
          the Cotai Landfill, the main receiving facility in Macau for
        
        
          building construction waste.  As the dumping site is underlain
        
        
          with a thick layer of very soft to soft marine clay deposits, the
        
        
          uncontrolled end-tipped material has generated mud waves and
        
        
          they were encroaching the piles supporting the Macau
        
        
          International Airport taxiway nearby. In order to prevent future
        
        
          potential damage to the taxiway, the Macau Government
        
        
          commissioned the design of a containment bund adjacent to the
        
        
          taxiway to retain the waste and to prevent further generation of
        
        
          mud waves that would affect the taxiway.
        
        
          This paper presents the design approach of the containment
        
        
          bund including the results of a limit equilibrium stability
        
        
          analysis and the numerical analyses carried out that
        
        
          demonstrated that the solution is appropriate as the bund will
        
        
          contain the landfill with minimal impact on the taxiway bridge
        
        
          piles. The analyses also demonstrated that the impacts during
        
        
          construction are also negligible. The sustainable design
        
        
          comprised the installation of vibrocompacted stone columns
        
        
          installed in over 20m thick, very soft to firm, moderately
        
        
          sensitive marine clay and alluvial clay, as the foundation to the
        
        
          waste retention bund, thereby avoiding the dredging and off-site
        
        
          disposal of a significant volume of dredged sediments. This
        
        
          paper presents the design approach and construction of the stone
        
        
          columns and the behaviour of the completed seawall.
        
        
          The authors show instrumental observations to monitor
        
        
          during the taxiway and seawall during construction. Survey
        
        
          results indicated that the installation of the stone columns and
        
        
          construction of the bund had minimal impact on the taxiways
        
        
          foundation piles. The seawall was been completed in November
        
        
          2011.
        
        
          6
        
        
          SOIL FRACTURING
        
        
          Auvinet and Mendez (2013) present updated information
        
        
          concerning land subsidence and associated soil fracturing in
        
        
          Mexico City. Subsidence was estimated from the evolution of
        
        
          the elevations of 2064 benchmarks and other references located
        
        
          in former Texcoco Lake. Geodesic and topographic surveys
        
        
          carried out in the middle of the XIX
        
        
          th
        
        
          century proved to
        
        
          constitute an excellent initial reference for subsequent
        
        
          measurements of land subsidence. Extensive use was made of
        
        
          new geocomputing tools to process these data. Results of
        
        
          surveys of soil fracturing associated to subsidence are also
        
        
          presented and discussed
        
        
          The demographic development in Mexico City has created
        
        
          an accelerated demand of services, mostly of potable water. One
        
        
          of the cheapest ways to meet this demand has been the
        
        
          exploitation of the local aquifer by pumping water from deep
        
        
          wells. This has produced a water pressure drawdown in the
        
        
          subsoil that in turn is causing general subsidence of the former
        
        
          lacustrine area and soil fracturing. This problem has been
        
        
          around for almost a century but is now reaching new worrying
        
        
          dimensions. Although regional land subsidence is an old
        
        
          phenomenon, it has not been possible to control it. In fact, it is
        
        
          expected to continue in the future for many more years since,
        
        
          due to the high cost of other alternatives, water pumping from