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Field study at Kakinada Port

First field trial of vacuum consolidation in India was carried out by Kumar et al. (2015) [27]

in Kakinada soft clay deposits. The foundation soil in this region is characterized by the presence of thick layers of soft marine clay deposits. In view of increasing demand for development of fertilizer plants and ports, a need for ground improvement was sought. A square area of 10 m x 10 m was considered for study. Because of cyclonic disturbances the test could not be conducted beyond 28 days [27]. It was observed that the settlements obtained after 28 days of vacuum pressure application were less than those expected from laboratory studies. Many parameters like pore pressure, lateral displacement, and loss of vacuum pressure in the field could not be measured; however, if predicted, can be of great help in studies of soft clay deposits. In this study, Plaxis 2D software is used to model the field trial and the numerical results obtained have been compared with the field data.

General Description of Site Conditions and Soil Characteristics

The site of field trial is located at Kakinada coast, Andhra Pradesh, India. Standard Penetration Test results showed that the first 3m of the soil strata was fine sand (Figure 4.1), followed by 10.5 m of very soft marine clay with SPT value 1 and natural water content of

84% [27]. Soil below 14m was very stiff clay with SPT value of 50. Ground water table was present at 0.5m below the ground level. Study of undisturbed core samples collected at the depth of 10.5m showed that the marine oft soil was found to be fine grained and classified as OH soil as per Indian Soil Classification System and Rao et al. (2011) [33]. The soil properties mentioned in the referred literature and adopted or calculated from given data are presented in Table 5.1.

Figure 4.1: Soil profile of treatment area Table 4.1: Adopted model parameters for the study

Property Unit Value

Unsaturated unit weight# γunsat (kN/m³) 16.00

Saturate unit weight# γsat (kN/m³) 16.00

Initial void ratio einit 1.76

Modified compression index## λ* 0.09450

Modified swell index## κ* 0.01120

Compression index Cc 0.6

Recompression index Cr 0.083

Secondary compression index Cs 0.036

Cohesive strength# cref (kN/m²) 3.5

Angle of internal friction# Φ (°) 2.0 Coefficient of horizontal permeability## kx (m/day) 3.615E-05 Coefficient of vertical permeability## ky (m/day) 6.245E-05

# assumed ## calculated from available data

4.3 2d Plane Strain Finite Element Model

The geometry of field trial was simulated using the finite-element software PLAXIS 2D.

The soil properties obtained from the laboratory tests (Table 5.2) along with the adopted properties were used to model the behavior of the test section. Soft soil model has been considered for the clay layer. Material properties have been defined in terms of effective stiffness and effective strength parameters. Undrained behavior has been assumed for soft clay layer. Fully coupled flow deformation is employed to analyze the given soil model with unsaturated soil condition. A fully coupled flow deformation is conducted when it is necessary to analyze the simultaneous development of deformations and pore pressures in saturated and partially saturated soils as a result of time-dependent changes of the hydraulic boundary conditions. The model has been set-up in plane strain situation using 15-nodes triangular elements which provide a high order of displacement and pore pressure interpolation.

Figure 4.2: Boundary Convergence Study for development of 2D model

Boundary convergence study was carried out to decide the extent of the horizontal boundaries of the model (Figure 4.2). After the distance between two boundaries exceeded 100m, no significant change in settlement was observed. So, soil model of width 100m and depth 18m was created in PLAXIS 2D including a 4.5m of stiff clay layer below the marine clay layer to maintain one-way drainage. Vacuum preload was modelled in an area 10m wide at the center of the model. The PVDs were modelled as drain elements. The PVDs were modelled as linear drain elements. A drain blanket of 0.2m height is provided over vacuum treatment area.

Table 4.2: Sensitivity study of 2D model in PLAXIS 2D

Mesh refinement

Relative element size

factor (re’)

Coarseness factor

no. of elements

no. of nodes

settlement at 300 days (mm)

ultimate settlement (mm)

very coarse 2 0.25 817 6723 500.2 601.9

coarse 1.5 0.25 826 6813 500.6 602.4

medium 1 0.25 857 7079 501 603

fine 0.67 0.25 1186 9761 502.14 604.7

Sensitivity study was conducted to analyze the effect of element size and on results. Four types of mesh were generated: Very Coarse, Coarse, Medium and Fine. Fineness of mesh is varied by changing Relative Element Size Factor (re). Values for this parameter are given in Table 3.

Figure 4.3: 2D Finite Element Mesh generated for the analysis

Another parameter called Coarseness Factor is used to refine the mesh locally at drains.

Finer meshes are helpful when the behavior of very closely situated points is to be studied.

It was found that the settlement was same for all the four types of meshes. Fine coarseness was finally adopted and the mesh is shown in Figure 4.3. The vacuum pressure is specified by the negative water head along the length of the drains (a reduction of groundwater head of 10m signifies under-pressure of 100kN/m2, i.e. complete vacuum). To apply saturated conditions in the soil volume, the unsaturated unit weight was made equal to the saturated unit weight. Otherwise, reduction in groundwater head in vertical drains would drop the phreatic level, thus resulting into change in unit weight of soil. Nodal point to calculate displacement was selected at the center of treatment area. Stress point for stresses and pressures was selected at the center of treatment area at mid depth of clay layer very near to the drain and also between two adjacent drains. The left and right flow boundaries were kept open. Bottom flow boundary was closed to seepage to maintain undrained conditions.

4.4 Results and Discussions

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