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an engineering geological characterisation of tropical clays - GBV

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209<br />

cc = 0,0099(122-LL)<br />

for black <strong>clays</strong>, <strong>an</strong>d<br />

cc = 0,0016(308-LL)<br />

for both black <strong>clays</strong> <strong>an</strong>d red soils, where<br />

cc = a dimensionless number, <strong>an</strong>d<br />

LL (%) = liquid limit<br />

Correlation between so calculated compression indices <strong>an</strong>d laboratory measured compression<br />

indices were found to be strong (R = 0,85) for the black <strong>clays</strong> alone; <strong>an</strong>d moderate (R = 0,58)<br />

for combined black <strong>clays</strong> <strong>an</strong>d red soils. However, these derivations were based on a limited<br />

amount <strong>of</strong> data on compression indices (n = 6 for black <strong>clays</strong>; n = 9 for black <strong>clays</strong> <strong>an</strong>d red<br />

soils) available in the current study. It would be useful that future works attempt the same<br />

correlations <strong>an</strong>d derivations based on a larger amount <strong>of</strong> data as regards laboratory results <strong>of</strong><br />

liquid limit tests performed on disturbed samples on one h<strong>an</strong>d, <strong>an</strong>d those <strong>of</strong> compression<br />

indices obtained from oedometer tests on undisturbed specimens on the other. Possible<br />

improvements in the strength <strong>of</strong> correlations <strong>an</strong>d assessment <strong>of</strong> compressibility characteristics<br />

<strong>of</strong> soils using index properties (Atterberg limits) would also be indicated. Investigations could<br />

also be extended to other types <strong>of</strong> soil world-wide, to find out if the same <strong>an</strong>d/ or similar<br />

relationships hold.<br />

All in all, it may be useful to initiate <strong>an</strong>d establish a field monitoring program for the soils <strong>of</strong><br />

the Nairobi area, aimed at monitoring <strong>of</strong> exp<strong>an</strong>sive/ reactive soil movements <strong>an</strong>d moisture<br />

ch<strong>an</strong>ges. The selected sites would involve soils <strong>of</strong> varying geographic <strong>an</strong>d lithological<br />

conditions. This would serve the purpose <strong>of</strong> providing a comprehensive picture <strong>of</strong> exp<strong>an</strong>sive<br />

<strong>an</strong>d/ or reactive soil behaviour, in terms <strong>of</strong> <strong>characterisation</strong> <strong>of</strong> site reactivity (shrink-swell<br />

potential) <strong>an</strong>d unsaturated moisture flow. The scheme my take the form <strong>of</strong> monitoring <strong>an</strong>d<br />

recording pr<strong>of</strong>iles <strong>of</strong> ground movements <strong>an</strong>d moisture ch<strong>an</strong>ges as well as providing general<br />

data on soils with time (e.g. on a monthly basis), over a period <strong>of</strong> some years. A further<br />

<strong>an</strong>alysis in terms <strong>of</strong> environmental factors would be necessary <strong>an</strong>d helpful.<br />

According to Del<strong>an</strong>ey & Allm<strong>an</strong> (1998), useful instrumentation for a field monitoring<br />

program may include use <strong>of</strong> surface <strong>an</strong>d sub-surface pegs (surface <strong>an</strong>d sub-surface levels),<br />

neutron probes (soil volumetric moisture content), thermocouples (soil temperature), gypsum<br />

blocks (matrix soil suction), piezometer (groundwater level, especially in alluvial soils),<br />

automatic weather stations (rainfall, humidity, temperature, solar radiation, wind velocity/<br />

direction) etc. Results may include data on design parameters for foundations on exp<strong>an</strong>sive<br />

<strong>an</strong>d/ or reactive soils (e.g. active depth, suction ch<strong>an</strong>ge, seasonal heave etc.), as well as<br />

detailed information on field behaviour to compare with models which may be developed in<br />

the laboratory to simulate <strong>an</strong>d characterise possible field behaviour <strong>of</strong> the soils. The results<br />

would also provide a basis for comparing <strong>an</strong>d assessing the different methods <strong>of</strong><br />

characterising site reactivity <strong>an</strong>d/ or shrink-swell behaviour.<br />

The first <strong>of</strong> the two methods developed in this study to estimate swelling characteristics <strong>of</strong><br />

black <strong>clays</strong> [i.e. Eq. (7.49): P = -22,3Ln(S) + 100,8] was shown to be limited in predicting<br />

percentage swelling that may be realised under selected structural loading conditions. It was<br />

also explained that the underestimation <strong>of</strong> percentage swelling values was most probably a<br />

result <strong>of</strong> some degree <strong>of</strong> plastic deformation (or consolidation <strong>of</strong> test specimens when initially

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