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an engineering geological characterisation of tropical clays - GBV

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59<br />

The presence <strong>of</strong> BaO in the red <strong>an</strong>d black soils is most likely a result <strong>of</strong> contributions in the<br />

form <strong>of</strong> BaCO3 <strong>an</strong>d/ or BaSO4 as contamin<strong>an</strong>ts from industrial effluents <strong>an</strong>d/ or wastes.<br />

Fertilizers <strong>an</strong>d industrial water could also account for the presence <strong>of</strong> traces <strong>of</strong> P2O5 in both<br />

types <strong>of</strong> soil.<br />

Table 6.2. Results <strong>of</strong> chemical <strong>an</strong>alyses <strong>of</strong> black <strong>clays</strong> obtained in this study.<br />

Content SA2- SA2- SA41- SB1- SB1- SB41- SB41- SC17- SC41- SC41-<br />

<strong>of</strong> (%): 70cm 105cm 50cm 50cm 70cm 30cm 50cm 50cm 30cm 50cm<br />

SiO2 52,50 51,40 58,35 52,79 53,44 52,64 53,21 56,38 52,06 53,71<br />

Al2O3 14,71 14,93 13,37 12,74 12,84 12,14 12,20 11,87 12,06 11,77<br />

Fe2O3 8,66 8,85 6,98 6,90 6,96 6,67 6,75 6,20 6,49 6,10<br />

FeO - - - - - - - - - -<br />

BaO 0,052 0,052 0,031 0,062 0,062 0,064 0,062 0,085 0,123 0,104<br />

MgO 1,25 1,22 1,13 1,16 1,23 1,43 1,42 1,28 1,34 1,31<br />

CaO 1,28 4,29 1,28 1,54 2,01 2,61 2,32 1,47 1,64 1,48<br />

Na2O 1,06 1,04 0,69 0,71 0,76 0,50 0,56 0,82 0,90 0,89<br />

K2O 1,78 1,73 1,25 1,27 1,34 1,02 1,04 1,41 1,32 1,31<br />

P2O5 0,026 0,024 0,037 0,032 0,038 0,038 0,038 0,047 0,036 0,04<br />

ZrO2 0,092 0,091 0,085 0,091 0,092 0,078 0,078 0,072 0,073 0,072<br />

TiO2 0,96 0,95 0,90 0,76 0,75 0,77 0,77 0,75 0,79 0,77<br />

MnO 0,312 0,363 0,249 0,455 0,439 0,497 0,505 0,488 0,469 0,511<br />

SO3 - - - - - - - 0,011 0,028 0,016<br />

Cl 0,065 0,039 - - - - - - 0,015 0,015<br />

F 0,262 0,362 0,247 0,294 0,325 0,281 0,267 0,311 0,300 0,293<br />

Loss on - - - - - - - - - -<br />

ignition<br />

Total 83,01 85,34 84,60 78,80 80,29 78,74 79,22 81,19 77,64 78,39<br />

SA2-70cm, SA2-105cm, SA41-50cm, SB1-50cm, SB1-70cm, SB41-30cm, SB41-50cm, SC17-50cm, SC41-<br />

30cm <strong>an</strong>d SC41-50cm are black clay samples.<br />

The total sum <strong>of</strong> the various chemical components <strong>of</strong> the black <strong>clays</strong> add up to only 77,64 –<br />

85,34% (Table 6.2), <strong>an</strong>d not 100%. This is a relatively large difference which could be partly<br />

accounted for by the presence in the soils <strong>of</strong> accessory amounts <strong>of</strong> heavy metal compounds,<br />

light <strong>an</strong>d noble elements; <strong>an</strong>d partly by the loss on ignition <strong>of</strong> org<strong>an</strong>ic matter components. The<br />

difference is comparatively small <strong>an</strong>d negligible in the red soils (Table 6.1) in which the total<br />

sum <strong>of</strong> the chemical components is virtually 100%, probably due to the relatively low <strong>an</strong>d/ or<br />

negligible org<strong>an</strong>ic content (Table 6.7).<br />

6.3 X-ray diffraction (XRD) studies<br />

6.3.1 Scope <strong>an</strong>d method<br />

X-ray diffraction studies <strong>an</strong>d <strong>an</strong>alyses were carried out in the present work to determine the<br />

mineralogical composition <strong>of</strong> the black <strong>clays</strong> <strong>an</strong>d red soils. Clay minerals present were<br />

identified by their characteristic diffraction patterns.<br />

A diffractometer (Type PW1710-Basis) was used to determine the presence <strong>of</strong> clay minerals<br />

which include smectites ( montmorillonite), kaolinite <strong>an</strong>d illite. This was done for selected<br />

conditions <strong>of</strong> continuous sc<strong>an</strong>ning rate <strong>of</strong> 0,020 (° 2θ/second), chart speed 0,10 (mm/ second)<br />

<strong>an</strong>d using Cu-Kα radiation. The clay minerals were X-rayed from prepared clay fractions (

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