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Proceedings - Balai Penelitian Tanah

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133<br />

Figure 1. Locations of assessment sites<br />

McLeod et al.<br />

In each site 1-3 permanent transects of about 100 m long each were<br />

selected based on visual assessment of crop performance (Poor,<br />

Medium and Good areas) at the initial survey in August 2005.<br />

The apparent soil electrical conductivity (ECa) was measured at 5 m<br />

intervals along each transect using the Geonic EM38 instrument. This<br />

was conducted every three months between August 2005 and<br />

January 2007. Both horizontal, EMh, (most sensitive to 0-45 cm<br />

depths) and vertical, EMv, (most sensitive to 45-150 cm depths)<br />

readings were taken at each measurement point. A higher EMh value<br />

indicates salt accumulation in the top 30-45 cm of the soil profile,<br />

while a higher EMv value indicates salt accumulation in the lower 45-<br />

150 cm of the soil profile.<br />

The site specific calibration to convert ECa data to soil electrical<br />

conductivity at field saturation (ECe) was developed following Slavich<br />

and Peterson (1993), and Slavich (2002).<br />

RESULTS AND DISCUSSION<br />

Soil salinity in the tsunami affected areas was highly variable between<br />

the assessment sites (Figure 2). It had a wide range of values and<br />

was generally higher at the soil surface (Table 1). Soil salinity reduced<br />

over time due to leaching from natural rainfall or irrigation water.<br />

However, some sites remained saline until January 2007.<br />

International Workshop on Post Tsunami Soil Management, 1-2 July 2008 in Bogor, Indonesia

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