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Vol. 35 – 2009 - Ecologia Mediterranea - Université d'Avignon et des ...

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MUSTAPHA DADDI BOUHOUN, LOUHICHI BRINIS, MOHAMED LAKHDAR SAKER, MARC COTE, JACQUES RABIER<br />

44<br />

Date palms rooting study<br />

In absence of a mechanical probe for sampling<br />

and a study of tree root depth (R.d.) like<br />

that of field cultures (Hansson 1987), we used<br />

a m<strong>et</strong>hod of measurement based on a progressive<br />

survey of Degl<strong>et</strong> Noor date palm rooting<br />

since 85% of the root are distributed in<br />

the zone of 2 m deep and 2 m on both lateral<br />

si<strong>des</strong> (Munier 1973; Zaid 2002). We used a<br />

manual drill of 150 cm depth and a scale.<br />

This m<strong>et</strong>hod consisted in measuring rooting<br />

up to 120 cm of depth, at 80 cm far from the<br />

trunk, with a gradual survey up to 150 cm of<br />

depth to confirm an absence of roots beyond<br />

120 cm. For each farm, we carried out three<br />

random measurements of rooting on adult<br />

date palms in full production to calculate average<br />

maximum depth of rooting. Root depths<br />

were classified in four groups; 0-40 cm, 40-<br />

80 cm, 80-120 cm and higher than 120 cm of<br />

depth.<br />

Statistical analysis<br />

Groups of depth range for roots and water<br />

tables were chosen for practical reasons.<br />

Several grouping of observations for the 167<br />

farms were formed according the tested hypotheses.<br />

The hypotheses were that low water<br />

table or crusts depth alone or in combination<br />

limit root growth. Means and standard deviations<br />

for subgroups of palm areas are shown<br />

in Table 1. Preliminary results of regression<br />

analyse obtained for the whole group or by<br />

group of palm areas which gave a higher<br />

number of outliers and lower d<strong>et</strong>ermination<br />

coefficients are not shown. Means, standard<br />

deviations, regression analyse and d<strong>et</strong>ermination<br />

coefficient (R 2 ) were performed with<br />

Excel 2004 software.<br />

Results<br />

The synth<strong>et</strong>ic results (Table 1) showed that<br />

the hydro-edaphic environment in the Ouargla<br />

basin was degraded. The groundwater<br />

levels had serious effects on rooting of date<br />

palms and physico-chemical soils degradation<br />

by waterlogging, gypseous crusts formation<br />

and soils’ salinization.<br />

Hydro-edaphic study<br />

In this study, 53.9% of the palm plantations<br />

showed a shallow water table, lowers than<br />

1.2 m of depth, varying from 29 to 119.4 cm<br />

(Figure 2). According to the USSL classification<br />

(1954), modified by Durand (1958), salinity<br />

degree of groundwater varied b<strong>et</strong>ween<br />

Table 1 <strong>–</strong> Synth<strong>et</strong>ic results showing means with standard deviations in the date palm areas of Ouargla Basin.<br />

Area types Date palm farms W.t.d. E.C. w.t. E.C. e1:5 E.C. i.w. G.c.d. R.d.<br />

areas numbers (cm) (dS.m-1 ) (dS.m-1 ) (dS.m-1 ) (cm) (cm)<br />

Deep water tables Bamendil 3 > 120 - 4.0 ± 0.7 2.20 ± 0.06 65 ± 27 65 ± 26<br />

with gypseous crusts Beni Thour 1 > 120 - 5.8 ± 0 4 ± 0 73 ± 0 72 ± 0<br />

Ksar 1 > 120 - 4.7 ± 0 4 ± 0 111 ± 0 114 ± 0<br />

Total 5 > 120 - 4.5 ± 0.9 2.8 ± 0.9 76 ± 28 76 ± 28<br />

Deep water tables Bamendil 15 > 120 - 2 ± 1 2.2 ± 0.1 - > 120<br />

without gypseous crusts Beni Thour 3 > 120 - 3 ± 1 3.63 ± 0.08 - > 120<br />

Ksar 8 > 120 - 2.8 ± 0.6 2.0 ± 0.2 - > 120<br />

Mekhadma 18 > 120 - 3.1 ± 0.6 2.6 ± 0.6 - > 120<br />

Said Otba 28 > 120 - 2.4 ± 0.7 4 ± 1 - > 120<br />

Total 72 > 120 - 2.6 ± 0.8 3 ± 1 - > 120<br />

Shallow water tables Bamendil 11 65 ± 27 15 ± 4 4.87 ± 1.83 2.4 ± 0.7 69 ± 17 70 ± 28<br />

with gypseous crusts Beni Thour 1 97 ± 0 18 ± 0 2.92 ± 0 2.3 ± 0 80 ± 0 101 ± 0<br />

Ksar 3 83 ± 25 23 ± 9 5.11 ± 0.8 4 ± 1 81 ± 31 86 ± 23<br />

Mekhadma 3 61 ± 48 16 ± 4 5.58 ± 2.3 2.7 ± 0.8 62± 47 63 ± 45<br />

Total 18 69 ± 30 17 ± 5 5 ± 2 2.7 ± 0.9 70 ± 24 73 ± 30<br />

Shallow water tables Bamendil 15 66 ± 36 18 ± 6 6 ± 2 3 ± 1 - 67 ± 31<br />

without gypseous crusts Beni Thour 11 68 ± 33 21 ± 8 6 ± 1 3 ± 1 - 79 ± 34<br />

Ksar 13 61 ± 29 21 ± 7 6 ± 1 3 ± 1 - 68 ± 27<br />

Mekhadma 27 65 ± 30 23 ± 8 6 ± 2 3 ± 1 - 78 ± 32<br />

Said Otba 6 77 ± 27 21 ± 7 5.7 ± 0.9 3.3 ± 0.7 - 87 ± 29<br />

Total 72 66 ± 31 21 ± 7 6 ± 1 3 ± 1 - 74 ± 31<br />

ecologia mediterranea <strong>–</strong> <strong>Vol</strong>. <strong>35</strong> <strong>–</strong> <strong>2009</strong>

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