Vol. 35 – 2009 - Ecologia Mediterranea - Université d'Avignon et des ...
Vol. 35 – 2009 - Ecologia Mediterranea - Université d'Avignon et des ...
Vol. 35 – 2009 - Ecologia Mediterranea - Université d'Avignon et des ...
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HANADI ISMAÏL, HUSSEIN ABOU-HAMDAN, AHMAD KOUBAYSSI, STÉPHANIE FAYOLLE, GABY KHALAF, ARLETTE CAZAUBON, JACQUES HAURY<br />
34<br />
High values for conductivity and TDS for all<br />
studied stations are linked to high imputs of<br />
organic compounds and mineral nutrients in<br />
these sations. However, conductivity and TDS<br />
content in were lower in L1 and L4 than in L2<br />
and L3. Thus L2 and L3 are much more mineralized<br />
than L1 and L4: (Tables 1a, b).<br />
Nitrate concentrations are high but below the<br />
permissible limit in drinking water (Nisb<strong>et</strong> &<br />
Vernaux 1970 <strong>–</strong> EU requirements), except for<br />
station L2 where values exceeded 50 mg/L.<br />
Phosphate and nitrite increased also considerably<br />
in station L2 which is more severely<br />
polluted than the other stations. The direct<br />
discharge of domestic wastes and sewage, and<br />
Figure 2 <strong>–</strong> Temperature, Velocity and Depth in the different stations<br />
(L1, L2, L3 & L4) at each sampling month.<br />
the proximity of the main road contribute to<br />
anthropogenic inputs elevating the measured<br />
physical and chemical param<strong>et</strong>ers in site L2.<br />
The substrate granulom<strong>et</strong>ry was finer at L3<br />
and L4 (fine = 95%, coarse = 5%) than L1<br />
(fine = 45%, coarse = 55%) and L2 (fine<br />
= 55%, coarse = 45%) which, tog<strong>et</strong>her with<br />
the high level of physical and chemical variables<br />
favoured the developpement of plants,<br />
such as macroalgae and phanerogams.<br />
Biotic variables<br />
Macrophytic richness<br />
Twenty seven taxa including hydrophytes,<br />
helophytes and terrestrial species were<br />
observed at the four stations (Table 2). The<br />
taxonomic richness differed among the stations:<br />
9 taxa at L1, 9 taxa at L2, 22 taxa at L3<br />
and 19 taxa at L4. This was mainly due to the<br />
greater helophytes and terrestrial taxonomic<br />
richness at L3 (11 and 8 taxa) and L4 (7 and<br />
5 taxa) than at L1 (3 and 1 taxa) and L2 (6<br />
and 0 taxa).<br />
The hydrophytes species were more numerous<br />
at L4 (7 taxa) and L1 (5 taxa) than L2 and<br />
L3 (3 taxa for each one).<br />
However, five taxa were common to all stations<br />
(Cladophora sp., Vaucheria sp., Lemna<br />
minor L., Glyceria plicata (Fries) Fries and<br />
Phalaris arundinacea L.). Some taxa were<br />
specific to one station like Chara sp. at L1,<br />
Myriophyllum spicatum L., Potamog<strong>et</strong>on crispus<br />
L., Potamog<strong>et</strong>on pectinatus L. at L4 and<br />
Veronica anagallis-aquatica L., Galium<br />
aparine L., Lactuca serriola L. and Urtica<br />
dioica L. at L3.<br />
Except in station L1, the taxonomic richness<br />
varied according to the season. The number<br />
of taxa is higher in spring and summer at all<br />
stations. Except for the dry period (total disappearance<br />
of the hydrophytes), richness in<br />
L1 was relatively stable during seasons (Figure<br />
3).<br />
The station L2 was characterized by the<br />
absence of terrestrial species and the stability<br />
of the number of hydrophyte over the seasons<br />
(Figure 3). However we noticed the disappearance<br />
of Lemna minor L. during the winter.<br />
The number of the helophytes presented a<br />
maximum during spring and decreased during<br />
other seasons with the disappearance of<br />
Apium nodiflorum L. Lag., Cyperus eragrostis<br />
Lam., Cyperus longus L., and Phalaris arun-<br />
ecologia mediterranea <strong>–</strong> <strong>Vol</strong>. <strong>35</strong> <strong>–</strong> <strong>2009</strong>