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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sented in figure 1 and table 1, respectively.<br />
Larvae were collected and their species identified.<br />
Biotic and abiotic param<strong>et</strong>ers<br />
of the water<br />
Once every two weeks, three water samples<br />
were collected from every water body with a<br />
n<strong>et</strong> (pore size was 450 µm) from a depth of<br />
approximately 10-30 cm. The water volume<br />
that passed through the n<strong>et</strong> was calculated<br />
according to the n<strong>et</strong>’s dimensions and the area<br />
of the water through which the n<strong>et</strong> was<br />
dragged. Zooplankton were counted and identified<br />
using a binocular microscope, and their<br />
numbers assessed from the average of three<br />
samples.<br />
The biomass of invertebrate species in various<br />
aquatic habitats was d<strong>et</strong>ermined. Following<br />
the identification of the species, a number<br />
of individuals of each species were preserved<br />
in <strong>et</strong>hanol. By means of an ocular with a graduated<br />
scale, the lengths and widths of every<br />
taxonomical representative were measured (in<br />
scale units which were converted to millim<strong>et</strong>ers).<br />
The computation of the biomass<br />
(Gophen 1976) was carried out by calculating<br />
the volume (according to the equation for a<br />
spherical volume), assuming that the density<br />
of the organism was close to that of water.<br />
The equation for the biomass is:<br />
ecologia mediterranea <strong>–</strong> <strong>Vol</strong>. <strong>35</strong> <strong>–</strong> <strong>2009</strong><br />
Breeding site selection according to suitability for amphibian larval growth<br />
under various ecological conditions in the semi-arid zone of northern Israel<br />
Table 1 <strong>–</strong> Amphibian larvae breeding sites in this study. Springs = Sp, Streams = St, Pits = Pi, Ponds = Po.<br />
Label Name Type Latitude Longitude Height<br />
(m.a.s.l)<br />
Sp1 Balad spring 157022 236119 446<br />
Sp2 Humema spring 187299 276819 900<br />
Sp3 Navoraya spring 197970 267307 663<br />
St1 Tel-Dan stream 211100 294800 190<br />
Pi1 Maalot pit 176000 267450 596<br />
Pi2 Nimrod pit 216900 295300 760<br />
Po1 Manof pond 172086 250470 340<br />
Po2 Kash pond 196203 270560 809<br />
Po3 Dovev pond 189158 272812 765<br />
Po4 Matityahu pond 192873 274808 665<br />
Po5 Lehavot pond 210150 284300 70<br />
Po6 Sasa pond 186972 270855 810<br />
Po7 Fara pond 193406 274579 676<br />
Po8 Raihaniya pond 195791 272861 665<br />
Water param<strong>et</strong>ers were measured at a depth<br />
of 10 cm every two weeks during the period<br />
in which the pools were filling up. Temperature<br />
and dissolved oxygen data were obtained<br />
by a hand-held oxygen m<strong>et</strong>er (WTW, Oxi330<br />
s<strong>et</strong>, Germany) in situ, and one liter of water<br />
was sampled for the laboratory tests of water<br />
quality, including pH, ammonium concentration,<br />
electrical conductivity (EC) and chlorophyll<br />
a concentration. Water param<strong>et</strong>ers were<br />
analyzed by one-way analysis of variance<br />
(ANOVA), with the level of significance<br />
b<strong>et</strong>ween groups s<strong>et</strong> at p < 0.05 (ANOVA).<br />
Niche width<br />
The niche breadth for each amphibian larvae<br />
species was characterized according to five<br />
important environmental water variables<br />
(which dramatically differed among the<br />
breeding sites and during the year) <strong>–</strong> temperature,<br />
conductivity, ammonium, relative oxygen<br />
content (O 2 ) and pH. These d<strong>et</strong>ermined<br />
the dimensions for a principle component<br />
analysis.<br />
67