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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

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