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The exposure and toxicity of pesticides to amphibians

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Amphibians <strong>and</strong> <strong>pesticides</strong><br />

were not tracked during migra<strong>to</strong>ry phase). Some were found <strong>to</strong> forage in arable fields at night up <strong>to</strong><br />

20m from the scrub they <strong>to</strong>ok refuge in during daylight. This suggests that <strong>to</strong>tal distance moved across<br />

the fields could be 40m or more.<br />

Using night counts <strong>of</strong> migrating <strong>to</strong>ads over two years (Hartel <strong>and</strong> Demeter 2005), breeding migration<br />

was found <strong>to</strong> last 19 <strong>to</strong> 36 days from mid March. In the study area the pasture l<strong>and</strong> formed a corridor<br />

between the forest <strong>and</strong> the pond such that very few migrating <strong>to</strong>ads were found on arable l<strong>and</strong>. <strong>The</strong><br />

furthest recorded <strong>to</strong>ad was 450m from the pond near the forest area. No active <strong>to</strong>ads were found when<br />

temperature was below 5°C. In periods <strong>of</strong> intense activity <strong>to</strong>ad density within 10m from the pond was<br />

0.16 <strong>to</strong>ads/m 2 while at 150m distance this was 0.055 <strong>to</strong>ads/m 2 .<br />

In a study <strong>of</strong> migration distances in March <strong>to</strong> April, maximum recorded movements in agricultural<br />

areas ranged from 450 <strong>to</strong> 518m. Maximal distances moved in other habitats ranged from 170-1835m<br />

(Kovar et al 2009).<br />

In a study <strong>of</strong> movements <strong>to</strong>wards the breeding pond (Sinsch et al. 1988a), <strong>to</strong>ads were observed at 70-<br />

240m from the breeding pond <strong>and</strong> did not move directly <strong>to</strong>wards the spawning site but entered the<br />

pond from any shore. Some paths deviated <strong>and</strong> allowed the pond <strong>to</strong> be approached via a ditch which<br />

terminated at the pond. Post spawning migration was also moni<strong>to</strong>red with individuals recorded up <strong>to</strong><br />

1.6km from the pond. In May <strong>and</strong> June migra<strong>to</strong>ry behaviour decreased with animals staying in their<br />

‘home range’ until autumn migration or hibernation. Of 29 <strong>to</strong>ads observed, 23 hibernated at distances<br />

<strong>of</strong> 70-420m from the breeding pond while six hibernated in their summer home range 1060-1230m<br />

from the pond.<br />

Berger et al (2011b) moni<strong>to</strong>red movements <strong>of</strong> common <strong>to</strong>ads on arable l<strong>and</strong> using radio-telemetry<br />

during post breeding movements in August <strong>and</strong> September. Two types <strong>of</strong> behaviour were found<br />

depending on the amount <strong>of</strong> cover present on the field. Where fields were freshly ploughed, animals<br />

moved across these quickly, one animal moving 580m in one night. In stubble fields with volunteer<br />

cereals or rape only or set-aside, small daily movements were observed, <strong>of</strong>ten less than 10m. In one<br />

case an animal using such a field survived the field being ploughed <strong>and</strong> moved <strong>to</strong> adjacent set-aside<br />

l<strong>and</strong>. Where animals remained on arable l<strong>and</strong>, cover was found under plant material, in small mammal<br />

burrows or cracks under clods <strong>of</strong> earth. <strong>The</strong>se resting places were <strong>of</strong>ten within 35m <strong>of</strong> non-arable<br />

areas. Toads tracked using the fluorescent dye method behaved in a similar fashion quickly traversing<br />

freshly ploughed fields <strong>and</strong> winter rape <strong>to</strong> reach areas with dense vegetation.<br />

1.3.1.2. Movement information for Bombina bombina<br />

In a study <strong>of</strong> migration distances in March <strong>to</strong> April, maximum recorded movement in an agricultural<br />

area was 167m. Maximal distances moved in other habitats ranged from 160-230m (Kovar et al 2009).<br />

1.3.1.3. Movement information for Bufo calamita/Epidalea calamita<br />

Radio-tagged individuals were tracked in barley fields on the way <strong>to</strong> (end <strong>of</strong> January <strong>to</strong> mid- April)<br />

<strong>and</strong> from (early April <strong>to</strong> September) breeding ponds (Miaud et al 2000). Maximum daily distances<br />

moved ranged from 22m <strong>to</strong> 577m in spring, <strong>and</strong> 125m <strong>to</strong> 353m after breeding. Maximum distances<br />

moved by a <strong>to</strong>ad in each period were 934m <strong>and</strong> 4411m respectively. Marginal habitats such as ditches<br />

with vegetation <strong>and</strong> s<strong>to</strong>ne embankments were used as shelter sites.<br />

Home range in an area <strong>of</strong> cereal agriculture was determined in a study by Miaud <strong>and</strong> Sanuy (2005).<br />

Median home range area was 0.5 ha (range 0.1-11 ha) during the breeding season (January-April).<br />

Home range size increased during the post-breeding season (April-September) with a median<br />

minimum concave polygon <strong>of</strong> 4.1 ha. Home ranges included crop fields but these were less preferred<br />

compared <strong>to</strong> other habitats. Order <strong>of</strong> habitat preference was s<strong>to</strong>ne embankments/ditches with reeds ><br />

Supporting publications 2012:EN-343 19<br />

<strong>The</strong> present document has been produced <strong>and</strong> adopted by the bodies identified above as author(s). This task has been carried out exclusively<br />

by the author(s) in the context <strong>of</strong> a contract between the European Food Safety Authority <strong>and</strong> the author(s), awarded following a tender<br />

procedure. <strong>The</strong> present document is published complying with the transparency principle <strong>to</strong> which the Authority is subject. It may not be<br />

considered as an output adopted by the Authority. <strong>The</strong> European food Safety Authority reserves its rights, view <strong>and</strong> position as regards the<br />

issues addressed <strong>and</strong> the conclusions reached in the present document, without prejudice <strong>to</strong> the rights <strong>of</strong> the authors.

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