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A Rocha Portugal Observatory Report 2009-2010

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36 A <strong>Rocha</strong> <strong>Portugal</strong> <strong>Observatory</strong> <strong>Report</strong> <strong>2009</strong>-<strong>2010</strong><br />

Brown) was ending its flight period at the beginning of the survey period, thus one would expect the<br />

numbers of this species to be low, however it might also have been more common in previous years. Some<br />

of the Pieridae had also just ended their expected flight period (Euchloe belemia, Euchloe crameri) as well<br />

as Medanargia ines (Spanish Marbled White) and Euphydryas aurinia (Marsh Fritillary). The low number of<br />

Pieris brassicae (Large White) recorded was assumed to be caused by the scarcity of available food plants.<br />

This species clearly takes advantage of Cruciferae growing abundantly in cultivated fields on Quinta da<br />

<strong>Rocha</strong>, a rare situation in Abicada due to the current lack of agricultural activity. In addition, the conditions<br />

in 1991 might have been unusually favourable for Pieris brassicae. Regarding the absence of Lasiommata<br />

megera (Wall Brown) in <strong>2009</strong>, it should be noted that it never appeared in very high numbers and it used to<br />

be most numerous on the limestone scrubland and coastal scrubland (transect 3, 5 in 1991), these habitat<br />

associations were not represented in the current survey and are no longer accessible on Quinta da <strong>Rocha</strong>.<br />

During the period of this survey the lowlands of Abicada were rather poor both in flowering plants and host<br />

plants. The most common butterfly species along Transect A1 was Pararge aegeria (Speckled Wood) which<br />

appeared to be taking advantage of the shade provided by the high reeds. Pyronia cecilia (Southern<br />

Gatekeeper) was present, but in low numbers. The rest of the butterflies recorded along this transect<br />

(Pieris rapae, Pieris brassicae and Papilio machaon), were mainly fast flying, attempting to reach a more<br />

sheltered area in the usually windy conditions. The observation of Celastrina argiolus (Holly Blue) was<br />

interesting because although widespread and common, this species is most commonly seen in woodland<br />

margins rather than in open marshland habitats. However, the individuals observed were seen crossing the<br />

open areas and seeking shelter around the reedbed, perhaps indicating that this species is more mobile<br />

than many other Lycaenidae.<br />

Although the butterfly species diversity in transects A2, A3 and M1 were dominated by grassland species,<br />

they clearly differed from each other in terms of composition. Transect A2 was the most sheltered site and<br />

included the greatest number of wood/scrubland specialists 4 . In comparison the vegetation around<br />

transects A3 and M1 was more open and, as might be expected, a higher number of grassland specialists 5<br />

was recorded at these locations. Muschampia proto (Sage Skipper) and Carcharodus tripolina (False Mallow<br />

Skipper), species observed mostly at the Mexilhoeira Grande site, M1, are known to show a strong<br />

correlation with their food plants.<br />

Conclusions and recommendations<br />

The diversity of butterfly species in the wider Alvor Estuary area was similar to that observed in previous<br />

studies in Quinta da <strong>Rocha</strong>. One notable difference in <strong>2009</strong> was the great abundance of Pyronia cecilia<br />

(Southern Gatekeeper), representing 48.5% of the total number of recorded individuals. A potential<br />

explanation for this difference includes the fact that the Abicada peninsula had less habitat diversity than<br />

Quinta da <strong>Rocha</strong> and the predominant habitat type (grassland) is very favourable for this species.<br />

While recognising the fact that populations fluctuate every year, the infrequent occurrence of Pieris<br />

brassicae (Large White) and Pontia daplidice (Bath White) was notable. Again the difference in habitat type,<br />

in this case the lack of cultivated fields on the Abicada peninsula, may have been a major contributing<br />

factor. These two species are not currently endangered but it would be interesting to continue to monitor<br />

their population dynamics.<br />

4 Iphiclides podalirius, Satyrium spini, Celastrina argiolus, Pararge aegeria<br />

5 Lycaena phlaeas, Aricia cramera, Polyommatus icarus, Maniola jurtina, Pyronia cecilia, Coenonympha pamphilus,<br />

Muschampia proto, Carcharodus tripolina, Thymelicus acteon

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