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IPM OF CITRUS PESTS IN GREECE<br />

43<br />

individuals/leaf respectively. As a final point the citrus leafminer causes problems<br />

particularly on young citrus trees <strong>and</strong> overgraftings in nurseries but its damage on<br />

adult trees under Mediterranean conditions lacks economic importance (Garcia-Marí,<br />

Gr<strong>and</strong>a, Zaragoza, & Agusti, 2002).<br />

2.4.1. Sampling <strong>and</strong> Monitoring<br />

Sampling for monitoring infestation <strong>by</strong> the citrus leafminer involves collection of<br />

new shoots <strong>and</strong> leaves from growth flushes <strong>and</strong> observation of mines. The<br />

economic threshold for a chemical application on citrus leafminer has been<br />

estimated <strong>by</strong> several researchers; in China it is 0.74 larvae/leaf (or percentage of<br />

leaf damage over 20%) (Huang & Li, 1989); in Australia it is fixed at 25% of<br />

shoots with leaves smaller than 3 cm exhibiting mines of L1 (Beattie & Smith,<br />

1993); in Florida it is set at 30% of young shoots baring mines with live larvae<br />

(sampling should be performed when half of the trees in the orchard have young<br />

shoots) (Knapp et al., 1995).<br />

2.4.2. Biological Control<br />

Five exotic hymenopteran parasitoid species were introduced from Cyprus in 1996<br />

<strong>and</strong> were subsequently mass reared in the insectary of the Institute of Subtropical<br />

Crops <strong>and</strong> Olive (National Agricultural Research Foundation) in Chania-Crete. The<br />

introduced species were the encyrtid Ageniaspis citricola Logvinovskaya<br />

(Hymenoptera: Encyrtidae) <strong>and</strong> the eulophids Cirrospilus quadristriatus (Subba<br />

Rao <strong>and</strong> Ramamani), Citrostichus phyllocnistoides (Narayanan), Quadrastichus sp.<br />

<strong>and</strong> Semielacher petiolatus (Girault) (Hymenoptera: Eulophidae). A small number<br />

of all parasitoids were released in 1996 but cultures of Ageniaspis citricola <strong>and</strong><br />

Cirrospilus quadristriatus could not be kept after the first year <strong>and</strong> hence these<br />

species did not establish (Kalaitzaki, 2004).<br />

Citrostichus phyllocnistoides, Quadrastichus sp. <strong>and</strong> Semielacher petiolatus were<br />

released systematically (100–250 individuals/species/10 days from June to November)<br />

in orange <strong>and</strong> m<strong>and</strong>arin orchards in Crete (Chania) <strong>and</strong> the impact of both native <strong>and</strong><br />

introduced parasitoids was studied from 1997 to 1999. Similar releases were also<br />

performed in Peloponnese (Argolis, Korinthia, Lakonia) (Tsagarakis et al., 1999).<br />

All of the released parasitoid species established in Crete <strong>and</strong> contributed to the<br />

reduction of the citrus leafminer population, especially Citrostichus<br />

phyllocnistoides which dispersed very rapidely <strong>and</strong> far from the release sites <strong>and</strong> it<br />

achieved the highest percentage parasitism (mean 15.2–20.8% <strong>and</strong> maximum 45.8–<br />

51.1% on m<strong>and</strong>arin <strong>and</strong> orange trees, respectively).<br />

Only a few native parasitoid species were found to parasitize the citrus leafminer in<br />

Crete i.e. Pnigalio pectinicornis L., Neochrysocharis formosa (Westwood) <strong>and</strong><br />

Cirrospilus pictus (Nees) (all Hymenoptera: Eulophidae) in very small numbers <strong>and</strong><br />

with small contribution in percentage parasitism of the citrus leafminer (Kalaitzaki,<br />

Lykouressis, & Michelakis 1999; Kalaitzaki, 2004). Among them, P. pectinicornis was<br />

the most abundant one (Kalaitzaki et al., 1999; Kalaitzaki, Lykouressis, Perdikis, &

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