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Observation of Arthropod Populations during Outbreak of Olive - Iresa

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<strong>Observation</strong> <strong>of</strong> <strong>Arthropod</strong> <strong>Populations</strong> <strong>during</strong> <strong>Outbreak</strong> <strong>of</strong><br />

<strong>Olive</strong> Psyllid Euphyllura olivina in Tunisian <strong>Olive</strong> Groves<br />

Naceur Gharbi, Institut de l’Olivier, Rue Hédi Karray, 2080 Ariana, Université de<br />

Sfax, Tunisia, Ali Dibo, and Mohieddine Ksantini, Institut de l’Olivier, P.O. Box.<br />

1087, 3000 Sfax, Université de Sfax, Tunisia<br />

__________________________________________________________________________<br />

ABSTRACT<br />

Gharbi, N., Dibo, A., and Ksantini, M. 2012. <strong>Observation</strong> <strong>of</strong> arthropod populations <strong>during</strong><br />

outbreak <strong>of</strong> olive psyllid Euphyllura olivina in Tunisian olive groves. Tunisian Journal <strong>of</strong> Plant<br />

Protection 7: 27-34.<br />

This study aims to investigate the <strong>Arthropod</strong> communities in pullulating period <strong>of</strong> Euphyllura olivina<br />

(Homoptera: Psyllidae) which is recognized as a serious problem pest <strong>of</strong> olive trees in Tunisia. The<br />

field trials were achieved in two successive years, i.e. 2009 and 2010, in two organic olive orchards<br />

situated in the regions <strong>of</strong> Taous and Chaal (Sfax, Southern East <strong>of</strong> Tunisia). The assessment <strong>of</strong><br />

abundance <strong>of</strong> different groups <strong>of</strong> <strong>Arthropod</strong>s showed that phytophagous and natural enemies were<br />

much more abundant in 2010 than in 2009 in Taous and Chaal groves. More than 94% <strong>of</strong> all herbivores<br />

were E. olivina. The most abundant natural enemies on olive trees was the indigenous bug Anthocoris<br />

nemoralis (Heteroptera: Anthocoridae) with an average population frequency <strong>of</strong> 49% <strong>of</strong> the total<br />

natural enemies found, followed by Psyllaephagus euphyllurae (Hymenoptera: Encyrtidae) (26%),<br />

lacewings (20%), Syrphid predators (3%), and other generalist predators (2%).<br />

Keywords: Biodiversity, Euphyllura olivina, natural enemies, olive tree<br />

__________________________________________________________________________<br />

<strong>Olive</strong> culture is considered to be <strong>of</strong><br />

great ecological, economic, dietary and<br />

social importance in Mediterranean<br />

countries. In Tunisia, olive plantations<br />

counts about 66 million trees and cover<br />

about one third <strong>of</strong> the arable land area<br />

(cultivated area 1.7 million ha).<br />

The olive grove is an<br />

agroecosystem that supports a wide range<br />

<strong>of</strong> diverse and functionally important<br />

groups <strong>of</strong> <strong>Arthropod</strong>s (13, 17, 18). The<br />

canopy arthropod community has<br />

Corresponding author: Naceur Gharbi<br />

Email: gharbi.naceur@yahoo.fr<br />

Accepted for publication 28 June 2012<br />

a complex structure that includes<br />

functional groups with phytophagous,<br />

predator, parasitoid and detritivore<br />

species (17, 18, 20).<br />

The olive psyllid Euphyllura<br />

olivina (Homoptera: Psyllidae) is a<br />

serious pest in Tunisia. High psyllid<br />

populations can affect the vegetative<br />

development, the fertility and the<br />

reproduction <strong>of</strong> the olive tree (1, 9, 10,<br />

12). During the beginning <strong>of</strong> early spring<br />

season, olive trees produce new shoots<br />

that continue to elongate throughout most<br />

<strong>of</strong> the spring. <strong>Outbreak</strong>s <strong>of</strong> olive psyllid<br />

populations may be associated with new<br />

shoot production, weather conditions (4)<br />

and with insecticide use which destroys<br />

the psyllid natural enemies (5, 12).<br />

Tunisian Journal <strong>of</strong> Plant Protection 27 Vol. 7, No. 1, 2012


The olive psyllid is commonly<br />

consumed by several species <strong>of</strong> generalist<br />

predators (Anthocoridae, Chrysopidae,<br />

Aranae, Coccinellidae, and Miridae) and<br />

many parasitoids (Psyllaephagus<br />

euphyllurae, Alloxista sp., Elasmus sp…).<br />

These natural enemies successfully<br />

control psyllid in some cases (4).<br />

At present, intensive pesticide use<br />

is being held responsible for irreversible<br />

damage to biodiversity, and numerous<br />

alternatives are being investigated in<br />

order to control crop pests (7, 16).<br />

The aim <strong>of</strong> this study was the<br />

monitoring <strong>of</strong> the group <strong>of</strong> <strong>Arthropod</strong>s in<br />

olive groves in the pullulating period <strong>of</strong><br />

E. olivina.<br />

MATERIALS AND METHODS<br />

Orchards. The study areas were<br />

located in two olive groves near Sfax<br />

(Southern East <strong>of</strong> Tunisia): Taous and<br />

Chaal groves with different agricultural<br />

systems. The predominant cultivar is<br />

Chemlali. Both olive groves have been<br />

conducted according to organic growing<br />

guidelines. All olive trees were well<br />

tended, but no pesticide sprays were<br />

applied against pests or diseases, and soil<br />

was ploughed superficially with a<br />

scarifier two to four times a year to<br />

control weeds.<br />

In Taous grove, the planting<br />

density is <strong>of</strong> 7 m × 7 m, the olive trees are<br />

about 10 years old and the field was<br />

irrigated. Chaal grove was planted in<br />

extensive (pluvial) mode with trees about<br />

70 years old spaced 24 m × 24 m apart.<br />

The two biotopes are characterized by a<br />

typical continental climate, cold winters<br />

(5.8°C in January) and very hot summers<br />

(32.2°C in August).<br />

<strong>Observation</strong>s. The survey <strong>of</strong> the<br />

fluctuation <strong>of</strong> psyllid population and<br />

beneficial insects was monitored weekly<br />

by sampling from the beginning <strong>of</strong><br />

February till the end <strong>of</strong> May over a period<br />

<strong>of</strong> 2009 and 2010. Two sampling<br />

techniques were applied in the current<br />

study: beating sheet and branch sampling.<br />

Beating sheet. Ten trees at about<br />

the same stage <strong>of</strong> growth were randomly<br />

selected in each biotope and five branches<br />

per tree were sampled. All captured<br />

individuals were identified under<br />

binocular at the order, family or species<br />

level and the total number <strong>of</strong> each taxon<br />

was recorded.<br />

Branch sampling. Five trees per<br />

site were randomly sampled, five twigs<br />

(10-15 cm in length) were cut per tree,<br />

covered in plastic bags and taken to the<br />

laboratory where they were examined<br />

under binocular and the current stages <strong>of</strong><br />

psyllids (eggs and juveniles) and<br />

parasitoids or predators were counted.<br />

Psyllid stages observed in sample<br />

were expressed in linear density (4, 5)<br />

that represents the total number <strong>of</strong> psyllid<br />

stages on length <strong>of</strong> examined twigs<br />

(number <strong>of</strong> stages/m).<br />

For the assessment <strong>of</strong> the<br />

fecundity <strong>of</strong> E. olivina, females were<br />

sampled weekly and examined in the<br />

laboratory for the presence <strong>of</strong> mature<br />

eggs, after opening their abdomen.<br />

Data analysis. Data were analyzed<br />

with ANOVA using LSD test (SPSS<br />

version 17). If necessary data were<br />

transformed using the Log-transformation<br />

for normal distribution and homogeneity<br />

<strong>of</strong> variances.<br />

RESULTS<br />

Beating sheet results. The<br />

assessments <strong>of</strong> abundance <strong>of</strong> the different<br />

groups <strong>of</strong> arthropods in the regions <strong>of</strong><br />

Taous and Chaal from February till end <strong>of</strong><br />

May over two years, a total <strong>of</strong> 60117<br />

insects were captured, among which<br />

51493 were herbivores and 8684 were<br />

natural enemies. Phytophagous and<br />

Tunisian Journal <strong>of</strong> Plant Protection 28 Vol. 7, No. 1, 2012


natural enemies were much more<br />

abundant in 2010 than in 2009 survey in<br />

Taous and Chaal groves. More than 94%<br />

<strong>of</strong> all herbivores were E. olivina (a total<br />

<strong>of</strong> 48490 individuals; sex ratio:<br />

male/female = 0.88/1). High population<br />

densities <strong>of</strong> psyllid occurred between the<br />

beginning <strong>of</strong> March till the end <strong>of</strong> May<br />

with two peaks; the first peak in the<br />

middle <strong>of</strong> March and the second one at<br />

the end <strong>of</strong> April. Other herbivores were<br />

olive moth, Prays oleae (Lepidoptera:<br />

Yponomeutidae) (4%) and Liothrips<br />

oleae (Thysanoptera: Phlaeothripidae) (<<br />

2%).<br />

The most abundant natural<br />

enemies on olive trees was Anthocoris<br />

nemoralis (Heteroptera: Anthocoridae)<br />

with an average population frequency <strong>of</strong><br />

49%, <strong>of</strong> the total <strong>of</strong> natural enemies<br />

found, followed by Psyllaephagus<br />

euphyllurae (Hymenoptera: Encyrtidae)<br />

(26%), green and brown lacewings<br />

(Neuroptera: Chrysopidae) (20%),<br />

Syrphid predators (Diptera: Syrphidae)<br />

(3%) and other generalist predators (2%).<br />

Mean numbers <strong>of</strong> E. olivina were<br />

significantly different between Taous and<br />

Chaal groves (Table 1). In contrast, there<br />

were significant location effects on the<br />

mean numbers <strong>of</strong> A. nemoralis and P.<br />

euphyllurae from February till end <strong>of</strong><br />

May samplings in both years (2009 and<br />

2010). In all cases, Taous grove had<br />

higher densities <strong>of</strong> these insects than<br />

Chaal grove. The effect <strong>of</strong> location by<br />

year interaction on the linear densities <strong>of</strong><br />

E. olivina was not significant (F3, 19 =<br />

1.097, P = 0.31). However, the locationyear<br />

interactions have no effects on the<br />

abundance <strong>of</strong> P. euphyllurae and A.<br />

nemoralis. Both P. euphyllurae and A.<br />

nemoralis were more abundant in Taous<br />

than Chaal grove in each <strong>of</strong> collection<br />

periods.<br />

Mean numbers <strong>of</strong> Chrysopid and<br />

Syrphid predators were not significantly<br />

different between Taous and Chaal<br />

groves. However, <strong>during</strong> both years, the<br />

mean numbers <strong>of</strong> Chrysopid and Syrphid<br />

predators were higher in Taous than in<br />

Chaal.<br />

In two orchards, every year, some<br />

predator species such as Chrysoperla<br />

carnea (Neuroptera: Chrysopidae) were<br />

present at low number before the growth<br />

<strong>of</strong> phytophagous populations. Overall,<br />

predator populations started to increase in<br />

numbers from March to mid May,<br />

especially for A. nemoralis. Furthermore,<br />

P. euphyllurae was observed especially in<br />

the period between mid April and mid<br />

May, and it was not frequently observed<br />

at the last period <strong>of</strong> observations<br />

(beginning <strong>of</strong> May), because the psyllid<br />

nymphs were absent in this period (Fig.<br />

1).<br />

Branch sampling results. The<br />

total number <strong>of</strong> collected E. olivina<br />

nymphs was 84623 and a total <strong>of</strong> 119309<br />

psyllid eggs were sampled. The structure<br />

<strong>of</strong> psyllid population was composed by<br />

68% young instars (L1, L2 and L3) and<br />

32% old instars (L4 and L5). The total<br />

number <strong>of</strong> immature mortality was 1287,<br />

with 65% <strong>of</strong> them consumed by natural<br />

enemies.<br />

Significantly, there were more<br />

eggs and immatures <strong>of</strong> E. olivina in<br />

Taous than Chaal <strong>during</strong> the sampling<br />

period. Also, mean proportion <strong>of</strong> intact<br />

immature was statistically similar in<br />

Taous than Chaal from March to mid<br />

May (Table 2). However, Taous had<br />

higher proportion <strong>of</strong> immatures<br />

parasitized than Chaal. Likewise, mean<br />

proportion <strong>of</strong> immatures consumed was<br />

higher in Taous than Chaal <strong>during</strong> the<br />

sampling period.<br />

Tunisian Journal <strong>of</strong> Plant Protection 29 Vol. 7, No. 1, 2012


Table 1. Phytophagous and predaceous insects occurring on olive trees colonized by Euphyllura olivina in<br />

Taous and Chaal groves <strong>during</strong> two years 2009 and 2010 (Sampling period: February - May)<br />

Insect species Mean number (± SE) <strong>of</strong> insects a Statistical values<br />

Sampling year Taous Chaal F P<br />

2009<br />

Phytophagous<br />

Euphyllura olivina<br />

Prays oleae<br />

Liothrips oleae<br />

Predaceous<br />

Anthocoris nemoralis<br />

Psyllaephagus euphyllurae<br />

Chrysopid predators<br />

Syrphid predators<br />

2010<br />

Phytophagous<br />

Euphyllura olivina<br />

Prays oleae<br />

Liothrips oleae<br />

Predaceous<br />

Anthocoris nemoralis<br />

Psyllaephagus euphyllurae<br />

Chrysopid predators<br />

Syrphid predators<br />

134.27 ± 42.09 a<br />

3.71 ± 0.41 a<br />

1.50 ± 0.61 a<br />

5.56 ± 1.86 a<br />

3.06 ± 0.85 a<br />

2.44 ± 0.69<br />

0.30 ± 0.18<br />

171.21 ± 65.29 a<br />

2.62 ± 0.84<br />

2.06 ± 0.43 a<br />

7.93 ± 1.02 a<br />

3.93 ± 0.87 a<br />

2.64 ± 0.66<br />

0.38 ± 0.04<br />

83.26 ± 24.67 b<br />

1.82 ± 0.35 b<br />

0.94 ± 0.11 b<br />

3.05 ± 1.12 b<br />

1.78 ± 0.55 b<br />

2.06 ± 0.47<br />

0.23 ± 0.08<br />

92.29 ± 31.30 b<br />

2.28 ± 0.63<br />

0.72 ± 0.07 b<br />

4.18 ± 0.82 b<br />

2.18 ± 0.54 b<br />

2.53 ± 0.59<br />

0.37 ± 0.02<br />

F1,31 = 5.91<br />

F1,31 = 8.67<br />

F1,31 = 4.25<br />

F1,31 = 12.253<br />

F1,31 = 6.321<br />

F1,31 = 3.662<br />

F1,31 = 2.698<br />

F1,31 = 23.051<br />

F1,31 = 0.543<br />

F1,31 = 21.066<br />

F1,31 = 24.514<br />

F1,31 = 6.124<br />

F1,31 = 9.546<br />

F1,31 = 0.776<br />

0.0410<br />

0.0331<br />

0.0110<br />

0.0421<br />

0.0341<br />

0.0708<br />

0.0927<br />

0.0013<br />

0.8761<br />

0.0012<br />

0.0134<br />

0.0112<br />

0.0638<br />

0.3847<br />

a Data show mean number (± SE) <strong>of</strong> insects per tree. Means followed by the same letter within a line are not<br />

significantly different according to LSD test at P < 0.05.<br />

Table 2. Mean number <strong>of</strong> immature stage <strong>of</strong> Euphyllura olivina on olive trees in Taous and Chaal groves <strong>during</strong><br />

two years 2009-2010 (Sampling period: February-May)<br />

Sampling year<br />

Mean linear density (± SE)<br />

<strong>of</strong> E. olivina<br />

Mean proportions (± SE) <strong>of</strong> Nymphs a<br />

Grove site<br />

2009<br />

Eggs Nymphs Intact Parasitized Consumed<br />

Taous 93.997 ± 28.951 a 52.875 ± 11.517 a 0.810 ± 0.052 a 0.054 ± 0.016 a 0.136 ± 0.038 a<br />

Chaal 59.752 ± 22.814 b 28.806 ± 11.506 b 0.935 ± 0.014 b 0.021 ± 0.006 b 0.043 ± 0.011 b<br />

F1,31 3.923<br />

17.013<br />

26.032<br />

17.470<br />

26.728<br />

P 0.036<br />

0.003<br />

0.00927<br />

0.00308<br />

0.00085<br />

2010<br />

Taous 146.961 ± 34.184 a 67.373 ± 18.419 a 0.616 ± 0.102 a 0.078 ± 0.014 a 0.306 ± 0.089 a<br />

Chaal 76.984 ± 31.526 b 32.579 ± 17.291 b 0.856 ± 0.024 b 0.049 ± 0.013 b 0.095 ± 0.018 b<br />

F1,31 29.358<br />

26.401<br />

25.875<br />

11.691<br />

26.363<br />

P 0.00923<br />

0.00817<br />

0.00945<br />

0.00909<br />

0.00089<br />

a<br />

Means followed by the same letter within a line are not significantly different according to LSD test at P < 0.05.<br />

Tunisian Journal <strong>of</strong> Plant Protection 30 Vol. 7, No. 1, 2012


Fig. 1. Linear densities <strong>of</strong> the different stages <strong>of</strong> Euphyllura olivina in Taous and Chaal groves <strong>during</strong> 2009<br />

and 2010 (Sampling period: February-May).<br />

Tunisian Journal <strong>of</strong> Plant Protection 31<br />

Vol. 7, No. 1, 2012


DISCUSSION<br />

In this study, the representative<br />

orders in olive orchard were Homoptera,<br />

Lepidoptera, Neuroptera, Thysanoptera<br />

and Coleoptera varying in proportion<br />

between groves and years. These groups<br />

have been reported in the literature as<br />

typically the abundant groups in olive<br />

groves (3, 11, 19). These orders include<br />

key-groups <strong>of</strong> predators, parasitoids and<br />

phytophagous. Natural enemies play an<br />

important role in the biological control <strong>of</strong><br />

olive pests like P. oleae and E. olivina (8,<br />

13, 14, 15).<br />

In Tunisia, the list <strong>of</strong> natural<br />

enemies <strong>of</strong> E. olivina is composed by 14<br />

species (11) that were recorded with<br />

different frequencies that varied<br />

according to species belonging to four<br />

families: Anthocoridae, Chrysopidae,<br />

Coccinellidae and Encyrtidae. The first<br />

three families include many predator<br />

species: A. nemoralis, C. carnea and<br />

Coccinella septempunctata (Coleoptera:<br />

Coccinellidae), and the fourth includes<br />

the endoparasitoid P. euphyllurae (4, 11).<br />

The role <strong>of</strong> herbivore induced volatiles in<br />

the searching behavior <strong>of</strong> predators like<br />

A. nemoralis and C. carnea under field<br />

conditions was studied (6).<br />

During both years <strong>of</strong> study, total<br />

abundance <strong>of</strong> arthropods was higher in<br />

Taous than in Chaal olive grove.<br />

However, this higher abundance is a<br />

result <strong>of</strong> the high number <strong>of</strong> Homoptera,<br />

which is due to the presence <strong>of</strong> the olive<br />

pest E. olivina. Our observations show<br />

clearly that E. olivina is a serious pest <strong>of</strong><br />

olive crop. Early attacks, especially in the<br />

spring, cause considerable damage to<br />

flowers and subsequent losses in both<br />

quality and quantity <strong>of</strong> olive fruits (5).<br />

Throughout the growing season, mid-<br />

February to the end <strong>of</strong> May, only E.<br />

olivina was constantly present. High<br />

population densities occurred at mid<br />

March to the end <strong>of</strong> May with two peaks:<br />

the first peak at the mid-March and the<br />

second peak in the second half <strong>of</strong> April<br />

(Fig. 1).<br />

The largest percentages <strong>of</strong> mature<br />

females <strong>of</strong> E. olivina were recorded<br />

<strong>during</strong> the period between early February<br />

and late April. Generally, the peak <strong>of</strong> egg<br />

laying occurred in the second week <strong>of</strong><br />

March (around 75 to 95% <strong>of</strong> total females<br />

respectively in 2009 and 2010) and<br />

remained high until mid-April (more than<br />

50% <strong>of</strong> total females), explaining the<br />

significant increase in its population size<br />

<strong>during</strong> the spring months (Fig. 1).<br />

In this evaluation, the most<br />

abundant predator found on olive in Sfax<br />

area was A. nemoralis with an average<br />

population frequency varying between 33<br />

and 41% <strong>of</strong> the total natural enemies<br />

found. Anthocorids are not abundant on<br />

olive early in spring. Its population starts<br />

to increase in numbers by mid-March,<br />

peaking at the end <strong>of</strong> April, coinciding<br />

with that <strong>of</strong> E. olivina, and representing<br />

the major part <strong>of</strong> the predator populations<br />

found on olive tree <strong>during</strong> the spring.<br />

This indicates the positive relationship<br />

occurring between E. olivina and A.<br />

nemoralis in olive orchards. This<br />

predator, A. nemoralis, can be reared<br />

easily and cheaply and is readily<br />

available. There are many reports<br />

describing the role <strong>of</strong> this predator in the<br />

biological control <strong>of</strong> E. olivina<br />

populations (2). However, little is known<br />

on their role in olive orchard and this<br />

needs to be clarified.<br />

The two years <strong>of</strong> this survey have<br />

provided useful and promising data as a<br />

basis for further research in the effective<br />

sustainable management <strong>of</strong> P.<br />

euphyllurae, A. nemoralis and C. carnea<br />

populations, which constitute the most<br />

important group <strong>of</strong> natural enemies <strong>of</strong><br />

insect pests recorded in olive orchards.<br />

Tunisian Journal <strong>of</strong> Plant Protection 32 Vol. 7, No. 1, 2012


__________________________________________________________________________<br />

RESUME<br />

Gharbi N., Dibo A. et Ksantini M. 2012. <strong>Observation</strong> des populations d’arthropodes durant la<br />

période de pullulation du psylle de l’olivier dans les oliveraies tunisiennes. Tunisian Journal <strong>of</strong><br />

Plant Protection 7: 27-34.<br />

Ce travail vise l’étude de la communauté des arthropodes durant la période de pullulation d'Euphyllura<br />

olivina (Homoptera: Psyllidae), un ravageur majeur des oliviers en Tunisie. Le suivi s’est étendu sur<br />

deux années successives 2009 et 2010, dans deux oliveraies biologiques localisées dans les régions de<br />

Taous et Chaal (Sfax, Sud-Est de la Tunisie). L’évaluation de l’abondance des différents groupes<br />

d’arthropodes montrent que les phytophages et les auxiliaires étaient plus abondants en 2010 qu’en<br />

2009 dans les oliveraies Taous et Chaal. Plus que 94% de la totalité des phytophages collectés est<br />

composée d’E. olivina. L’ennemi naturel le plus rencontré est la punaise prédatrice Anthocoris<br />

nemoralis (Heteroptera: Anthocoridae) avec une population moyenne de 49% de la totalité des<br />

auxiliaires collectés, suivi de Psyllaephagus euphyllurae (Hymenoptera: Encyrtidae) (26%), des<br />

chrysopes (20%), des syrphes (3%) et d’autres prédateurs généralistes (2%).<br />

Mots clés: Biodiversité, ennemis naturels, Euphyllura olivina, olivier<br />

__________________________________________________________________________<br />

���ﻣ<br />

ﻼ��ﺑ ﻲ��ﺗ ة��ﻓ لﻼﺧ �ﺟرﻷا تﺎ����ﻣ تﺎﻋ����ﻟ<br />

�ﺻر . 2002 . ﻲ�����ﻗ �ﻳ�ﻟا ﻲ�ﻣو ��ﻳد ﻲ�ﻋو �ﺻﺎﻧ ،ﻲﺑ�ﻐﻟا<br />

. ���ﻧ��ﻟا ن��ﻳ�ﻟا ��ﺗﺎ�ﺑ ﻲﻓ Euphyllura olivina ن��ﻳ�ﻟا<br />

Tunisian Journal <strong>of</strong> Plant Protection 7: 27-34.<br />

Euphyllura olivina ن��ﻳ�ﻟا ﻼ��ﺑ �ﺛﺎ��ﻟ ���ﻼ�ﻟا ة���ﻟا لﻼﺧ �ﺟرﻷا تﺎ����ﻣ ع��ﺗ �ﺳارد ﻰﻟإ ��ﻌﻟا ا�ه ف�ﻬﻳ<br />

��ﻣﺎﻋ لﻼﺧ �ﺳار�ﻟا ه�ه �ﻳ�ﺟأ . �ﻧ�ﺗ ﻲﻓ ن��ﻳ�ﻟا<br />

رﺎ�ﺷﻷ �ﻳ�ﺟ ����ﻣ ّ�ﻌﺗ ﻲ�ﻟاو ،(Homoptera:<br />

Psyllidae)<br />

ﻲﻗ��ﻟا ب���ﻟا ،�ﻗﺎ�ﺻ)<br />

لﺎﻌ�ﻟاو سووﺎ�ﻟا ْﻲ�����ﺑ �ﻳ�ﻀﻋ/<br />

��ﺟ�ﻟ��ﺑ ن��ﻳز ��ﺗﺎ�ﺑ ﻲﻓ ،2010<br />

و 2009 ���ﻟﺎ��ﻣ<br />

لﻼﺧ �ﻓوأ �ﻧﺎآ ��ﻌ���ﻟا ءا�ﻋﻷاو ��ﺗﺎ��ﻟا تﺎﻓﻵا نأ �ﺟرﻷا تﺎ����ﻣ<br />

�ﻣ �����ﻣ<br />

تﺎﻋﺎ�ﺟ ة�ﻓو �ﻳ��ﺗ<br />

�ﻬ�أ . ( ﻲ�ﻧ��ﻟا<br />

�ﻣ % 94 �ﻣ ��آأ ﺎهد���ﺑ ن��ﻳ�ﻟا ﻼ��ﺑ ���ﻣ<br />

�ﻗو . لﺎﻌ�ﻟاو<br />

سووﺎ�ﻟا ْﻲﻧﺎ��ﺑ ﻲﻓ ،2009<br />

��ﺳ ﻲﻓ ��ﻣ 2010 ��ﺳ<br />

Anthocoris nemoralis (Heteroptera: ﻲﻌ���ﻟا و�ﻌﻟا نﺎآو . ﺎﻬﻌ�ﺟ �ﺗ ﻲ�ﻟا ��ﺷﺎﻌﻟا تﺎﻓﻵا دا�ﻋأ ع���ﻣ<br />

����ﻟا هﻼﺗ ،ﺎﻬﻌ�ﺟ<br />

�ﺗ ﻲ�ﻟا ��ﻌ���ﻟا ءا�ﻋﻷا ع���ﻣ �ﻣ % 49 ـﺑ ر��ﻳ ل�ﻌ�ﺑ ًارﺎ��ﻧا ��آﻷا Anthocoridae)<br />

��ﻓ��ﻟا بﺎﺑ�ﻓ<br />

(% 20)<br />

��ﻟا �ﺳأ �ﺛ (% 26)<br />

Psyllaephagus euphyllurae (Hymenoptera: Encyrtidae)<br />

.(% 2)<br />

�����ﻟا ��ﻏ تﺎﺳ����ﻟا �ﻌﺑ ���ﻌ� ����ﺑو ا��ﺧأو (% 3)<br />

Euphyllura olivina ،ن��ﻳ�ﻟا ة��ﺷ ،ﻲﺟ�ﻟ���ﻟا ع���ﻟا ، ��ﻌ���ﻟا ءا�ﻋﻷا : ��ﺣﺎ��ﻣ تﺎ��آ<br />

__________________________________________________________________________<br />

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Tunisian Journal <strong>of</strong> Plant Protection 34 Vol. 7, No. 1, 2012

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