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Parasitoids of Ips typographus (Coleoptera: Scolytidae) - Journal of ...

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Volume 16(1), 171-173, 2012<br />

JOURNAL <strong>of</strong> Horticulture, Forestry and Biotechnology<br />

www.journal-hfb.usab-tm.ro<br />

Predators <strong>of</strong> Pityogenes chalcographus (<strong>Coleoptera</strong>:<br />

<strong>Scolytidae</strong>) in Natural Park Apuseni<br />

Fora, C.G. 1* , Lauer, K.F. 2 , Berar, C. 1 , Ştefan, C. 1 , Silivăşan, M. 1 , Lalescu, D. 1<br />

1 Banat University <strong>of</strong> Agricultural Sciences and Veterinary Medicine from Timisoara; 2 University <strong>of</strong> Applied<br />

Sciences Weihenstephan-Triesdorf<br />

* Corresponding author. Email: foraciprian@yahoo.com<br />

Abstract Alongside the European spruce bark beetle, in the Natural Park<br />

Apuseni, the small spruce bark beetle Pityogenes chalcographus encountered<br />

favourable mass reproduction conditions. Thus, massive attacks at the trees’<br />

feet were observed in different arboreta. This phenomenon will largely spread<br />

unless urgent measures for eradicating the pest hole are undertaken. This is<br />

why we have decided to investigate the parasitoid populations for Pityogenes<br />

chalcographus in the protected environment. In 2011 the most numerous<br />

species were: Nemosoma elongatum, Rhizophagus cribratus, Rhizophagus<br />

depressus, Thanasimus formicarius, Quedius plagiatus, Quedius lateralis,<br />

Quedius cruentus, Quedius xanthopus.<br />

The Natural Park Apuseni, 75.784 ha in surface, is<br />

situated in the Bihor Mountains <strong>of</strong> the Western<br />

Romanian Carpathians.<br />

The construction <strong>of</strong> the natural park took place in<br />

2004, in order to protect the karstic values <strong>of</strong> the area,<br />

the tradition and the flora and fauna biodiversity, listed<br />

as V IUCN category - Protected areas. In the protected<br />

area two zones were created. The first one is a<br />

conservation zone, occupying approximately 18% <strong>of</strong><br />

the total park surface, and the second one, a buffer<br />

zone, occupying the rest <strong>of</strong> the surface, approximately<br />

82%.<br />

In the natural park, wood vegetation is dominant<br />

and it covers approximately 75% <strong>of</strong> its total surface.<br />

Wood species are mainly represented by spruce (70%),<br />

beech (27%), fir (2%). Other resinferous species are<br />

represented, like the scots pine and the larch or<br />

deciduous species like the ash, the holm, the sycamore<br />

maple, the birch and the elm, which get mixed up with<br />

the dominant species. The spruce either forms pure<br />

arboreta or it mixes with the ash and the fir forming<br />

valuable arboreta.<br />

Together with <strong>Ips</strong> <strong>typographus</strong>, due to its size and<br />

to the fact that it predominantly attacks the crown <strong>of</strong><br />

the host trees, Pityogenes chalcographus is in its turn<br />

one <strong>of</strong> the most important predators <strong>of</strong> the spruce in<br />

Romania. That is why we have to examine it most<br />

carefully. We are motivated by the fact that, initially,<br />

the Pityogenes chalcographus attacks thin parts <strong>of</strong> the<br />

Key words<br />

Pityogenes chalcographus,<br />

predators, Natural Park<br />

Apuseni<br />

spruce’s crown, contributing thus to their<br />

supplementary destabilization and creating favourable<br />

conditions for the installation <strong>of</strong> the <strong>Ips</strong> <strong>typographus</strong><br />

species, which undertakes the final blow leading to the<br />

desiccation and death <strong>of</strong> the attacked trees. The only<br />

chance <strong>of</strong> stopping the mass reproduction <strong>of</strong> the <strong>Ips</strong><br />

<strong>typographus</strong> species as well as <strong>of</strong> the Pityogenes<br />

chalcographus pest is to transport the infested wood<br />

outside the arboreta (Feicht, 2004). Unless immediate<br />

measures are undertaken in order to stop such attacks,<br />

the effects upon natural or planted forests will be<br />

catastrophic on large surfaces (Niemeyer et al., 1995;<br />

Dengler, 1995; Weslien and Schroeder, 1996). As a<br />

general rule, the predators <strong>of</strong> the studied species are not<br />

taken into account, since it is estimated that they do not<br />

have a major influence on the abundance in number <strong>of</strong><br />

the pest species. The hypothesis that parasitoids have a<br />

decisive influence in the reduction <strong>of</strong> pest populations<br />

is not yet fully verified.<br />

Material and Method<br />

Study area<br />

The sampling areas were set in the special<br />

conservation zone <strong>of</strong> the Natural Park Apuseni, were<br />

wood material infested by the bark beetle was<br />

identified. Thus, three areas were chosen in Poiana<br />

Ponor, Valea Someşului Cald and Cheile Ordâncuşii<br />

(table 1).<br />

171


Table 1<br />

Characteristics <strong>of</strong> the plots in the Natural Park Apuseni<br />

Location<br />

Arboretum<br />

composition<br />

Average<br />

age<br />

Consistency Litter Altitude Array Declivity Tree<br />

no.<br />

Sample<br />

no.<br />

Poiana Ponor 10MO 100 0.7 4 1160 SV 21 2 8<br />

Valea Someşului<br />

Cald<br />

10MO 120 0.7 3 1175 S 20 2 8<br />

Cheile Ordâncuşii 6MO 4FA 70 0.8 3 868 SE 36 2 8<br />

Sampling method<br />

The sampling trees were chosen from those<br />

infested, and the sampling took place in two takes. The<br />

total tree number and the samples taken are presented<br />

in table 1. The first take <strong>of</strong> peaks and branches was<br />

sampled after flight I (10 June) and the second take<br />

after flight II (27 July). From each tree 4 samples were<br />

taken, thin parts <strong>of</strong> the crown (peaks and branches)<br />

infested by bugs. Each sample measured 1m in length<br />

6-12 cm in diameter, since it is a well know fact that<br />

Pityogenes chalcographus predominanatly attacks<br />

bodies less than 15 cm in diameter (Stolina, 1969).<br />

Thus, in take I 12 infested assays were gathered and in<br />

take II other 12 assays. The samples thus constituted<br />

were numbered, introduced in collectors and set in<br />

three locations near the sampling areas (Padiş, Doda<br />

Pilii, Casa de Piatră).<br />

Collectors<br />

The collectors (figura 1) are made from PE type<br />

transparent pipes, with 30 cm in diameter and 1 m in<br />

length, placed vertically. At their inferior end the<br />

collectors have a broad cone which at its base unloads<br />

in an insect collecting recipient.<br />

172<br />

Fig. 1. Collectors for insects (Natural Park<br />

Apuseni/Padiş)<br />

On their superior side, the collectors have a cloth<br />

which allows inside ventilation but does not allow the<br />

insects to exit. Once in 7 days the insects are collected<br />

in plastic recipients, they are numbered and dated. The<br />

last verifications were carried out in 19.09.<br />

Species identification<br />

The samples were analysed in the Forest<br />

Entomology laboratory <strong>of</strong> the Faculty for Horticulture<br />

and Forestry <strong>of</strong> Timişoara, from the point <strong>of</strong> view <strong>of</strong><br />

the species composition as well as from a quantitative<br />

point <strong>of</strong> view.<br />

Results and Discussions<br />

During the 3 months observation period, 8 main<br />

predator species for the Pityogenes chalcographus<br />

beetle could be identified (figura 2), as follows:<br />

Nemosoma elongatum (<strong>Coleoptera</strong>: Trogositidae),<br />

Rhizophagus cribratus (<strong>Coleoptera</strong>: Monotomidae),<br />

Rhizophagus depressus (<strong>Coleoptera</strong>: Monotomidae),<br />

Thanasimus formicarius (<strong>Coleoptera</strong>: Cleridae),<br />

Quedius plagiatus (<strong>Coleoptera</strong>: Staphylinidae),<br />

Quedius lateralis (<strong>Coleoptera</strong>: Staphylinidae), Quedius<br />

cruentus (<strong>Coleoptera</strong>: Staphylinidae), Quedius<br />

xanthopus (<strong>Coleoptera</strong>: Staphylinidae).<br />

The first three species represented 90.74% (figure<br />

2) <strong>of</strong> the total captured predator number: Nemosoma<br />

elongatum, Rhizophagus cribratus şi Rhizophagus<br />

depressus. Less represented were the species<br />

Thanasimus formicarius, Quedius plagiatus, Quedius<br />

lateralis, Quedius cruentus and Quedius xanthopus. On<br />

all three locations Nemosoma elongatum was the<br />

dominant species <strong>of</strong> main importance. Not the same<br />

can be said about the other 7 species which, together,<br />

represented less than 24% <strong>of</strong> the total captures. The<br />

Nemosoma elongatum species was encountered in<br />

every wood sample from the collectors <strong>of</strong> both take I<br />

and II, thus accounting for the greatest frequency. Next<br />

in line was the predator Rhizophagus cribratus which<br />

represented 25% <strong>of</strong> the take I samples and 67% <strong>of</strong> the<br />

take II samples. Rhizophagus depressus was present in<br />

42% <strong>of</strong> the take I samples and in 50% <strong>of</strong> the take II<br />

samples. Thanasimus formicarius came up in 25% <strong>of</strong><br />

the take I samples and in 25% <strong>of</strong> the take II samples.<br />

Quedius plagiatus was present in 20% <strong>of</strong> the take I<br />

samples and in 20% <strong>of</strong> the take II samples. Quedius<br />

cruentus came up in 17% <strong>of</strong> the take I samples and in<br />

20% <strong>of</strong> the take II samples. Quedius lateralis and<br />

Quedius xanthopus were in 8% <strong>of</strong> the take I samples<br />

and in 17% <strong>of</strong> the take II samples.


100%<br />

80%<br />

60%<br />

40%<br />

20%<br />

0%<br />

17.6. 21.6. 28.6. 5.7. 12.7. 19.7. 26.7. 1.8. 8.8. 15.8. 22.8. 29.8. 5.9. 12.9. 19.9. Total<br />

Nemosoma elongatum Rhizophagus cribratus Rhizophagus depressus Quedius plagiatus<br />

Quedius lateralis Quedius cruentus Quedius xanthopus Thanasimus formicarius<br />

Fig. 2. Specific relative abundance <strong>of</strong> predators in Poiana Ponor, Valea Someşului Cald and Cheile Ordâncuşii<br />

Although 8 predator species were identified in the<br />

wood samples in all three locations <strong>of</strong> the natural park,<br />

we can not say whether they largely influenced the<br />

Pityogenes chalcographus populations. Still, their<br />

presence indicates the fact that there is a connection<br />

between the predators and their pray in the studied<br />

perimeter.<br />

Conclusions<br />

The research carried out on the predators <strong>of</strong> the<br />

spruce bark beetle Pityogenes chalcographus, in 2011,<br />

on 3 locations from the Natural Park Apuseni (Poiana<br />

Ponor, Valea Someşului Cald and Cheile Ordâncuşii)<br />

led to the following conclusions:<br />

1. From the 8 main predator species<br />

identified, Nemosoma elongatum,<br />

Rhizophagus cribratus and Rhizophagus<br />

depressus were the best represented.<br />

Thanasimus formicarius, Quedius<br />

plagiatus, Quedius lateralis, Quedius<br />

cruentus and Quedius xanthopus<br />

represented less than 24% <strong>of</strong> the total<br />

captures.<br />

2. The frequency <strong>of</strong> the predators’ appearance<br />

in the 24 studied samples was <strong>of</strong> 100% for<br />

the Nemosoma elongatum species, 46% for<br />

Rhizophagus cribratus and Rhizophagus<br />

depressus, 25% for Thanasimus<br />

formicarius, 20% for Quedius plagiatus,<br />

18.5% for Quedius cruentus and 12.5% for<br />

Quedius lateralis and Quedius xanthopus.<br />

Acknowledgements<br />

This study was financed by the project “Postdoctoral<br />

School in Agriculture and Veterinary Medicine”,<br />

POSDRU/89/1.5/S/6237, co-financed by the European<br />

Social Fund, through the Sectorial Operational<br />

Programme for Human Resources Development 2007-<br />

2013. We would like to thank the administration <strong>of</strong><br />

Natural Park Apuseni for technical support and general<br />

permission. Also, our thanks to Mister Mircu Adrian<br />

from the Institute for Research and Forest Facilities <strong>of</strong><br />

Timişoara, who helped determine the species.<br />

References<br />

1.Dengler, K., 1995: [Is it possible to control bark<br />

beetles?] Forst und Holz. 50, 244-249.<br />

2.Feicht, E., 2004: <strong>Parasitoids</strong> <strong>of</strong> <strong>Ips</strong> <strong>typographus</strong><br />

(Col., <strong>Scolytidae</strong>), their frequency and composition in<br />

uncontrolled and controlled infested spruce forest in<br />

Bavaria. J. Pest Sci. 77, 165-172.<br />

3.Niemeyer, H., Ackermann, J., Watzek, J., 1995: Eine<br />

ungestörte Massenvermehrung des Buchdruckers (<strong>Ips</strong><br />

<strong>typographus</strong>) im Hochhartz. Forst und Holz. 50, 239-<br />

243.<br />

4.Stolina, M., 1969: The influence <strong>of</strong> bark beetles to<br />

development <strong>of</strong> structure <strong>of</strong> natural montainous forests<br />

in Western Carpathians. Lesnícky ćasopis. 15, 1, 45-<br />

63.<br />

5.Waslien, J. & Schroeder, L.M., 1996: Naturliche<br />

Dynamik des Borkenkäferbefalls nach Windwurf.<br />

Allgemeine Forst Zeitschrift für Waldwirtschaft und<br />

Umveltvorsorge. 51(19), 1052-1055.<br />

173

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