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EDGE EFFECTS OF Pinus nigra FORESTS ON ABUNDANCE AND BODY LENGHT OF Ips sexdentatus
UTJECAJ ŠUMSKOG RUBA SASTOJINE Pinus nigra NA GUSTOĆU POPULACIJE I DULJINU TIJELA Ips sexdentatusErol #AAAKKUZU, Hidayet GUZEL
Ips sexdentatus (Börner, 1776) (Coleoptera: Curculionidae: Scolytinae) is one of the most devastating pests of coniferous forests in Turkey. The pest not only kills individual host trees, but also it can outbreak readily and cause great damage under favorable conditions. Distribution and damage of this pest vary depending on some biotic and abiotic factors (e.g. edge effect, climatic factors, and host plant). The present study investigated the edge effect of Pinus nigra Arnold stands on the population level and the body length of I. sexdentatus. For this purpose, edge effects of P. nigra forests on I. sexdentatus were studied at Kastamonu Regional Directorate of State Forests located in northwestern black sea region of Turkey in the years 2012–2013. Three factors (forest interior, forest edge, and forest exterior) were used to test the effects of forest edges on the abundance and body length of I. sexdentatus. A number of five study sites were selected to deploy Lindgren® funnel-type pheromone traps. Fifteen-unit traps baited with commercial pheromone Ipssex® were set in 5 replicate blocks of three traps per block. The results of the study were as follows: 1) Double bark thicknesses and diameter of the trees along the forest edges were significantly higher than those in forest interior; 2) The number of I. sexdentatus captured from forest outside and forest edge was significantly higher than those in forest interior; 3) Body length of I. sexdentatus was significantly higher on trees along the forest edges than those in forest interior.
KEY WORDS: Pinus nigra, bark beetles, forest edges, Turkey
Bark beetles (Coleoptera: Curculionidae, Scolytinae) are considered as one of the most notorious biotic agents that cause extensive damage to conifer forests. Most bark beetles depend on dead or weakened trees but aggressive species switch to healthy trees during epidemic outbreaks (Jurc et al., 2006; Rossi et al., 2009). Population density and attack severity of bark beetles in a forest vary with so many biotic and abiotic factors, such as, improper forest management, stand composition, edge effect, wind-felled logs, long-lasting drought period.
Ips sexdentatus (Börner, 1767) (Coleoptera: Curculionidae, Scolytinae), one of the most common bark beetle species of Turkey, is a Palearctic species distributed throughout Eurasia which is capable of breeding in many coniferous
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genera, including Pinus L., Picea A. Dietr. (Pinaceae), Larix Mill. (Pinaceae), and Abies Mill. (Pinaceae) (Balachowksy, 1949; Pfeﬀer, 1995; Lopez and Goldarazena, 2012). This pest is distributed throughout Turkish conifer forests excluding Southeastern Turkey. It occurs mostly on Pinus spp. and Picea orientalis (L.) Link. having two generations per year.
Species richness and density of forest pests depend on some biotic and abiotic factors, such as forest structure, climate, topographic conditions, parasites, pathogens, and associated organisms. Fragmentation, one of the most influential factors on forest pest population dynamics, changes the spatial structure of the landscape, increases the amount of edges and induces changes in the abiotic and biotic environment (Marozas, 2014). Ewers and Banks-Leite (2013) indicated that forest fragmentation, and the creation of forest edges, exposes parts of the forest stand to external climatic conditions, reducing the ability of a forest to buffer its internal microclimate from those more extreme macroclimate conditions. Therefore, forest fragmentation and creation of forest edges cause some changes in the environment, including changes in wind, humidity, throughfall deposition, radiation, predation, parasitism, and species interactions (Murcia, 1995; Donovan et al., 1997; Brazaitis et al., 2005; Wuyts et al., 2008; Marozas et al., 2009; Marozas, 2014). For this reasons, habitat edges exert a strong influence on spatial patterns of biodiversity for many taxa in many ecosystems (Ries et al., 2004; Ewers et al., 2013).
Effects of forest edges on bark beetles are poorly understood. Many factors (e.g. tree species, bark thickness, topographic factors, and edge effect) may affect the ecology and biology of bark beetle species. Previous studies have shown that the effects of forest edges differ significantly between bark beetle species. Peltonen and Heliovaara (1999) reported that attack density, number of offspring emerging and number of new bark beetles per mother gallery were lowest in open area bolts and increased towards the forest interior. On the other hand, Jakuš et al., (2003) indicated that I. typographus usually attacks trees on forest edges and on borders of clearings.
Further studies are needed to establish the linkage between effects of forest edges and population dynamics of bark beetles. The present study investigated the edge effect of Pinus nigra Arnold stands on the population level and the body length of I. sexdentatus.
Materials and Methods
Materijali i metode
Study area – Područje istraživanja
The sampling was carried out in 2012–2013 in the Dikmen Forest District of Kastamonu Regional Directorate of State Forests located in northwestern Black sea region of Turkey (Figure 1). The study area is mostly covered by natural P. nigra stands. In the study area, mean tree age was 47±7.35, mean tree diameter was 26±6.12 cm, and mean tree density was 2158 stems/ha. The altitude of the study area various from 1340 m to 1400 m (a.s.l.). Climate is generally characterized by cold winters and semi-arid summers. In winter, the ground is covered with snow, which accumulated more heavily on the upper elevations than lower elevations in the study area. The annual mean precipitation is 478.5 mm and the annual mean temperature is 9.8 °C. Average monthly temperature ranges from –1.0 °C in January to 20.3 °C in July (1954–2013 meteorological data from Kastamonu Meteorology Station) (Anonymous, 2015).
Sample sites and field methods – Pokusne plohe i terenski rad
In this study, three factors (forest interior, forest edge, and forest exterior) were determined to evaluate the effects of forest edges on the abundance and body length of
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In this study, edge effect of P. nigra forests on the population size of I. sexdentatus was analyzed. One-way analysis of variance (ANOVA) indicated significant differences (p<0.05) in the number of I. sexdentatus captured by pheromone traps across the three sample sites (forest edge, forest interior and forest outside) (Table 5, Table 6).
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The results from the LSD multiple comparison test showed that the number of I. sexdentatus captured outside of the forest and forest edge was significantly (p<0.05) higher than those from forest interior (Table 6).
Body length of I. sexdentatus was measured to test the effect of forest edge via bark thickness and stem temperature regime on their growth. We found that mean body length of the pest was 5.76±0.07 mm at the forest edge, 5.55±0.08 mm at the forest interior, and 5.98±0.06 mm at the forest exterior in the study area (Figure 3). Therefore, body length of I. sexdentatus was significantly (p<0.05) higher on trees along the forest edges than those in forest interior (Table 7, Table 8).
Bark is an important part of the tree that provides protection of the inner living tissues against climatic effects, air pollution, mechanical damage, and biotic agents that attack the tree (Michel et al., 2011; Mmolotsi et al., 2012). Bark anatomy and the physiological condition of a potential host tree are crucial for the success of a bark beetle attack (Wermelinger, 2004). Bark thickness, as an important factor in breeding success for I. sexdentatus, generally increases with stem diameter and tree age. As forests age they become more vulnerable to agents of disturbance, such as high winds, fire, fungi, and bark beetles (Christiansen et al., 1987). In the present study, DBT and DBH of the trees along the forest edges were significantly greater than those in forest interior. Similar findings were obtained for Pinus radiata D. Don. in New Zealand (Berg, 1973), Quercus robur Linnaeus, and Fraxinus excelsior Linnaeus in the eastern part of the Czech Republic (Sálek et al. 2013). Gorte (2009) indicated that the adult mountain pine beetles (Dendroctonus ponderosae Hopkins, 1902), disperse with preference for trees of larger diameter
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I. sexdentatus. Five study sites were chosen to deploy Lindgren® funnel-type pheromone traps baited with commercial pheromone Ipssex®. Fifteen-unit pheromone traps were set in 5 replicate blocks of three traps per block (Figure 2). Experimental periods ranged from early to mid-summer, comprising the part of the flight period of I. sexdentatus. Traps were placed from 02 June to 28 July 2012 along the forest edges. All traps were fastened to wooden sticks with the top of the trap at 1.5 m above the ground. The quantification of captured insects took place every 7-10 days by counting insects, or by measuring volume of the insects if the catch were greater than 500 insects per trap.
In each study area, a total of 60 pine trees (stem >8 cm diameter at breast height (DBH), 1.3 m above ground level) were measured for DBH and double bark thickness (DBT). DBT and DBH were measured with a bark gauge and a diameter tape, respectively. After that, mean DBT and mean DBH were calculated. Bark thickness values were determined by averaging two bark thickness measurements taken at the angle of 90 degree. On standing trees, DBT is the double of averaging two measurements (Sonmez et al. 2007).
Statistical analysis – Statistička raščlamba
All statistical analyses were performed using SPSS® 19.0 for Windows®. We analyzed the edge effects on I. sexdentatus abundance and body length of the developed adults using one-way analysis of variance (ANOVA). Independent samples t-test was applied to test the DBT of the trees. If differences were significant, a LSD multiple comparison test was performed to identify variation between pairs of means. Means were considered to be significantly different when P<0.05.
An aim of this research is to find out whether forest edges had any significant effect on the DBT and DBH of the trees. This study showed that DBT of the trees along the forest edges were significantly higher than those in forest interior (p<0.05) (Table 1 and 2).
Diameter of tree trunks (DBH) along the forest edge and in the forest interior significantly differentiate (p<0.05) in the study area (Table 3, 4). Diameter of tree trunks (DBH) was higher along the forest edge.
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(thicker trees have thicker phloem, and thus more food) and trees under stress (e.g., injured, diseased, or suffering from drought, and thus offering less resistance to attack).
We found that the number of I. sexdentatus captured from forest outside and forest edge was significantly higher than those from forest interior. Previous studies have shown that compared with the forest-interior environment, solar incidence on the edges brings about an increment in light intensity and it’s duration and, therefore, both soil and air temperatures can be both higher and more variable (Wales, 1972; Ranney et al., 1981; Lovejoy et al., 1986; Williams-Linera, 1990; Brothers and Spingarn, 1992). Bark beetle development is directly affected by phloem temperature, which in turn is dependent on air temperature and direct solar radiation (Wermelinger and Seifert, 1999). Therefore, sunlit trees are preferably attacked, especially after abrupt increases in solar radiation levels (Jakuš, 1998; Lobinger and Skatulla, 1996; Wermelinger, 2004).
In this study, body length of the pest was used to characterize I. sexdentatus populations in relation to the breeding sites (forest edge and forest interior). Body length of I. sexdentatus was significantly higher on trees along the forest edges than those in forest interior. Grodzki (2004) conducted a research on a similar subject concerning closely related I. typographus on Picea abies (Linneaus). Grodzki (2004) indicated that the reaction of I. typographus populations to better environmental conditions is expressed as an increase in the infestation density on trees and greater body length of beetles (Grodzki, 2004).
I. sexdentatus is distributed naturally throughout Europe, Northern Asia, South and Southeast Asia. Forest fragmentations and forest edges influence the abundance and body length of the pest in its distribution range because they may alter forest structure, species composition, biodiversity, microclimate, physical and chemical properties of soil. In this study, we examined the edge effects of P. nigra forests on abundance and body length of I. sexdentatus. We revealed that forest edges may contribute to I. sexdentatus population increases and also cause increase in body length of the pest.
This study is funded by the Scientific Research Projects Committee of Kastamonu University with the project number KUBAP-01/2012-09.
Anonymous, 2015. Resmi istatistikler (illerimize ait istatistiki veriler); http://www.dmi.gov.tr/veridegerlendirme/il-ve-ilceler-istatistik.aspx?m=KASTAMONU.
Balachowksy, A., 1949: Faune de France, Volume 50: Coleopteres Scolytides, Federation Francaise des Societes de Sciences, 320 p., Paris.
Berg, P. 1973: Silviculture of Pinus radiate stand edge trees at Woodhill Forest. New Zeal. J. For. 18(1): 115-121.
Brazaitis, G., J.M. Roberge, P. Angelstam, V. Marozas, K. Petelis, 2005: Age-related effects of clear-cutold forest edges on bird communities in Lithuania. Scand. J. For. Res. 20 (6): 59–68.
Brothers, T.S., A. Spingarn, 1992: Forest fragmentation and alien plant invasion of central Indiana old-growth forests. Conserv. Biol. 6:91-100.
Christiansen, E., R.H. Waring, A.A. Berryman, 1987: Resistance of conifers to bark beetle attack: Searching for general relationships. For. Ecol. Manag. 22: 89-106.
Donovan, T.M., P.W. Jones, E.M. Annand, F.R. Thompson III, 1997: Variation in local-scale edge effects: mechanisms and landscape context. Ecology 78: 2064–2075.
Ewers, R.M., C. Banks-Leite, 2013: Fragmentation impairs the microclimate buffering effect of tropical forests. Plos One, 8(3): 1-7.
Ewers, R.M., S. Bartlam, R.K. Didham, 2013: Altered species interactions at forest edges: contrasting edge effects on bumble bees and their phoretic mite loads in temperate forest remnants. Insect Conserv. Divers. (6): 598–606.
Gorte, R.W., 2009: Mountain Pine Beetles and Forest Destruction: Effects, Responses and Relationship to Climate Change. Washington, D.C.: Congressional Research Service.
Grodzki, W, 2004: Some reactions of Ips typographus (L.) (Col.: Scolytidae) to changing breeding conditions in a forest decline area in the Sudeten Mountains, Poland. J. Pest Sci. 77: 43-48.
Jakuš, R., 1998: Types of bark beetle (Coleoptera: Scolytidae) infestation in spruce forest stands affected by air pollution, bark beetle outbreak and honey fungus (Armillaria mellea). Anz. für Schädlingskunde 71: 41-49
Jakuš R, F. Schlyter, Q.H. Zhang, M, Blaženec, R. Vavercák, W. Grodzki, D. Brutovsky, E. Lajzová, M. Turcáni, M. Bengtsson, Z. Blum, J.C. Gregoiré, 2003: Overview of development of an anti-attractant based technology for spruce protection against Ips typographus: from past failures to future success. J. Pest Sci. 76: 89-99.
Jurc M., M. Perko, S. Džeroski, D. Demšar, B. Hrašovec, 2006: Spruce bark beetles (Ips typographus, Pityogenes chalcographus, Col.: Scolytidae) in the Dinaric mountain forests of Slovenia : monitoring and modeling. Ecol. Model., 194, 1/3: 219-226.
Lobinger, G., U. Skatulla, 1996: Untersuchungen zum einfluss von sonnenlicht auf das schwärmverhalten von borkenkäfern. Anz. für Schädlingskunde 69: 183-185.
Lopez, S., A. Goldarazena, 2012: Flight dynamics and abundance of Ips sexdentatus (Coleoptera: Curculionidae: Scolytinae) in different sawmills from Northern Spain: Differences between Local Pinusradiata (Pinales: Pinaceae) and Southern France incoming P. pinaster timber. Hindawi Publishing Corporation Psyche, Article ID 145930, 6 pages doi:10.1155/ 2012/145930.
|ŠUMARSKI LIST 9-10/2015 str. 43 <-- 43 --> PDF|
Lovejoy, T., R. Bierregaard, J. Rylands, J. Malcolm, C. Quintela, L. Harper, K. Brown, A. Powell, G. Powell, H. Schubart, M. Hays, 1986: Edge and other effects of isolation on Amazon forest fragments. In: M. Soule (Editor), Conservation Biology. The Science of Scarcity and Diversity. Sinauer, Sunderland, MA, pp. 257-285.
Marozas V., K. Pėtelis, G. Brazaitis, J. Baranauskaitė, 2009: Early changes of ground vegetation in fallow deer enclosure. Balt. For. 15: 268–272.
Marozas, V., 2014: Effect of the coniferous forest – grassland edge on ground vegetation in the mixed European forest zone, Lithuania. Dendrobiology, 71: 15-22.
Michel, A.K., S. Winter, A. Linde, 2011: The effect of tree dimension on the diversity of bark microhabitat structures and bark use in Douglas-fir (Pseudotsuga menziesii var. menziesii). Can. J. For. Res. 41: 300–308.
Mmolotsi, R., I. Kopong, M. Rampart, 2012: Bark Thickness and Diameter Variation in Spirostachys africana, a Multipurpose Tree Commonly used in Households in Southern Botswana. 1:539 doi:10.4172/scientificreports.539.
Murcia, C., 1995: Edge effects in fragmented forest: implications for conservation. Trends Ecol. Evol. 10: 58–62.
Peltonen, M., K. Heliövaara, 1999: Attack density and breeding success of bark beetles (Coleoptera, Scolytidae) at different distances from forest-clearcut edge. Agric. For. Entomol. 1: 237-242.
Pfeﬀer, A., 1995. Zentral-und westpalaearktische Borken- und Kenkafer, Pro Entomologia, c/o Naturhistorisches Museum Basel, 310 p., Basel.
Ranney, J., M. Bruner, J. Levenson, 1981: The importance of edge in the structure and dynamics of forest islands. In: R. Burgess and D. Sharpe (ed), Forest Islands Dynamics in Man-dominated Landscapes. Springer, p. 67-95, New York.
Ries, L., R.J.Jr. Fletcher, J. Battin, T.D. Sisk, 2004: Ecological responses to habitat edges: mechanisms, models and variability explained. Annu. Rev. Ecol. Evol. Syst. 35: 491–522.
Rossi, J.P., J.C. Samalens, D. Guyon, I. van Halder, H. Jactel, P. Menassieu, D. Piou, 2009: Multiscale spatial variation of the bark beetle Ips sexdentatus damage in a pine plantation forest (Landes de Gascogne, Southwestern France). For. Ecol. Manag. 257: 1551–1557.
Šálek, L., D. Zahradník, R. Marušák, L. Jerábková, J. Merganicˇ, 2013. Forest edges in managed riparian forests in the eastern part of the Czech Republic. For. Ecol. Manag. 305: 1–10.
Sonmez, T., S. Keles, F. Tilki, 2007: Effect of aspect, tree age and tree diameter on bark thickness of Picea orientalis. Scand. J. For. Res. 22: 193-197.
Wales, B., 1972: Vegetation analysis of northern and southern edges in a mature oak-hickory forest. Ecol. Monogr. 42: 451-471.
Wermelinger, B., M. Seifert, 1999: Temperature-dependent reproduction of the spruce bark beetle Ips typographus, and analysis of the potential population growth. Ecol. Entomol. 24: 103–110.
Wermelinger, B., 2004: Ecology and management of the spruce bark beetle Ips typographus – a review of recent research. For. Ecol. Manag. 202: 67-82.
Williams-Linera, G., 1990: Vegetation structure and environmental conditions of forest edges in Panama. J. Ecol. 78: 356-313.
Wuyts K., A. De Schrijver, J. Staelens, L. Gielis, J. Vandenbruwane, K. Verheyen, 2008: Comparison of forest edge effects on throughfall deposition in different forest types. Environ. Pollut. 156: 854–861.
Ips sexdentatus (Börner, 1776) (Coleoptera: Curculionidae: Scolytinae), velik šestozubi borov potkornjak, jedan je od najvažnijih štetnika iz porodice potkornjaka na području Turske. Ne samo da je sposoban napasti pojedinačna stable, već u povoljnim okolnostima može ući u prenamnoženja uzrokujući štete većih razmjera. Prostorna raširenost i štetnost ovog štetnika varira ovisno o različitim biotskim i abiotičkim čimbenicima (primjerice utjecaju šuimskog ruba i fragmentiranosti, klimi i vitalitetu biljaka domaćina). Provedeno istraživanje imalo je za cilj utvrditi utjecaj šumskog ruba sastojina crnog bora (Pinus nigra) na populacijsku gustoću i duljinu tijela (veličinu) potkornjaka I. sexdentatus. Za ovu je svrhu postavljena serija pokusa u regiji Kastamonu na sjeverozapadu crnomorske obale Turske u razdoblju od 2012. do 2013. godine. Tri mikropozicije na pet pokusnih lokaliteta testirane su na spomenuta dva obilježja I. sexdentatus: unutrašnjost šume, šumski rub i otvoreni prostor izvan šume (Slika 2). Odrasli potkornjaci hvatani su linijski postavljenim lijevkastim tipom feromonskih klopki (Lindgren®) opremljenim feromonom Ipssex®. Klopke sastavljene od 15 lijevkastih segmenata postavljene su u blokovima od 5 replikacija s tri klopke po bloku.
Rezultati istraživanja mogu se svesti na sljedeće: 1) Dvostruka debljina kore i promjer stabala na šumskom rubu veća je od stabala u unutrašnjosti sastojine; 2) Broj ulovljenih imaga I. sexdentatus izvan šume i na šumskom rubu značajno je veći od ulova u unutrašnjosti sastojine; 3) Duljina tijela I. sexdentatus iz kore stabala na šumskom rubu značajno je veći od jedinki izdvojenih iz kore stabala u unutrašnjosti sastojine.
KLJUČNE RIJEČI: Pinus nigra, potkornjaci, šumski rubovi, Turska