Research Article |
Corresponding author: Massimiliano Tini ( massimiliano.tini@uniroma3.it ) Academic editor: Sonke Hardersen
© 2017 Massimiliano Tini, Marco Bardiani, Alessandro Campanaro, Franco Mason, Paolo Audisio, Giuseppe M. Carpaneto.
This is an open access article distributed under the terms of the Creative Commons Attribution License (CC BY 4.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Citation:
Tini M, Bardiani M, Campanaro A, Mason F, Audisio P, Carpaneto GM (2017) Detection of stag beetle oviposition sites by combining telemetry and emergence traps. In: Campanaro A, Hardersen S, Sabbatini Peverieri G, Carpaneto GM (Eds) Monitoring of saproxylic beetles and other insects protected in the European Union. Nature Conservation 19: 81-96. https://doi.org/10.3897/natureconservation.19.12678
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The European stag beetle, Lucanus cervus, is a flagship species for biodiversity conservation of old-growth forests and is protected under the Habitats Directive. Although it has been the focus of active research in the last two decades, many aspects of its ecology and habitat requirements for the larvae remain poorly known, particularly to what extent certain factors limit larval development. The objectives of this preliminary work were: (1) to explore the feasibility of a non-invasive method for detecting oviposition sites; (2) to attempt the characterisation of above-ground ecological factors recorded in the oviposition sites and (3) to quantify the number of traps and operators needed for obtaining a number of beetles suitable for statistical analysis. In 2014, twelve females were followed by means of radio-telemetry to detect potential oviposition sites in a relict broadleaf forest of northern Italy. In 2015, emergence traps were set in nine sites selected from the 21 sites where females were recorded digging deeply in the soil near to dead wood during the previous year. Traps were checked during the 2015 and 2016 flight seasons. Overall, 15 stag beetles were detected (8 males and 7 females) from five emergence trap sites which were therefore regarded as real oviposition sites. All oviposition sites were characterised in terms of typology of dead wood, tree species, canopy openness, trunk diameter, dead wood volume, decomposition stage (five classes) and wood hardness (four classes). All the detected emergence sites belonged to the genus Quercus, two being from the allochthonous Q. rubra, but no preferences for a dead wood species nor for a typology were shown and a broad variation was apparent for all the considered variables. The mean values of canopy openness, diameter, dead wood volume, decay status and wood hardness were 2.54%, 51cm, 4.92m3, 3 and 3.4 respectively. These data suggested an important heterogeneity in the oviposition sites selection. Although this method (telemetry + emergence traps) provided substantial aid to finding newly emerged beetles, it required a large amount of fieldwork effort, both in terms of time and man-hours. The advantage of the method is its low degree of invasion while its drawback is the amount of effort needed. Calculations were made to assess the minimum number of operators and traps needed to gather a number of data suitable for statistical analysis. It was found that two full time operators should be able to detect about 50 potential oviposition sites in one flight season, 28 of which were expected to be real oviposition sites.
emergence traps, radio-telemetry, saproxylic insects, dead wood, oviposition sites
Detecting the breeding sites for a protected species is of great importance for its conservation and monitoring, as the knowledge of these crucial spots is needed to optimise management and surveillance.
The European stag beetle, Lucanus cervus (Linnaeus, 1758) (Coleoptera: Lucanidae), is a flagship species for conservation of forest ecosystems, particularly for the saproxylic community (
Three methods have been developed for detecting larvae in a monitoring context:
In this preliminary study, for the first time radio-telemetry was used in combination with emergence traps set to detect and describe the oviposition sites. The specific objectives were: (1) to explore the feasibility of a mildly invasive method for detecting oviposition sites in forest habitats, assuming that they were also potential development sites for the larvae; (2) to verify whether the method could be used to characterise the oviposition sites in terms of above-ground ecological factors to be used as a proxy for underground conditions of wood and (3) to quantify the average number of individuals captured by emergence traps in order to assess the minimum quantity of traps and operators needed for obtaining the amount of data suitable for statistical analysis.
The study area “Bosco della Fontana” is located in northern Italy (Marmirolo, province of Mantua, Region Lombardy) (45°12'N 10°44'E, altitude: 24–26m a.s.l.). This area is one of the last remains (233ha) of the lowland broadleaf forests in the Po valley, an intensively cultivated area. The forest has been a Biogenetic Nature Reserve since 1977, included in the Nature 2000 network as Special Protected Areas (SPAs IT20B0011) since 1998 and a Site of Community Importance (SCI IT20B0011) since 2004. This State Reserve, formerly managed by the national forestry service (CFS), is currently managed by the Ufficio Territoriale Carabinieri per la Biodiversità di Verona [= Territorial Office of Carabinieri for Biodiversity of Verona]. Since 2007, it has also been part of the Italian Long Term Ecological Research Network (LTER-Italy). Around 85% of the Reserve is covered by broadleaf forests, the remaining part consisting of grassland and a small wetland. The deciduous forest of the study area is dominated by Quercus cerris L., Q. robur L., Carpinus betulus L. and Fraxinus ornus L., with Alnus glutinosa (L.) and Fraxinus oxycarpa Vahl along the main watercourses (
In 2014, from 29th May to 10th July, twelve females were captured, radio-tagged and released for detecting potential oviposition sites. In 2015, before the emergence of the adults (early May), these sites were covered with anti-aphid plastic nets (hereafter: emergence traps) to capture newly emerged individuals and hence demonstrating the role of those dead wood spots as larval development sites. After studying emergence activities during these two years, the traps were removed at the end of the study.
The females for radio-tracking were captured mostly at sunset, by hand while they were crawling on the ground or with a hand net while they were flying. The hand net had a circular frame (50cm diameter) and a telescopic handle (up to 199cm). Each captured adult was weighed, marked ventrally with a permanent marker and with a numbered sticker on the right elytron, then equipped with a battery-powered radio transmitter (LB-2X / 0.31g; Holohil Systems Ltd., Carp, Ontario, Canada) (Figure
The radio-tagged beetles were released the next evening, at the same location from where they had been captured and at a time when there was no rainfall and the temperature was mild. The ‘homing technique’ (
In the first half of May 2015, emergence traps were set in nine potential oviposition sites based on data obtained during the previous year. Different typologies of dead wood spots were considered as potential oviposition sites: standing dead trees (SDT), lying dead trees (LDT), logs (portions of a trunk or a large branch), stumps, snags, uprooted LDTs, uprooted stumps and roots. A snag was defined as a standing dead tree without branches, with height >130cm and diameter at breast height (DBH) >10 cm; if branches were present, the snag was considered as an SDT; if the snag was less than 130cm in height, it was considered as a stump. The DBH of SDT, LDT and snags was measured.
Emergence traps were made with anti-aphid plastic nets wrapping a large dead wood spot and fixed with nails to the ground and/or to the deadwood (Figures
For each potential oviposition site, at the end of the 2014 flight season, the following environmental variables were recorded (Table
A female of Lucanus cervus marked with a numbered sticker on the right elytron and equipped with a battery-powered radio transmitter (LB-2X / 0.31g; Holohil Systems Ltd., Carp, Ontario, Canada).
Emergence traps placed on larval development sites (DS) detected in 2014 by means of radio-telemetry. A Emergence trap on Quercus sp. SDT (DS01) B Emergence trap on Quercus rubra Uprooted stump (DS10).
Number of beetles captured by emergence traps and dead wood variables. ID number of females radio-tagged in 2014 (eight on the whole) which remained at least three days in one dead wood spot, therefore considered as a potential oviposition site and a potential larval development site (DS); number of emerging males and females captured by emergence traps in 2015 and 2016 in each DS N° and environmental variables. SDT: standing dead tree; LDT: lying dead tree; Ø: diameter (for snags, SDT, LDT is considered as DBH); DW: dead wood.
Digging Female | DS N° | Emerging Males | Emerging Females | Date of emergence | Typology | Species | Canopy openness (%) | Ø (cm) | DW volume (m3) | Decay status | Wood hardness |
---|---|---|---|---|---|---|---|---|---|---|---|
F061 | DS01 | 6 | 1 | 22/06/15 | SDT | Quercus sp. | 3.06 | 72.5 | 12.97 | 3 | 4 |
F061 | DS02 | 0 | 0 | LDT | Q. robur | 4.83 | 50 | 8.39 | 2 | 3 | |
F061 | DS03 | LDT | Carpinus betulus | 0.78 | 33 | 1.03 | 3 | 3 | |||
F038 | DS04 | 2 | 27/06/15 04/07/15 |
Log | Quercus sp. | 2.94 | 47 | 0.90 | 4 | 3 | |
F060 | DS05 | 2 | 9 and 27/06/16 | Uprooted LDT | Q. rubra | 1.28 | 36.5 | 1.93 | 3 | 4 | |
F060 | DS06 | Roots | C. betulus | 4.48 | 8 | 0.01 | 1 | 1 | |||
F075 | DS07 | Stump | Quercus sp. | 2.75 | 68 | 0.32 | 5 | 4 | |||
F038 | DS08 | Snag | C. betulus | 1.02 | 52 | 0.91 | 4 | 4 | |||
F075 | DS09 | 0 | 0 | Stump | Q. rubra | 0.70 | 65 | 0.40 | 5 | 4 | |
F075 | DS10 | 1 | 2 | 27/05/15 (1M) 1/07/15(1F) |
Uprooted stump | Q. rubra | 1.28 | 52 | 4.40 | 3 | 4 |
9/06/16 (1F) | |||||||||||
F075 | DS11 | SDT | Q. rubra | 1.86 | 55 | 4.03 | 3 | 4 | |||
F075 | DS12 | Uprooted LDT | unidentified | 1.60 | 80 | 4.49 | 5 | 4 | |||
F072 | DS13 | SDT | Prunus avium | 8.61 | 60 | 4.23 | 2 | 1 | |||
F072 | DS14 | SDT | C. betulus | 4.24 | 22 | 0.53 | 1 | 1 | |||
F020 | DS15 | 1 | 27/06/16 | Uprooted LDT | Quercus sp. | 4.14 | 47 | 4.98 | 2 | 2 | |
F091 | DS16 | Log | Quercus sp. | 5.36 | 32 | 4.5 | 2 | 2 | |||
F091 | DS17 | Log | Fraxinus ornus | 11.38 | 16 | 8.14 | 3 | 2 | |||
F091 | DS18 | Stump | unidentified | 5.28 | 32 | 0.06 | 2 | 1 | |||
F013 | DS19 | 0 | 0 | Stump | unidentified | 3.76 | 45 | 0.08 | 4 | 3 | |
F013 | DS20 | 0 | 0 | Uprooted LDT | C. betulus | 12.29 | 31 | 2.48 | 1 | 1 | |
F013 | DS21 | LDT | C. betulus | 2.50 | 29 | 0.77 | 5 | 4 |
To estimate the minimum number of operators and traps needed to obtain an amount of data suitable for statistical analysis, the following values were calculated. The emergence site detection ratio was calculated by dividing the number of emergence sites detected by the number of traps used. To estimate the number of emergence sites which can be expected to yield emergence data, the number of set traps was multiplied by the emergence site detection ratio. The minimum, maximum and mean numbers of capture expected in one season were also estimated.
As this work was a preliminary study, data on which the estimates are based were few, thus the results of the number of traps and operators assessment have very broad confidence intervals and a solid statistical approach to evaluate the dead wood productivity cannot be performed.
At the end of the reproductive season for 2014, the 12 radio-tagged females allowed the detection of 21 dead wood spots as potential oviposition sites and these were covered by emergence traps. In the first half of May 2015, due to logistic constraints, only nine of these spots were chosen, based on their accessibility and feasibility of being covered by emergence traps without damaging the surrounding vegetation. In 2015 (from 27th May to 27th June) and 2016 (from 9th to 27th June), 11 (9 males and 2 females) and 4 individuals (all females) were respectively captured by the emergence traps.
During the radio-telemetry study carried out in 2014 (
Approximately half (10/21) of the dead wood spots, identified as potential oviposition sites, could be assigned to the genus Quercus with certainty: five Quercus sp., four Q. rubra and one Q. robur (Table
The highest number of beetles (7) was captured within the trap DS01 wrapping an SDT of Quercus sp. (Figure
In 2015, 29 stag beetles (20 males and 9 females) were radio-tracked by two operators, thus it was calculated that 30 females can be tracked by the same number of operators during the same period. As the radio-tracking of 12 females led to the detection of 21 potential oviposition sites, it was calculated that, with 30 females, it would be possible to detect about 50 potential oviposition sites (30 * 21 / 12 = 52.5). As five emergence sites were detected by mean of nine traps, an emergence site detection ratio of 0.56 (5 / 9 = 0.56) was calculated. Thus, by setting 50 traps, 28 sites are expected to yield emerging adults (50 * 0.56 = 28). It was calculated that 50 traps would be required for the capture of at least 28 emerging adults. For the highest number of captures, the same value as observed in the present work (seven adults) was used (28 * 7 = 196). The mean number of captures obtained by the emergence sites was three, thus for a total of 50 traps a mean number of captures of 84 stag beetles is expected (28 * 3 = 84). Considering about 30 minutes for checking one trap, one operator should be able to control about 25 traps twice a week, working about 4 hours per day. Therefore 2 operators should be able to check about 50 traps twice a week.
This study is only a pioneering approach for the combined use of telemetry and emergence traps (wrapping nets), with the aim of detecting the oviposition sites of the stag beetle. Moreover, it was also a preliminary investigation on the characteristics of dead wood spots suitable for oviposition. Emergence traps have previously been used to capture freshly emerged stag beetles by Rink and Sinsch (
According to these results, L. cervus showed a broad heterogeneity in the selection of potential oviposition sites, in agreement with previous literature (
This method could be used for improving the knowledge of dead wood requirements for larval development and for studying the first part of the adult lifespan when individuals are more active, at least concerning their dispersal movements (
In any case, the monitoring of a high number of oviposition sites, investigated by emergence traps, cannot last for more than five years because the nets hinder the females laying their eggs and the number of emergent individuals will become zero in the fifth year after the trap setting. This hindrance to egg-laying, due to the presence of nets over the oviposition site, may lead to an important impact on the reproduction of L. cervus in areas where suitable dead wood is scarce and localised. In this study area, where there is plenty of dead wood, such an impact is probably less important and the application of this method during a long-term study, could also be useful for investigating how long the dead wood is suitable for larval development.
An unsolved issue concerns the selection of the best checking time during the day, a problem which can be addressed with this working protocol, based on controls twice a week. In fact, even with more controls per day at different time slots, this problem is linked to beetle detectability under the net mesh that may vary consistently throughout the day in relation to species behaviour and to the visual acuity of the checking operator. Many studies revealed that the peak of stag beetle activity, at least in northern Italy, is in late afternoon to almost one hour after sunset (
The data available with this method, if applied to a long term study, could be of great importance for the conservation of L. cervus, as they could give information on the effects of different wood decaying stages on stag beetle larval development. The combined use of radio-telemetry and emergence traps is a useful method for finding oviposition sites and for detecting emerging individuals. Little evidence is available on the length of the larval development of the stag beetle from a single oviposition site and location. In fact, the duration of the life cycle may vary between three to five years dependent on several factors such as quality of food and climatic conditions. A long term monitoring of the emergence of stag beetles from a single site can help to calculate the duration of its suitability as a larval development site. Such knowledge could be very helpful in order to build artificial oviposition sites in a protected area, thus allowing the managing authorities to plan the dates for cutting logs or uprooting trees and could predict how long these would be suitable for larval development thus ensuring a continuing availability of essential resources.
The present paper was supported by the EU project LIFE11 NAT/IT/000252 MIPP “Monitoring Insects with Public Participation” with the contribution of the LIFE financial instrument of the European Union and by the Regional Park Agency (ARP Lazio) project “Monitoring of saproxylic and xylophagous insect populations in the protected areas of Latium”. Our greatest thanks are due to Marco Bologna, who is the Coordinator of the MIPP Beneficiary Roma Tre University. We are also grateful to the staff of the Centro Nazionale per lo Studio e la Conservazione della Biodiversità Forestale “Bosco Fontana” Carabinieri at the State Reserve “Bosco della Fontana”, for facilitations and help. In particular to Ilaria Toni for fieldwork and Emma Minari for canopy openness calculations with the Gap Light Analyser. Special thanks are due to Randi Rollins (Ogden, Utah, USA) who voluntarily helped during the fieldwork in 2014 and to Alice Malavasi for the fieldwork assistance in 2015. We thank Agnese Zauli for useful discussions and suggestions.
Special issue published with the contribution of the LIFE financial instrument of the European Union.