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. 2013 Mar 14;1:25. Originally published 2012 Oct 9. [Version 2] doi: 10.12688/f1000research.1-25.v2

Longhorned beetle (Coleoptera: Cerambycidae) diversity in a fragmented temperate forest landscape

Daniel M Pavuk 1,a, Andrea M Wadsworth 1
PMCID: PMC3924947  PMID: 24627763

Version Changes

Updated. Changes from Version 1

Upon the recommendation of referee Patrick Tobin, we have provided additional data that shows the relationship between log (species richness) and log (forest area). We have also updated Figure 6 to show if the respective area of each forest could explain the difference in species number. The large R2 value does suggest that larger forests tended to have larger number of cerambycid species. We also estimated the diversity of Cerambycidae using the Shannon Diversity Index value for each of the forests.  These calculated Shannon Index values allows comparisons to other studies that have examined cerambycid diversity (e.g., Ohsawa 2004; Holland 2007).

Abstract

Longhorned beetles (Coleoptera: Cerambycidae) are an important component of temperate forest ecosystems.  We trapped longhorned beetles in forests in northwest Ohio during 2008 to test the hypothesis that larger forests have greater species diversity than smaller forests.  Large forests had a significantly greater cerambycid species richness than small forests (t = 3.16. P = 0.02), and there was a significant relationship between forest size and cerambycid species richness.

Introduction

Longhorned beetles, or cerambycids, are important species in temperate forest ecosystems, due to their feeding impacts on trees. Many cerambycids feed on dead wood and therefore assist in the decomposition of dead trees in forest ecosystems. Saproxylic cerambycids (dead wood dependent) and other saproxylic beetles are thought to be useful indicators of forest biodiversity 1. We were interested in testing the hypothesis that larger forests have greater cerambycid species diversity than smaller forests in NW Ohio, a highly fragmented landscape in terms of forest ecosystems.

Methodology

  • Three types of traps (Lindgren funnel trap, Intercept Panel trap, and Window trap) were set up in each of 8 forests in northwestern Ohio. 95% ethanol was used to attract beetles ( Figure 1Figure 3).

  • We started collecting beetles in early June, and we continued to collect them until early October ( Figure 4).

  • We put the traps into 8 different forest areas. Four forests were large (>100 hectares) and four forests were classified as small (<20 hectares).

Figure 1. Intercept Panel trap used for capturing Cerambycid beetles.

Figure 1.

Figure 2. Lindgren Funnel trap used for capturing Cerambycid beetles.

Figure 2.

Figure 3. Window trap used for capturing Cerambycid beetles.

Figure 3.

Figure 4. Examples of Cerambycids species that were caught in the 8 forests sampled.

Figure 4.

Strophiona nitens (top left), Gaurotes cyanipennis (top right) Urographus fasciatus (bottom left) and Microgoes oculatus (bottom right).

Table 1. Cerambycid (Coleoptera: Cerambycidae) Species Captured in Oak Openings Preserve, 2008 (Western Lucas County, OH).

Total number of individuals of each species caught during the entire trapping period (early June to early October). Traps were positioned in the approximate center of each forest and all checked each week.

Cerambycid species Number of individuals
Strangalepta abbreviata (Germar) 35
Cyrtophilus verrucosus (Olivier) 8
Xylotechus colonus (Fabricius) 8
Clytus ruricolis (Olivier) 5
Gaurotes cyanipennis (Fabricius) 3
Neoclytus acuminatus (Fabricius) 2
Microgoes oculatus (LeConte) 2
Urographis fasciatus (DeGeer) 2
Pidonia ruficollis (Say) 1
Phymatodes testaceus (Linnaeus) 1
Sarosesthus fulminatus (Fabricius) 1
Strophiona nitens (Forster) 1
Urgleptes querci (Fitch) 1
Total number of individuals (N) 70
Species richness (s) 13

Table 2. Cerambycid (Coleoptera: Cerambycidae) Species Captured in Secor Woods, 2008 (Northern Lucas County, OH).

Total number of individuals of each species caught during the entire trapping period (early June to early October). Traps were positioned in the approximate center of each forest and all checked each week.

Cerambycid species Number of individuals
Clytus ruricola (Olivier) 7
Cyrtophilus verrucosus (Olivier) 3
Pidonia ruficollis (Say) 3
Gaurotes cyanipennis (Fabricius) 2
Microgoes oculatus (LeConte) 1
Psenocerus supernotatus (Say) 1
Trachysida mutabilis 1
Astylopsis collaris (Haldeman) 1
Total number of individuals (N) 19
Species richness (s) 8

Table 3. Cerambycid (Coleoptera: Cerambycidae) Species Captured in Wildwood Preserve, 2008 (Northern Lucas County, OH).

Total number of individuals of each species caught during the entire trapping period (early June to early October). Traps were positioned in the approximate center of each forest and all checked each week.

Cerambycid species Number of individuals
Strangalepta abbreviata (Germar) 3
Clytus ruricola (Olivier) 2
Gaurotes cyanipennis (Fabricius) 2
Microgoes oculatus (LeConte) 2
Cyrtophilus verrucosus (Olivier) 1
Analeptura lineola (Say) 1
Pidonia ruficollis (Say) 1
Total number of individuals (N) 12
Species richness (s) 7

Table 4. Cerambycid (Coleoptera: Cerambycidae) Species Captured in Pearson Park, 2008 (Eastern Lucas County, OH).

Total number of individuals of each species caught during the entire trapping period (early June to early October). Traps were positioned in the approximate center of each forest and all checked each week.

Cerambycid species Number of individuals
Clytus ruricola (Olivier) 3
Astylopsis macula (Say) 2
Urographis despectus (LeConte) 1
Cyrtophilus verrucosus (Olivier) 1
Psenocerus supernotatus (Say) 1
Total number of individuals (N) 8
Species richness (s) 5

Table 5. Cerambycid (Coleoptera: Cerambycidae) Species Captured in Bradner Preserve, 2008 (Western Wood County, OH).

Total number of individuals of each species caught during the entire trapping period (early June to early October). Traps were positioned in the approximate center of each forest and all checked each week.

Cerambycid species Number of individuals
Xylotrechus colonus (Fabricius) 2
Total number of individuals (N) 2
Species richness (s) 1

Table 6. Cerambycid Cerambycid (Coleoptera: Cerambycidae) Species Captured in Carter Woods, 2008 (Central Wood County, OH).

Total number of individuals of each species caught during the entire trapping period (early June to early October). Traps were positioned in the approximate center of each forest and all checked each week.

Cerambycid species Number of individuals
Heterachthes quadrimaculatus Haldeman 4
Xylotrechus convergens LeConte 1
Obrium maculatum (Olivier) 1
Total number of individuals (N) 6
Species richness (s) 3

Table 7. Cerambycid (Coleoptera: Cerambycidae) Species Captured in Fuller Preserve, 2008 (Central Wood County, OH).

Total number of individuals of each species caught during the entire trapping period (early June to early October). Traps were positioned in the approximate center of each forest and all checked each week.

Cerambycid species Number of individuals
Heterachthes quadrimaculatus Haldeman 4
Neoclytus acuminatus (Fabricius) 3
Total number of individuals (N) 7
Species richness (s) 2

Table 8. Cerambycid (Coleoptera: Cerambycidae) Species Captured in BGSU-ENVS Woods, 2008 (Central Wood County, OH).

Total number of individuals of each species caught during the entire trapping period (early June to early October). Traps were positioned in the approximate center of each forest and all checked each week.

Cerambycid species Number of individuals
Neoclytus acuminatus (Fabricius) 2
Sternidius variegatus (Haldeman) 1
Urgleptes signatus (Fabricius) 1
Anelaphus villosus (Fabricius) 1
Total number of individuals (N) 5
Species richness (s) 4

Table 9. Shannon Diversity Index Values for Forest Study Sites.

Forest site Shannon Index (H’ = -∑pilnpi)
Oak Openings 1.78
Secor Woods 1.81
Wildwood Preserve 1.86
Pearson Park 1.49
Bradner Preserve* -
Carter Woods 0.87
Fuller Preserve 0.68
BGSU-ENVS Woods 1.33

*It is not possible to calculate a Shannon Diversity Index value for this site, because only one cerambycid species was caught.

Results and discussion

  • Large forests had greater cerambycid species richness than small forests. ( Figure 5, Figure 6).

    The larger forests had larger Shannon Diversity index values compared to the smaller forests. The calculated Shannon Diversity Index Values allows comparisons to other studies that have focused on cerambycid diversity in forest ecosystems 1, 2.

  • Regression of log (species richness + 1) versus log (forest area + 1) indicated a strong linear relationship between cerambycid species richness and forest size (R 2 = 0.80). ( Figure 7). The large R2 value suggests that larger forests tend to have greater cerambycid species diversity than do smaller forests, perhaps due to greater amounts of resources for these beetles in the larger forests compared to the smaller ones.

  • Future research should focus on the landscape matrix and degree of isolation of forests, especially isolation of smaller forests.

  • Many other beetle species from other families were also captured (e.g., Elateridae, Curculionidae), so these data should also be examined.

Figure 5. Comparison of Cerambycid species richness between large forests and small Forests.

Figure 5.

The four large forests were Oak Opening, Secor, Pearson, and Wildwood, and the four small forests were Bradner Preserve, Fuller Preserve, Carter Woods, and Environmental Studies Woods. The t-test was significant (t = 3.16, df = 6, P = 0.02).

Figure 6. Total number of Cerambycid species caught in each forest during 2008.

Figure 6.

Oak Openings, Secor, Wildwood, and Pearson were the Large Forests, and Bradner Preserve, Carter Woods, Fuller Preserve, and ENVS Woods were the small forests.

Figure 7. Regression of Log (Cerambycid Species Richness + 1) versus Log (Forest Area + 1).

Figure 7.

Acknowledgements

We thank Mr. John Jaeger, Director of Natural Resources, Toledo, Metroparks, and Mr. Chris Smalley, Stewardship Director, Wood County, OH, Parks, for permission to do research in their parks and preserves. Thanks also to Dr. Jeff Holland, Purdue Univ., for his advice and suggestions on this research project.

Funding Statement

This research was supported by funds provided by The Department of Biological Sciences, Bowling Green State University, Bowling Green Ohio.

The funders had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.

v2; ref status: indexed

References

  • 1.Holland JD: Sensitivity of Cerambycid Biodiversity Indicators to definition of high diversity. Biodivers Conserv. 2007;16(9):2599–2609 10.1007/s10531-006-9066-1 [DOI] [Google Scholar]
  • 2.Ohsawa M: Species richness of Cerambycidae in larch plantations and natural broad-leaved forests of the central mountainous region of Japan. Forest Ecol Manag. 2004;189(1–3):375–385 10.1016/j.foreco.2003.09.007 [DOI] [Google Scholar]
F1000Res. 2014 Jan 20.

Referee response for version 2

Peter Silk 1

I have read this submission. I believe that I have an appropriate level of expertise to confirm that it is of an acceptable scientific standard.

F1000Res. 2013 Mar 18.

Referee response for version 2

Patrick Tobin 1

I have read this submission. I believe that I have an appropriate level of expertise to confirm that it is of an acceptable scientific standard.

F1000Res. 2012 Oct 17.

Referee response for version 1

Peter Silk 1

I have read this submission. I believe that I have an appropriate level of expertise to confirm that it is of an acceptable scientific standard.

F1000Res. 2012 Oct 15.

Referee response for version 1

Patrick Tobin 1

The overall merits of the study, general aspects of the experimental design, and hypothesis tested are interesting and conceptually sound.

The incredible amount of work involved in such a study is also recognized. A primary concern is that only one year of data was collected, which limits the interpretation of the findings. Measuring populations in the field over only one year, from which species richness was estimated, can be subject to annual variation that may lead to over- or underestimates of individuals in any given year. Moreover, some species of Cerambycidae may take more than one year to undergo a generation and thus these species could be undercounted. Regardless, the finding of increased richness with increased forest size confirms prior observations in related diversity studies. Also, the methods applied in this study are sound and thus provide a protocol in future endeavors.

One modification I would like to see in a revised manuscript is that instead of examining differences in richness between two categories (large versus small forests), I would prefer to see richness examined along a continuous measurement (i.e., the size of each forest), assuming that there is variation in sizes among the forests. In looking at Figure 6, I wonder if the respective area of each forest could explain the difference in species number. It also could be insightful to consider estimating diversity using established indices (e.g., Shannon, Simpson), which could help relate your work to other similar studies.

I have read this submission. I believe that I have an appropriate level of expertise to confirm that it is of an acceptable scientific standard, however I have significant reservations, as outlined above.


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