Research Article |
Corresponding author: Philipp Andreas Unterweger ( philipp.unterweger@biodiversitaetsplanung.de ) Academic editor: Jack Neff
© 2016 Laura Wastian, Philipp Andreas Unterweger, Oliver Betz.
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:
Wastian L, Unterweger PA, Betz O (2016) Influence of the reduction of urban lawn mowing on wild bee diversity (Hymenoptera, Apoidea). Journal of Hymenoptera Research 49: 51-63. https://doi.org/10.3897/JHR.49.7929
|
To analyse the effects of reduced green space management in urban areas on the biodiversity of insects, we compared intensely mowed lawns (mowed 12 times per year) with meadows under reduced maintenance (mowed only twice per year) in the city of Tübingen (Baden-Württemberg, Germany). Over the entire field season, 177 wild bee individuals representing 43 species were caught using sweep nets. Areas with reduced maintenance showed significantly higher total species numbers and biodiversity indices. Our research supports the initiative “Bunte Wiese (Colourful Meadow) - Species Diversity in Public Greenspaces” of the University of Tübingen, which is campaigning for the enhancement of species diversity in public urban greenland areas by reorganising intensive mowing into a “twice a year” programme.
Colourful meadow, conservation, grassland, meadow, mowing, urban ecology, urban green space, wild bees
Urbanisation is one of the major environmentally relevant phenomena of our time. The expansion of urban areas is rapidly increasing. In western Germany, the areas settled by humans has increased by about 140% in the past fifty years (Kompakt 2011, Russel 2005). 13.6% of the area of Germany is covered by settlements and infrastructure (
Urban areas can offer classic nature, providing a wide range of different small habitats with positive impacts on, for instance, flower-visiting insects (
We have investigated the influence of maintenance reduction on public grasslands in the city of Tübingen (Germany, Baden-Württemberg) on the occurrence of flower-visiting wild bees. We assume that the simple reduction of the lawn mowing frequency compared with an intense monthly mowing regime in cities can make an important contribution to the international efforts to reduce the loss of biodiversity (
If mowing events occur too frequently and at inappropriate times, they can cause significant harm on the biodiversity of both plants and insects (
Unimproved flower-rich grassland is one of the most important habitats for bumble bees. However, in western Europe, it has been largely lost to agriculture (
In 2010, both students and employees of the University of Tübingen founded a pressure group to support national and international aims to protect biodiversity (
In the present work, we investigate the influence of a reduced mowing regime on the diversity of flower-visiting wild bees in urban green spaces. We hypothesize that (1) endangered species are strongly linked to areas with reduced maintenance and (2) the number of both species and individuals is significantly higher in these areas.
The locations of the five sampling areas in the city of Tübingen (Baden-Württemberg, Germany) are shown in Figure
Map of the sampling sites in the urban area of Tübingen. A = Europastraße, B = Sand Süd, C = Sand Courtyard, D = university institute of political science, E = Julius-Wurster-Straße and X the city centre. Each area was divided into an intensely mowed lawn and an area with reduced maintenance (two cuts per year). Provided by OpenStreetMap contributors.
The climatic conditions in 2010 did not significantly differ from those of the past six years. The average annual temperature was about 8.7 °C. In July, the average temperature was 19.9 °C. Rainfall was rare at the beginning of the year. However, this changed in May (99 mm m-2). In June and July, the weather conditions were wetter than usual but returned to normal in September.
We followed the sampling methods of
Bees that could not be determined to species in the field were killed with ethyl acetate and carefully prepared. Genitalia were prepared if necessary. Determinations were performed according to the five volumes of
To compare the two types of maintenance, we also used the Shannon Index and Evenness to evaluate the number of species and individuals (
We performed Wilcoxon-tests to check the differences between the intensely mowed lawns and the areas with reduced maintenance. All statistical analyses were performed with SPSS (SPSS 22, IBM).
Over the entire sampling time, on the five pairs of sampling sites, 177 wild bee individuals representing 43 species (Table
List of bee species recorded from the five pairs of study plots. The red list categories correspond to the classifications of IUCN (3 = =vulnerable, V =near threatened). The numbers of captured individuals is also given (A = intense mowing, B = reduced management). The months of capture are marked in Roman numerals (I = January, II = February etc.). The dominance Di and the sampling sites are presented in the last two columns. The sampling sites are named as in Figure
Scientific name | Red List GER | Red List BW | No. of ind. A | No. of ind. B | month | Di | Sampling sites |
---|---|---|---|---|---|---|---|
Andrena cineraria (Linnaeus, 1758) | 3 | 4 | IV,V | 3.95 | B1,B2,D1,D2,E1 | ||
Andrena gravida (Imhoff, 1832) | 5 | 1 | IV,V | 3.39 | B1,E1,D1,D2 | ||
Andrena haemorrhoa (Fabricius, 1781) | 0 | 1 | IV,V | 0.56 | E2 | ||
Andrena labiata (Fabricius, 1781) | 2 | 1 | V | 1.69 | B1,C1,C2 | ||
Andrena minutula (Kirby, 1802) | 0 | 1 | V,VI | 0.56 | B2 | ||
Andrena minutuloides (Perkins, 1914) | 0 | 5 | VI,VII,VIII | 2.82 | A2,B2 | ||
Andrena nitida (Müller, 1776) | 2 | 0 | IV,V | 1.13 | C1,D1 | ||
Andrena ovatula (Kirby, 1802) | 1 | 0 | V | 0.56 | E1 | ||
Andrena strohmella (Stoeckhert, 1928) | 0 | 1 | IV | 0.56 | D2 | ||
Andrena subopaca (Nylander, 1848) | 2 | 0 | IV,V,VI | 1.13 | A1,B1 | ||
Andrena ventralis (Imhoff, 1832) | 2 | 0 | IV | 1.13 | A1 | ||
Anthophora plumipes (Pallas, 1772) | 1 | 2 | IV,V | 1.69 | A1,C2,D2 | ||
Bombus hortorum (Linnaeus, 1761) | 0 | 1 | V-IX | 0.56 | D2 | ||
Bombus humilis (Illiger, 1806) | vu, 3 | vu, V | 0 | 2 | VI,VII,VIII | 1.13 | A2,B2 |
Bombus hypnorum (Linnaeus, 1758) | 0 | 3 | V,VIII | 1.13 | E2,D2 | ||
Bombus lapidarius (Linnaeus, 1758) | 2 | 3 | V-VIII | 2.82 | B2,C2,D1,D2 | ||
Bombus lucorums.l. (Linnaeus 1761) | 1 | 0 | VIII | 0.56 | D1 | ||
Bombus pascuorum (Scopoli, 1763) | 6 | 15 | V-IX | 11.86 | B2,A1,A2,C2,D1,D2 | ||
Bombus pratorum (Linnaeus, 1761) | 1 | 2 | V | 1.69 | C1,C2,D2 | ||
Bombus sylvarum (Linnaeus, 1761) | vu, V | vu, V | 0 | 2 | VIII,IX | 1.13 | B2,A2 |
Bombus terrestriss.l. (Linnaeus, 1758) | 0 | 5 | V-VIII | 2.82 | B2,A2,C2 | ||
Chelostoma florisomne (Linnaeus, 1758) | 6 | 8 | V,VI | 7.91 | B1,B2,C1,C2,D2 | ||
Colletes similis (Schenck, 1853) | vu, V | 0 | 1 | V | 0.56 | B2 | |
Eucera nigrescens (Pérez, 1879) | 0 | 2 | V | 1.13 | E1 | ||
Halictus simplex (Blüthgen, 1923) | 0 | 2 | V,VI,IX | 1.13 | B2,A2 | ||
Halictus tumulorum (Linnaeus, 1758) | 9 | 6 | V-IX | 5.65 | B1,B2,D1,D2,E1,E2 | ||
Halticus scabiosae (Rossi, 1790) | vu, V | 0 | 3 | V | 0.56 | B2 | |
Heriades truncorum (Linnaeus, 1758) | 0 | 2 | VI | 1.13 | D2 | ||
Hoplitis leucomelana (Kirby, 1802) | 0 | 2 | VI | 1.13 | D2 | ||
Hylaeus communis (Nylander, 1852) | 0 | 3 | VIII | 1.69 | B2,A2,D2 | ||
Hylaeus gredleri (Förster, 1871) | 0 | 1 | VII-IX | 1.13 | A2 | ||
Hylaeus punctatus (Brullé, 1832) | 0 | 2 | VIII | 1.13 | A2,B2 | ||
Lasioglossum calceatum (Scopoli, 1763) | 1 | 1 | V,VIII,IX | 1.13 | C1,D2 | ||
Lasioglossum glabriusculum (Morawitz, 1872) | vu, V | 0 | 2 | IV, VII-IX | 1.13 | A2 | |
Lasioglossum laticeps (Schenck, 1870) | 2 | 3 | IV,V,VII,VIII | 2.82 | B2,C1,C2 | ||
Lasioglossum leucozonium (Schrank, 1781) | 2 | 2 | V,VIII | 2.26 | C1,D1,D2 | ||
Lasioglossum morio (Fabricius, 1793) | 4 | 5 | IV,VII-IX | 5.08 | D1,D2 | ||
Lasioglossum pauxillum (Schenck, 1853) | 9 | 14 | V-IX | 7.91 | B2,A2,E1,C1,C2,D2,E2 | ||
Lasioglossum villosulum (Kirby, 1802) | 1 | 0 | VII-IX | 1.69 | B1,D1 | ||
Megachile circumcincta (Kirby, 1802) | vu, V | vu, V | 0 | 1 | V,VI | 0.56 | B2 |
Melecta albifrons (Forster, 1771) | 1 | 1 | IV,V | 1.13 | D1,D2 | ||
Osmia bicornis (Linnaeus, 1758) | 6 | 8 | IV,V | 9.60 | B1,B2,C1,C2,D1,D2 | ||
Osmia cornuta (Latreille, 1805) | 0 | 1 | IV | 0.56 | C2 |
The average number of dicotyledon species was to 13,6 species on the intensely mowed plots and to 15,8 species on the extensively mowed sites.
The comparison of intensely mowed lawns with areas with reduced maintenance show significant differences, both at the species and at the individual level. Figure
The comparison of the Shannon Index revealed a significant difference between lawns and areas with reduced maintenance (p < 0.05). On all sampling sites, Evenness was between 0.81–0.95.
Our results indicate that a reduction in mowing intensity has impacts on the wild bee fauna at various levels. Figure
Even the number of individuals of more common species can rapidly decline in areas of high mowing intensity. As seen in Table
The number of sampled species had its maximum in May and August (IV = 15, V = 28, VI = 15, VII = 13, VIII = 20, IX = 11), a finding that indicates that mowing before the end of May has the greatest effect on urban wild bee populations. The importance of unmown summer meadows follows from the second peak in species richness in August. Wild bees often show a high preference for certain plant species and will benefit from the long-term reduction of maintenance (
Our results further support the conclusions drawn from studies of the initative “Bunte Wiese Tübingen” on other insect orders such as Orthoptera, Hemiptera, Coleoptera and Lepidoptera showing that a reduction of the maintenance of public urban green spaces supports the diversity of insects. Such actions are relatively easy to achieve in accord with local policy makers and form an effective way of meeting the demands of the global aspiration to stop the loss of biodiversity. The reduction of maintenance and the establishment of natural (infrequently, rather than intensely, mowed) green spaces and waysides can have a significant impact on mitigating the biodiversity crisis, even in our highly populated and highly degraded areas (low abundance and diversity numbers reported here indicate reduced mowing can lessen the impacts of urbanization but does not cure them) and, at the same time, increase the awareness of ecological problems occurring in urban human populations.
The English of this manuscript was corrected by Dr. Theresa Jones. Hans Schwenninger (Stuttgart) verified the species identifications. We thank the editor and our anonymous reviewers for their helpful comments.