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(Hemiptera) Assemblages Following Heath and Grassland Habitat Creation on Lowland Farmland

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(Hemiptera) Assemblages Following Heath and Grassland Habitat Creation on Lowland Farmland Ann. Zool. Fennici 57: 1–10 ISSN 0003-455X (print), ISSN 1797-2450 (online) Helsinki 19 November 2019 © Finnish Zoological and Botanical Publishing Board Re-establishment of Auchenorrhyncha (Hemiptera) assemblages following heath and grassland habitat creation on lowland farmland Sandra Åhlén Mulio & Andrew Cherrill* Department of Crop and Environment Sciences, Harper Adams University, Shropshire, TF10 8NB, United Kingdom (*corresponding author’s e-mail: [email protected]) Received 12 Aug. 2019, final version received 2 Nov. 2019, accepted 2 Nov. 2019 Mulio, S. Å. & Cherrill, A. 2020: Re-establishment of Auchenorrhyncha (Hemiptera) assemblages following heath and grassland habitat creation on lowland farmland. — Ann. Zool. Fennici 57: 1–10. Leafhopper and planthopper (Auchenorryncha) assemblages were investigated at a lowland site in the United Kingdom supporting acidic and mesotrophic grasslands reverting from agricultural use, alongside remnants of semi-natural acidic heath. Further areas of agricultural land had been subject to soil inversion with or with- out addition of sulphur, heather brash and seed material to establish acidic heath or mesotrophic grassland. Eleven years after work commenced, Auchenorrhyncha assemblages of heath created on former arable land were most closely related to those of remnant semi-natural heath and reversion acidic grasslands. In contrast, an area of heath created on former pasture eight years previously, and at an earlier stage of devel- opment, supported an insect assemblage more closely related to those of mesotrophic grasslands. Time since creation, former land use and degree of isolation are identified as potential factors determining the similarity between Auchenorrhyncha assemblages of the remnant and created heaths. Introduction Major impediments to the restoration of degraded heath, and creation of new heath on Lowland heath is a plagioclimax habitat that agricultural land, are elevated pH and nutrient developed on typically acidic infertile soils levels, along with damage to the natural soil pro- over many hundreds of years of livestock graz- file, presence of ‘weeds’ and lack of propagules ing, burning and turf cutting in the absence to establish heath vegetation. These issues were of artificial fertilisers (Webb 1998). The UK identified in pioneering studies of the 1980s and has an internationally important lowland heath 1990s (Putwain et al. 1982, Clarke 1997, Gilbert resource, yet much has been lost since the begin- & Anderson 1998). Considerable progress has ning of the 20th century due to land use change, since been made in the development of tech- including forestry, housing and the contrasting niques to overcome these challenges. Techniques processes of intensification of agriculture and the include application of soil amendments (such as abandonment of marginal land (English Nature elemental sulphur) to reduce pH, turf stripping 2002). and deep-ploughing to remove or bury undesir- This paper was edited by Kai Ruohomäki 2 Mulio & Cherrill • ANN. ZOOL. FENNICI Vol. 57 able seeds and nutrient-rich top-soil, continued of created heath resemble those of the surviving crop production and harvesting to deplete key remnants of semi-natural habitat eleven years nutrients in the soil, and importing seed and plant after habitat creation began. material to aid recovery of the vegetation (Marrs et al. 1998, Webb 2008, Glen et al. 2017). Most studies have focussed on soil and vegetation to Material and methods assess the success of interventions. In contrast, few studies have investigated the recovery of Study site invertebrate assemblages following creation of lowland heath, or indeed upland heath and moor- Prees Heath Common Nature Reserve land (Webb 2008, but see Littlewood et al. 2006, (52°55´37´´N, 2°39´25´´W) in Shropshire, Forup et al. 2008, Brochard & Fartmann 2014). United Kingdom, is an area of approximately Invertebrates have important functions 60 ha (altitude 90 m a.s.l.) owned and managed within ecosystems and are also valuable indica- by Butterfly Conservation for the nationally tors of the success of habitat creation (Majer et threatened silver-studded blue butterfly Plebe­ al. 2002). Among the invertebrates, Auchenor- jus argus (Davis et al. 2011). In 1880, most of rhyncha are a candidate group with which to the site supported grazed lowland heath, but by investigate, and monitor, the success of habitat 1991 only around 5 ha of heathland vegetation creation (Biedermann et al. 2005). Auchenor- remained and this area, along with 20 ha of rhyncha are a group encompassing two subor- semi-natural acidic grassland, was given statu- ders of Hemiptera (Cicadomorpha and Fulgoro- tory protection as a Site of Special Scientific morpha) and known as leafhoppers, planthop- Interest (SSSI) (a designation used to protect pers, froghoppers, treehoppers and cicadas. They the UK’s most important wildlife sites). The are exclusively phytophagous and feed variously majority of the original heathland had been lost on phloem sap, xylem sap and mesophyll cell as a result of military training (including an contents of vascular plants (Nickel 2003). They airfield in the 1940s), woodland encroachment have been shown to be useful indicators of envi- and, from the 1960s, intensive cultivation for ronmental and botanical change because (a) the beans, wheat, potatoes and oilseed rape. After group includes species with diets ranging from 1991, intensive cultivation continued in some generalist to highly host specific, (b) community undesignated areas, with addition of chicken composition responds to management, botanical manure, until the whole site was purchased by and abiotic variation, (c) they are numerically Butterfly Conservation in 2006. Since then, work abundant in grassland and heath habitats, and has been undertaken to create areas of heath (d) taxonomy and sampling methods are well- and meadow vegetation using combinations of established (Biedermann et al. 2005). deep ploughing to invert and bury nutrient-rich This paper reports on a survey of Auche- top-soils, addition of sulphur to reduce soil pH, norrhyncha at Prees Heath Common Nature and addition of seeds, and heather brash. The Reserve, a lowland site in the English West dominant dwarf shrub at Prees Heath Common Midlands, where habitat creation techniques is Calluna vulgaris, although management to have been applied to former agricultural land increase the cover of Erica cinerea (as a butterfly since 2006. Management objectives have been nectar source) is being undertaken using plug to establish both heath and grassland adjacent plants and seeds. to surviving remnants of a semi-natural acid grass heath mosaic (Davis et al. 2011). Inver- tebrates could be expected to rapidly colonise Survey areas these newly created habitats from the adjacent semi-natural vegetation (Waloff 1973, Morris Ten areas were selected subjectively to rep- 1990, Littlewood et al. 2006, 2009). Analysis resent five principal vegetation types reflect- of the Auchenorrhyncha data is used to test the ing different management histories (Fig. 1). specific hypothesis that invertebrate assemblages The following descriptions of these areas are ANN. ZOOL. FENNICI Vol. 57 • Re-establishment of Auchenorrhyncha (Hemiptera) assemblages 3 based on the site management plan (Butterfly Conservation 2012), monitoring reports (Eco- logical Restoration Consultants 2009, 2016), and vegetation surveys conducted in 2007 and 2017 (Whild Associates 2007, McCullagh 2017) which assigned plant communities to the clos- est vegetation types within the framework of the National Vegetation Classification (NVC) (Rodwell 1991, 1992, 2006). The assignment of areas to NVC types in the paragraphs below should be treated as indicative rather than imply- ing precise matches with the NVC floristic tables (McCullagh 2017). Additional observations on the botanical dominants, the percentage cover of bare ground, dwarf shrub species, and their growth phases, within each sample area were made by the authors in 2018. Botanical nomen- clature follows Stace (2019). Heather growth phases follow Gimingham (1972). REMNANT HEATHLAND (RH): Two areas sup- ported mosaics of semi-natural acidic grassland (resembling NVC type U1 Festuca ovina–Agros­ tis capillaris–Rumex acetosella grassland) and dwarf shrub heathland (resembling NVC type H8 Calluna vulgaris–Festuca ovina heath) (Fig. 1). One of these, with an area of approxi- mately 0.5 ha, may represent original heathland Fig. 1. Prees Heath Common Nature Reserve with the that has survived since the 1880s (RH1). The location of sampling areas. Cross-hatched areas are other area was located on the line of the former heath created on former arable in 2007 (CH1, CH2); airfield runway, from which concrete was broken dark stippling is heath created on former pasture in up and removed in the 1970s, and along which 2010 (CH3); light stippling is mesotrophic grassland reverting from pasture since 2007 (RMG1); diagonal semi-natural vegetation subsequently re-estab- hatching indicates mesotrophic grasslands created on lished in the absence of agricultural cultivation former arable in 2007 (CMG1, CMG2); unshaded land (RH2). Characteristic species were E. cinerea, is variously acid grassland reverting from former arable C. vulgaris, Luzula campestris, Anthoxanthum fields since 1991 (RAG1, RAG2), remnants of semi- odoratum, Lotus corniculatus, Festuca ovina, natural grass heath (RH1, RH2) and small areas of scrub woodland. F. rubra, Carex pilulifera and Avenella
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