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Earthworm community composition,seasonal population structure,and casting activity on Kentucky golf courses
Affiliation:1. Institute of Soil Biology, Biology Centre CAS, Na Sádkách 7, CZ-37005 České Budějovice, Czech Republic;2. Faculty of Science, University of South Bohemia, Branišovská 31, CZ-37005 České Budějovice, Czech Republic;3. Department of Soil and Water Conservation and Organic Waste Management, Centro de Edafología y Biología Aplicada del Segura, CSIC, P.O. Box 4195, E-30080 Murcia, Spain;1. School of Agriculture and Biology, Shanghai Jiao Tong University, Shanghai 200240, China;2. Landcare Research, PO Box 40, 7640, Lincoln, New Zealand;3. Shanghai Shengran Agricultural Science Technology Corporation Limited, Shanghai 201401, China;4. Institute of Agriculture & Environment, Massey University, Private Bag 11-222, Palmerston North, New Zealand;1. INRA, UR251 PESSAC, F-78026 Versailles cedex, France;2. INRA, UMR211 Agronomie INRA AgroParisTech, F-78850 Thiverval-Grignon, France;3. AgroParisTech, UMR211 Agronomie INRA AgroParisTech, F-78850 Thiverval-Grignon, France;1. UK Centre for Ecology & Hydrology, Maclean Building, Crowmarsh Gifford, Wallingford, Oxfordshire, OX10 8BB, UK;2. Cardiff School of Biosciences, BIOSI 1, University of Cardiff, P.O. Box 915, Cardiff, CF10 3TL, UK;3. UK Centre for Ecology & Hydrology, Lancaster Environment Centre, Library Av., Bailrigg, Lancaster, LA14AP, UK
Abstract:Earthworms can be troublesome pests on golf courses when their soil-rich casts become abundant enough to disrupt the maintenance, aesthetics, and playability of putting greens and fairways. Management of the problem is hindered by lack of knowledge of earthworm community structure on North American golf courses. We surveyed communities of endogeic earthworms inhabiting golf course fairways and putting greens in central Kentucky and tracked the seasonal population structure and casting activity of the predominant species. Seven earthworm species, six of them non-native, were identified in varying proportions from fairways of the different golf courses. Aporrectodea trapezoides (Dugès) dominated, although Allolobophora chlorotica (Savigny), Diplocardia singularis (Ude), and Amynthas sp. also were abundant on some courses. Soil characteristics (pH, percentages of sand, silt, clay, and organic matter) at fairway sample sites were not good predictors of overall earthworm density or proportionate abundance of particular species. Ap. trapezoides was found in the upper 21 cm of topsoil throughout the year except when frozen ground precluded sampling. The Ap. trapezoides population consisted mainly of adults and cocoons in late autumn and winter, and juveniles in summer. Casting by Ap. trapezoides, which also occurs on soil-based greens, was greatest in late autumn and early winter, with a secondary peak in early spring. Amynthas hupeiensis, an east Asian megascolecid earthworm, was the only species found damaging sand-based greens. Prolific casting by Am. hupeiensis continued during summer after other species’ casting activity on fairways had waned. Am. hupeiensis is established along river banks in Kentucky and neighboring states, and is used as fish bait. We hypothesize that it may be introduced onto golf courses as cocoons in river sand used for course renovations, or from bait discarded by anglers fishing in golf course ponds.
Keywords:Turfgrass
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