Background: The South Downs National Park (SDNP) is the UK's most visited National Park, and a foci of tick-borne Lyme disease. A range of human pathogens have been detected in UK ticks and related hosts, and the first presumed autochthonous cases of tick-borne encephalitis and babesiosis were recorded in 2019-20. SDNP's key objectives include conserving wildlife and encouraging enjoyment of the countryside, so interventions are needed that reduce hazard without negatively affecting ecosystem health. To be successful these require knowledge of site hazards, and we aimed to provide this to enable action.
Methods: British Deer Society volunteers submitted ticks removed from deer. Key potential intervention sites were selected and ticks collected by drag-sampling six 50 m2 transects per site, in most cases twice yearly for two years. Ticks were identified in-lab (sex, life stage, species), hazard measured as tick presence, Density of Ticks (all life stages, DOT), and Density of Nymphs (DON). Sites and habitat types were analysed for association with hazard. Distribution across SDNP was mapped in a Geographic Information System (GIS), by combining and comparing our fieldwork results with records from five other data sources (recent and historic).
Results: 87 Ixodes ricinus (all but one adults, 82%F) were removed from 14 deer (Dama dama n=10; Capreolus capreolus n=3; 1 not recorded; tick burden, 1-35) at 12 locations (commonly woodland). Five potential key intervention sites were identified and drag-sampled 2015-16, collecting 623 ticks (238 on-transects): 53.8% nymphs, 42.5% larvae, 3.7% adults (13M, 10F). Ticks were present on-transects at all sites drag-sampled (I.ricinus at three, Haemaphysalis punctata at two). The Mens (TM, the quietist site for human visitors) had the highest DOT at 30/300 m2 (DON=30/300 m2), followed by Queen Elizabeth Country Park (QECP, the busiest) at 22/300 m2 (12/300 m2), Cowdray Estate (CE) at 8/300 m2 (6/300 m2), and Seven Sisters Country Park (SSCP) at 1/300 m2 (1/300 m2). Ditchling Beacon Nature Reserve (DBNR) was sampled 2016 only (one adult H.punctata collected). Woodland had significantly higher hazard than grazed downland, but ticks were present at all downland sites drag-sampled. GIS mapping showed I.ricinus identified in 33/37 of SDNPs 10 km2 grid squares, Ixodes hexagonus 10/37, H.punctata 7/37, Dermacentor reticulatus 1/37.
Conclusions: Mapping shows tick hazard is broadly distributed across SDNP. Ixodes ricinus was most common, though the seeming range expansion of H.punctata is concerning, particularly as it seems to thrive better on grazed downland than I.ricinus. Site specific recommendations include: management of small high hazard plots with heavy visitor numbers (QECP); signage on post-visit precautions (all sites); repellent impregnated clothing for deerstalkers (CE); flock trials to control H.punctata (SSCP, DBNR). Further research at TM, which has high tick density, may contribute to knowledge on ecological dynamics underlying infection density, and the potential use of predator re-introduction/protection as a public health intervention. Ecological research on H.punctata would aid control. The SDNP Authority is ideally placed to link and champion site-based and regional policies to reduce hazard, whilst avoiding or reducing conflict between public health and ecosystem health.