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Failing badger protection

Published online by Cambridge University Press:  01 March 2022

Daniel Wood
Affiliation:
ACD Environmental Ltd, Malmesbury, UK
Christina Buesching
Affiliation:
Department of Biology, The University of British Columbia, Kelowna, Canada
Chris Newman
Affiliation:
Wildlife Conservation Research Unit, Department of Zoology, University of Oxford, Oxford, [email protected]

Abstract

Type
Conservation News
Creative Commons
Creative Common License - CCCreative Common License - BY
This is an Open Access article, distributed under the terms of the Creative Commons Attribution licence CC BY 4.0.
Copyright
Copyright © The Author(s), 2022. Published by Cambridge University Press on behalf of Fauna & Flora International

Despite legal protection (Protection of Badgers Act 1992), 105,960 badgers were culled in the UK during 2018–2020 as part of bovine tuberculosis control measures, with licences currently issued to remove up to a further 75,930 badgers commencing 1 June 2021. Nevertheless, developments interfering with badger setts still require licence from Natural England, often necessitating that ecological consultancies mitigate any destructive effects. When a sett impedes intended development, ecological consultancies are contracted to assess the feasibility of replacement with an artificial substitute. There is, however, no legal requirement stipulating that such setts should be adopted, beyond proof the badgers have investigated their new accommodation. In response to our data request of 8 February 2021, Natural England was unable to confirm how many of 1,471 licences granted during 2019–2020 required the construction of artificial setts to replace those closed down or whether any replacement setts subsequently supported breeding.

Surveying ecological consultancies via the British Ecologists Facebook Group during 19 May–15 June 2021, we established that only 10 of 29 respondents were required by Natural England to conduct follow-up monitoring of the artificial setts they constructed; eight additional artificial setts were monitored of the consultant's own volition. Of these 18 setts, breeding was detected at only eight. The success rate is likely to be lower among consultants involved in artificial sett construction who did not respond to our survey. Many artificial setts fail either because the sett is not located within the territorial range of the disenfranchised badger group, as a result of a lack of territorial baitmarking surveying, or because the sett is not sited and constructed in the correct soil substrate to achieve the underground complexity and thermal stability badgers require, especially for breeding success (Tsunoda et al., 2018, Journal of Thermal Biology, 74, 226–233). With culling, traffic accidents and direct persecution already exerting a c. 20% additional mortality burden on the UK's c. 485,000 badgers (Judge et al., 2017, Scientific Reports, 7, 276), this is an underappreciated issue that needs urgent attention. Every effort should be made to ensure that investments in conservation mitigation are effective; simply demonstrating compliance with minimal criteria does not serve intended welfare or conservation goals.