Recreational angling as a pathway for invasive non-native species spread: awareness of biosecurity and the risk of long distance movement into Great Britain
Identifying and establishing the relative importance of different anthropogenic pathways of invasive non-native species (INNS) introduction is critical for effective management of their establishment and spread in the long-term. Angling has been identified as one of these pathways. An online survey of 680 British anglers was conducted to establish patterns of movement by British anglers abroad, and to establish their awareness and use of biosecurity practices. The survey revealed that 44% of British anglers travelled abroad for fishing, visiting 72 different countries. France was the most frequently visited country, accounting for one-third of all trips abroad. The estimated time taken to travel from Western Europe into Great Britain (GB) is within the time frame that INNS have been shown to survive on damp angling equipment. Without biosecurity, it is therefore highly likely that INNS could be unintentionally transported into GB on damp angling gear. Since the launch of the Check, Clean Dry biosecurity campaign in GB in 2011, the number of anglers cleaning their equipment after every trip has increased by 15%, and 80% of anglers now undertake some form of biosecurity. However, a significant proportion of the angling population is still not implementing sufficient, or the correct biosecurity measures to minimize the risk of INNS dispersal on damp angling equipment. With the increase in movement of anglers abroad for fishing, further work is required to establish the potential for INNS introduction through this pathway.
KeywordsAngling Biosecurity Awareness Invasive species Human pathways
Introduction of non-native species by human-mediated jump dispersal is well documented and encapsulates a variety of activity, from the unintentional harbouring of non-native species within shipping cargo (Suarez et al. 2001) to intentionally introducing species for economic purposes such as aquaculture in the case of the Signal crayfish (Pacifastacus leniusculus) (Holdich et al. 2004). Although many anthropogenic jump dispersal mechanisms or ‘pathways’ have been identified (Hulme 2009), the relative importance of each pathway is unknown. Related to this, is the increasing recognition that, for many invasive non-native species (INNS) the most cost-effective approach to minimising their environmental and socio-economic impacts is prevention of initial establishment in the first place (Leung et al. 2002; Finnoff et al. 2007; Caplat and Coutts 2011; Brundu 2015). Once an INNS is introduced, unless it is detected early and rapid eradication is undertaken, it often becomes highly expensive, and in some cases impossible to completely eradicate (Mack et al. 2000; Kolar and Lodge 2001; Wittenberg and Cock 2001; Simberloff et al. 2013). Recognising the long-term economic and environmental benefits of preventing further INNS invasions, prevention has been placed at the forefront of the EU Regulation of Invasive Alien Species (1143/2014) (Beninde et al. 2014). Following the introduction of this regulation it is now an obligation for EU Member States to investigate and prioritise potential pathways of human INNS introduction (Trouwborst 2015). An INNS pathway refers to a suite of processes or human activities, that result in the intentional or unintentional movement of an INNS from its natural range, either past or present, into a new environment (Genovesi and Shine 2004; Pyšek et al. 2011). Vectors are distinguished as the physical means or agent such as a ship, vehicle wheels or angling net, via which INNS are moved outside their native range. Through the creation of pathway action plans (PAPs), resources can be allocated to target the most significant pathways, or a particular aspect of a vector identified as the weakest link or greatest biosecurity threat. Managing pathways of human introduction represents a more effective approach than individual INNS management as it reduces the risks of all non-native species using that pathway. This is particularly important as the dispersal mechanisms of many non-native species remain uncertain, and due to time lags it is hard to predict which non-native species may, or may not become invasive in the future (Essl et al. 2015).
Recreational angling has been identified in the EU Regulation and the convention on biological diversity (CBD) as a potential human pathway of INNS introduction (Hulme 2009; Harrower et al. 2018). Used traditionally for the provision of food, angling has also evolved into a popular catch-and-release sport in Western countries, with a rod and line used to catch a variety of fish species (Von Brandt 1964; Pitcher and Hollingworth 2002). Grouped together with aquaculture and other leisure activities, angling has been reported to account for more than 40% of aquatic INNS invasions in Europe (DAISIE 2009). Angling is a highly popular activity, with an estimated 11.7% and 4.8–6.5% of the population in the United States and Europe participating in fishing every year (Hickley 2018). Around 9% of the population in England and Wales aged 12 years or older took part in angling in 2009–2010, equating to around 4.2 million people (Simpson and Mawle 2010; Sports England 2011). However, despite the link between angling and non-native species being reported for many years (Maitland 1987; Winfield et al. 1996; William and Moss 2001; Zięba et al. 2010) the relative importance of angling as a pathway and vector for non-native species dispersal is still relatively unknown. A few studies have been undertaken to investigate the role of angling in the secondary dispersal of INNS between water bodies (Gates et al. 2009; Anderson et al. 2014), and others have reported the potential for INNS introduction and spread from the use of live bait by anglers (Keller et al. 2007; Kilian et al. 2012; Drake and Mandrak 2014; Cerri et al. 2017). In North America, higher numbers of non-native species have also been found to coincide with areas of greater recreational fishing demand (Davis and Darling 2017). However, there have been limited, if any, studies undertaken to investigate the potential for long-distance jump dispersal of INNS between continents/countries on damp angling equipment. This is despite a recent increase in the number of tourists travelling abroad for recreational activities including angling (Hulme 2015).
Many INNS can survive for a few days (Stebbing et al. 2011; Bacela-Spychalska et al. 2013) and in some cases up to two weeks in damp angling equipment and clothing (Fielding 2011; Anderson et al. 2015). In 2011 around 64% of British anglers stated that they fished in more than one catchment per fortnight (Anderson et al. 2014). The high frequency of anglers returning from fishing within the time frame of INNS persistence in damp equipment suggests that angling gear could act as vector for the spread of INNS between waterbodies. Thus, mechanisms need to be implemented to ensure any invasive species present on equipment are removed or killed before re-use. Recognising this, the biosecurity campaign check, clean, dry (CCD) was launched in Great Britain by Defra in 2011. Biosecurity refers to the undertaking of a set of measures which individually, or collectively, contribute to a reduction in the risk of spreading INNS, including plants, animals and microbes (Dobson et al. 2013; Shannon et al. 2018). The aim of the CCD campaign is to provide simple biosecurity guidance to recreational water users in order to increase awareness of INNS and in turn to minimise their spread. There are further measures that complement the CCD including strategic planning to ensure sites without INNS are visited prior to sites with known INNS populations, and/or rotating different sets of equipment between sites (Dunn and Hatcher 2015). By preventing the spread of INNS in the first place, it may save substantial environmental and economic costs in the long-term due to damage to the environment, and expenses to remove INNS.
Public engagement and compliance will be essential for the success of this biosecurity campaign (Bremner and Park 2007; Garcia-Llorente et al. 2008; Gozlan et al. 2013). People are often the weakest leak in the control of INNS species (Cliff and Campbell 2012) and it can take time for individuals to adopt biosecurity measures as a new social norm (Rogers 2003; Prinbeck et al. 2011; Sutcliffe et al. 2018). Consequently, monitoring the uptake of biosecurity by recreational users is essential to assess the success of the campaign and to identify future priorities. However, except for a baseline study conducted during the first year of the CCD launch (Anderson et al. 2014), changes in the biosecurity behaviour of recreational water users including British anglers is unknown. This study explores changes in angling biosecurity behaviour since the launch of the CCD campaign, and assesses the risk of recreational angling activity unintentionally introducing, or spreading, non-native species into Great Britain (GB) from abroad on damp angling equipment (boots, nets). We focus on the dispersal of INNS species potentially transmitted in angling equipment such as macrophytes and macroinvertebrates. Although parasites and diseases such as the Salmon louse (Gyrodactylus salaris) are not explicitly investigated, there is also potential for dispersal of these in contaminated angling equipment (Peeler et al. 2004).
A structured online questionnaire survey was conducted between the 8th of July and 31st of October 2015. The survey was produced using the online software, SurveyMonkey. The use of the internet for data collection is accepted as an effective approach to data collection, providing access to a geographically dispersed population, and a sampling size not always achievable using an interview-based approach (Couper et al. 2007; Couper and Miller 2008). The questionnaire was publicised to anglers by Angling Trust social media (Facebook and Twitter) and also circulated via email to their members. The Angling Trust is an organisation that represents all game, coarse and sea anglers in England and Wales on environmental and angling issues. As a result, there is potential for a high response from anglers that have an interest in the natural environment as they are more likely to engage with Angling Trust ideas. To account for this, the questionnaire was also circulated to angling clubs, relevant angling magazines, and promoted at three GB angling events. This included two regional angling forums which brought together angling clubs in the southwest and southeast of England, and the Country Land and Business Association (CLA) game fair in northern England. The CLA is a membership organisation for owners of land, property and business in England and Wales, and the fair is well attended by members and the general public. The different events are attended by different angling club representatives and provided an opportunity to promote the questionnaire across a reasonable geographic coverage, whilst minimising bias in responses from particular regions. All of the events were attended in July 2015. Hard copies of the questionnaires were also made available to minimise potential for selection bias by excluding anglers that do not use the Internet. Despite attempts to reduce potential bias through promotion of the questionnaire at other angling events, it should be recognised that data derived from this survey are assumed to represent the maximum percentage of anglers currently conducting biosecurity in GB.
Questionnaire survey design
This study focused on quantifying the potential for recreational angling to facilitate jump dispersal of NNS from Europe to GB by investigating the frequency at which anglers travelled to different countries and undertook biosecurity after a fishing trip. Given this overall aim, a closed-format questionnaire was deemed the most appropriate approach. Questions that required more extensive individual responses such as names of fishing sites had a ‘free-text’ option included. Interviews and group discussions would have provided a greater insight into why individuals behave in particular ways and how this is influenced by different factors (Longhurst 2010). However, interviews and group discussions would not have reached the high volume of respondents required in this study. Using a web-based approach enabled access to greater numbers of anglers across a larger geographical area within GB (Schmidt 1997).
The questionnaire was organised into marked sections applying filter questions to avoid asking irrelevant questions to the respondents. For example, after asking an individual whether they went fishing abroad, if a respondent answered ‘no’ the questionnaire would automatically skip to the next relevant section. This ensured that the questionnaire was as easy to follow and fill in as possible, thus maximising the number of respondents that completed the questionnaire.
The questionnaire was phrased to allow comparison against the baseline angling awareness survey undertaken by Anderson et al. (2014) in 2011. The first section focused on frequency and patterns of movement of anglers within GB and abroad. Answers were generally quantitative, employing statements such as fishing once a week, every two weeks rather than more generic ‘often’, ‘sometimes’ statements thereby providing a more accurate representation of their activity (Angelsen and Lund 2011). The second section explored the use of different equipment such as nets, slings, waders, and the frequency with which equipment was cleaned and dried. The CCD campaign, as launched in 2011 has been used to promote awareness of INNS and simple biosecurity guidance that can be undertaken by the general public and practitioners in the field to reduce the risk of spreading INNS. It is focused on three main elements: ‘Check’—examining equipment, boats and clothing and removing any fragments of plants, mud or other material, ‘Clean’—thoroughly washing equipment and clothing in hot water or disinfectant, and ‘Dry’—leaving equipment and clothing to dry in the sunlight for at least two days. As these are the key messages promoted by the campaign, these were used to phrase questions around biosecurity procedures conducted by anglers. The final section of the questionnaire included questions on angler awareness of the CCD campaign and INNS. It is recognised that, by using the terminology ‘INNS’, the questionnaire overlooks non-native species, which after a lag phase, have the potential to become invasive at a later stage (Crooks et al. 1999). However, the focus on the study was to ascertain anglers awareness of INNS. Thus, although biosecurity measures undertaken by anglers are likely to minimise introduction of all non-native species being spread by this vector, to ensure clarity in the questionnaire only the term INNS was used. This section was placed at the end of the survey to minimise the risk of conditioning the respondents’ answers surrounding their cleaning and drying behaviour in the earlier section of the questionnaire. This survey complied with University College London (UCL) guidelines on ethical conduct. Respondents were asked for their age, gender and the first 3–4 digits of their postcode. This information would not enable any respondent to be identified. All data were collected and stored anonymously.
A pilot study was undertaken to pre-test the survey before publishing it online. This ensured that questions were interpreted correctly and that sufficient answer options were available for the closed questions (Gaddis 1998). Ten anglers were asked to undertake the online survey. Following the pilot, minor modifications were made to the final questionnaire to improve question clarity and to include additional tick box options in certain questions such as additional angling equipment. The final questionnaire is available in “Appendix”.
Differences in biosecurity behaviour between different types of freshwater anglers were analysed. Anglers that fished mainly for Common carp (Cyprinus carpus) were treated as a separate group from general coarse anglers who target other freshwater species such as Bream (Abramas spp.), Roach (Rutilus spp.) and Tench (Tinca spp.) Many anglers undertake sea fishing alongside freshwater fishing. However, due to differences in the environmental tolerances of freshwater and marine INNS, particularly in relation to salinity, anglers that only undertook sea fishing were removed from the analysis. This accounted for three respondents only. Subsequently, five different types of anglers were derived: game, competition, lure, coarse-other and coarse-carp. Match anglers are those that fish in competitions in contrast with the other groups that fish simply for pleasure. Demographic information obtained for the 2015 GB Environment Agency (EA) rod licence data was used to test the representativeness of the sample compared to the overall GB angling population.
Categorisation of anglers’ risk based on their cleaning and drying frequency
Cleaning and drying frequency
Individual cleans and dries after every angling trip
Undertake both every 2–5 trips
Angler may clean his/her equipment every trip but only dries it every 2–5 trips or vice versa
Every 6–10 trips for both cleaning and drying
Angler may only clean his/her equipment every 6–10 trips, but dries every 2–5 or vice versa
Does not undertake both parts of the biosecurity process (clean, dry).
Angler cleans his/her equipment after a trip but does not dry it
To assess temporal changes in the biosecurity activity of anglers, only anglers that fished at least once a fortnight were included to reflect the approach used in the 2011 baseline data collection. Consequently, for this part of the analysis only 79% (anglers that fished once a fortnight) of the 680 responses were used.
The first 3–4 digits of the respondent’s postcode were converted into longitude and latitude data using Doogal (http://www.doogal.co.uk/BatchGeocoding.php). These data were then superimposed onto a map of GB in ArcMap (version 10.3.1) to assess the geographic distribution of the sample angler population, and to identify any spatial patterns in the distribution of anglers of different risk in GB.
Kolmogorov–Smirnov tests were undertaken in SPSS 24 to determine the representativeness of the sample questionnaire in relation to the entire British freshwater angling population. Age and gender demographic data were compared against environment agency (EA) rod licence data for 2015 following similar comparisons conducted by Anderson et al. (2014) and White et al. (2005). Rod licence was used as any angler wishing to fish in freshwater bodies in GB requires a licence. Chi squared tests were employed to determine relationships between the risk of types of anglers, their risk categories and awareness of the CCD. As there were less than five anglers who stated that they mainly lure fish, these were removed from this aspect of the analysis to meet the assumption of the Chi squared test. Both tests had over 500 sets of observations indicating robust p-values (Jaeger 2008). Post-hoc Cramer tests were applied to the risk and biosecurity awareness Chi squared tests to assess the significance and size of the effect.
Frequency of fishing trips of British anglers within the UK (%), by fishing type. The group coarse carp refers to anglers that primarily fish for common carp Cyprinus carpio and is treated as a separate group from anglers that fish primarily for other fish species such as roach, tench, bream and rudd (Coarse excluding carp)
Frequency of fishing per angler type (%)
More than once a week
Once a week
Every 3 weeks
Once a month
Once every 2 months
Once every 3 months
Less than once every 3 months
Coarse (excluding common carp Cyprinus carpio)
Frequency of travel of British anglers to different countries for fishing as proportion of the total number (n = 680) of respondents and a percentage of anglers fishing abroad (total anglers travelling abroad n = 300) (%). Islands placed within brackets were grouped together to represent a single country
Total number of respondents
Percentage of total anglers
Percentage of anglers traveling abroad
Cyprus, Greece, Portugal, Sweden
Czech Republic, Hungary, Malta, Bosnia and Herzegovina
Finland, Luxembourg, Slovakia, Switzerland
North and South America
(Canary Islands, Tenerife, Lanzarote, Grand Union), (Trinidad and Tobago)
Argentina, Cyprus, Thailand
Antigua, (West Indies, Caribbean, British Virgin Islands, Barbados)
Guyana, Peru, Suriname, Venezuela, Jamaica
Egypt, Gambia, Mauritius,
Guyana, Morocco, Myanmar, Nepal, Oman, Peru, Uganda, Zambia
India, Myanmar, Nepal, Oman, Outer Mongolia, Philippines, Singapore,
Cars and vans were the primary mode of transport for some 43% of the anglers fishing abroad. Airplane travel represented the second most popular mode of transport for anglers fishing abroad, accounting for 34.7% of travel. For British anglers that fished exclusively in Western Europe (Scandinavia, the Netherlands, France, Spain, Ireland, Iceland and Portugal) some 64.7% used motor vehicles as their primary mode of transport. 18.4% and 16.2% of anglers also used airplanes and ferries to travel to these Western European countries. 69.4% of anglers fishing exclusively in France and The Netherlands travelled primarily by car or van.
Risk categorisation of anglers fishing at least once a week or once a fortnight (%)
Anglers fishing once a week
Anglers fishing once a fortnight
Anglers fishing less than once a fortnight
The biosecurity risk of anglers fishing at least once a fortnight was investigated and a similar percentage for the angler risk was identified. Over 40% of anglers fishing at least once a fortnight were low risk (Table 4). Twenty percent of anglers that fished at least once a fortnight were classified as major risk. 17% of anglers fishing once a fortnight never cleaned or dried their equipment after fishing.
Except for competition anglers, 40% of anglers represented by each angler type were categorised as low risk. The carp and game angler categories had the greatest proportion of low risk anglers at 55% and 52.2%, respectively. Carp anglers had the lowest percentage of high risk anglers, with 12.5% compared to over 20% for coarse, game and competition (match) anglers. However, these differences were not significant (n = 525, df = 3 p = 0.105).
Temporal changes in angler biosecurity behaviour
Angling as a pathway for the unintentional introduction of INNS from Europe
Responding to the obligation for GB to investigate potential human pathways and vectors of INNS introduction, this study represents the first known study assessing the potential for anglers to act as unintentional vectors for the spread of invasive species between countries in Europe. Over 40% of anglers used their equipment abroad for fishing. With 4 million estimated anglers in GB (EA 2004) this extrapolates to around 1.76 million GB anglers potentially travelling abroad with their angling equipment, often to two countries or more. This includes potentially 588,000 travelling to France for fishing, and 847,100 travelling to a country in Western Europe including The Netherlands and Norway. Horizon scanning studies indicate there are at least 16 freshwater invasive species present within Western Europe that are of medium or high-risk of entering GB (Roy et al. 2014; Gallardo et al. 2016), including at least 10 aquatic Ponto-Caspian INNS (Gallardo and Aldridge 2013a). In addition to invasive species, invasive parasites and pathogens such as the ecto-parasite Salmon louse (Gyrodactylus salaris) also represent a major biosecurity concern to British waters. Gyrodactylus salaris has had devastating impacts on salmon populations in invaded Norwegian rivers and if introduced to GB is likely to have similar negative impacts on GB salmon populations (Peeler et al. 2004). Given the bioclimatic similarities between Western Europe and GB (Gallardo and Aldridge 2013b), it is anticipated that any INNS establishing in these regimes have a high likelihood of being able to survive and spread within GB (Gallardo and Aldridge 2013b, 2015). Consequently, Western Europe represents a substantial source for new invasive species that could be introduced by recreational pathways such as angling.
In addition to the establishment of new INNS there is also the risk of introducing new genetic and phenotypic strands of INNS already established in GB. Some INNS are limited in their current distribution due to genetic or fitness bottlenecks, meaning they are not adequately suited to the environment they have invaded (Crooks et al. 1999). The introduction of new phenotypic variants from different source regions could release the INNS from these environmental restrictions and facilitate expansions in their distribution, thereby increasing impacts on invaded habitats (Lavergne and Molofsky 2007; Forsman 2014). In GB, some invasive species with limited distribution such as Floating water primrose (Ludwigia grandiflora) have been targeted for eradication. The introduction of new phenotypic strands or populations could therefore undermine efforts to control or eradicate these INNS.
Estimated duration in hours of ferry journeys between the UK and the Netherlands, Belgium France and Ireland.
(Source: Brittany Ferries and P&O Ferries http://www.poferries.com/en/portal Accessed 02/06/2016)
Ferry routes between Europe, Ireland and GB
Estimated duration (h)
Frequency of ferries (number per day)
Number of cars per ferry
Hull to Zeebrugge
Poole to Cherbourg
Portsmouth to Caen
Portsmouth to Cherbourg
Portsmouth to Le Havre
Portsmouth to St Malo
Plymouth to Roscoff
Cairnyan to Belfast
Cairnryan to Larne
Fishguard to Rosslare
Liverpool to Belfast
Liverpool to Dublin
Awareness and implementation of biosecurity
It should be recognised that self-report style questionnaires are vulnerable to social desirability response bias, with participants potentially stating answers that they believe to be socially acceptable, or desirable by the researcher (Randall and Fernandes 1991; Lajunen and Summala 2003). This cannot be factored out of any questionnaire (Brace 2008). As a result, it is possible that some respondents may overestimate how often they clean and dry their equipment in order to satisfy the surveyor (Cliff and Campbell 2012). Therefore, although the demographic analysis indicated this study was representative of British angler population holding a rod licence in 2015, the findings of this questionnaire should be interpreted with caution. Furthermore, the opt-in nature of this questionnaire means there is potential for a greater response from individuals that are aware and care about conservation issues, or who represent more affluent members of the angling community due to the recruitment of responses via the Internet and at the game fair event (White et al. 2005). These individuals are therefore more likely to have excess income to spend on fishing trips abroad. The percentages presented here should therefore be seen as representing a maximum estimate for anglers fishing abroad and undertaking biosecurity. Taking these factors into account, despite the potential respondent errors, the marked increase in biosecurity implementation since 2011 can undoubtedly be attributed to greater uptake of biosecurity. Therefore, there is evidence that anglers are becoming more aware of the risk of invasive species, resulting in the implementation of measures aimed at reducing the risk of dispersing species between water bodies.
Despite the substantial increase in the number of anglers undertaking biosecurity in our study, only 48% of anglers claimed to be aware of the Check Clean Dry campaign. This compares to New Zealand where 80% of recreational users are aware of an equivalent initiative (Anderson 2015). Initiated in 2004, the New Zealand campaign represents a long-established initiative, promoted through a national campaign, and implemented through regional biosecurity plans. Greater levels of awareness may therefore be partially due to the longer exposure of water users to the campaign. However, differing levels in awareness of the campaign, may also be partially attributed to the communication channels through which individuals are hearing about the campaign. Whilst 54% of water users in the regional area of Bay of Plenty, New Zealand had heard of the campaign through signage at boat ramps (Anderson 2015), the majority of British anglers were made aware of the CCD through angling magazines or environmental organisations. Consequently, although British anglers were being informed of the importance of biosecurity, this may not be explicitly tied to the Check, Clean Dry campaign, with this reflected by a weak, but significant association recorded between anglers’ awareness of the campaign and their likelihood of frequently undertaking biosecurity. Therefore, it is suggested that practitioners should exercise caution in using awareness of the Check Clean Dry campaign as the sole predictor of biosecurity uptake by the public in GB. Instead, a combination of factors, including measures of action after leaving the water should be used to monitor uptake of biosecurity procedures.
There has been a marked increase in the total proportion of anglers undertaking some form of biosecurity, in terms of either cleaning or drying their equipment occasionally after a fishing trip. However, over the same time period there has also been a 7% increase in the number of anglers who are not undertaking any biosecurity. INNS are highly adaptable species, capable of regenerating and spreading from a single plant node, asexual invertebrate or egg-bearing macroinvertebrate (Havel and Shurin 2004; Hussner 2009; Okada et al. 2009; Pigneur et al. 2011; Bruckerhoff et al. 2015; Riccardi 2015). Consequently, the unintentional introduction of a single viable plant fragment or live INNS specimen is all that is required to enable a new INNS population to establish. Further work is therefore required to engage with anglers that are still not conducting adequate biosecurity measures. This includes identifying the factors that are currently preventing anglers from undertaking biosecurity. Anglers stated that the availability of a cleaning station and the visual cleanliness of the equipment were some of the main reasons affecting whether an angler cleaned their equipment after use, with the financial cost of undertaking biosecurity and the availability of information being less important. These factors have also been reported as some of the main reasons inhibiting biosecurity for canoeists and boaters (Anderson et al. 2014; De Ventura et al. 2017). Going forward, the importance of routinely cleaning equipment needs to be reiterated, and more resources need to be assigned to ensure easy access to cleaning facilities at the angling waters. In addition to promotion of the CCD campaign, greater clarification is still required on the appropriate methods for cleaning equipment. The use of hot water is increasingly considered to be one of the most efficient, environmentally friendly and cost-effective methods for cleaning equipment and clothing (Beyer et al. 2010; Perepelizin and Boltovskoy 2011; Stebbing et al. 2011; Anderson et al. 2015; Sebire et al. 2018). Disinfectants such as Virkon® Aquatic and Virasure® have also been proposed as effective approaches to decontaminate equipment and small watercraft (Coughlan et al. 2018; Cuthbert et al. 2018). However, although the percentage of anglers cleaning their equipment has risen since the launch of the CCD guidance, 50% of anglers are using cold water. For ‘low’ risk anglers cleaning their equipment after every trip, cold water cleaning accounted for the only cleaning method for 31% of the category. These findings indicate that although anglers are undertaking cleaning approaches, their ‘cleaning’ method may not be effective in killing any attached INNS. It is therefore essential that promoters of the CCD campaign provide clearer messaging regarding effective cleaning.
Following the launch of the EU Regulation (1143/2014) in 2015, EU Member States are obliged to investigate potential anthropogenic pathways of INNS introduction and create pathway action plans (PAPs) for INNS pathways identified as being a risk (Caffrey et al. 2014; Beninde et al. 2014). This study represents the first attempt at quantifying the importance of angling as an international pathway, providing estimates of the volume of British anglers travelling to Europe for recreational fishing as well as valuable insights into changes in anglers’ behaviour since the launch of the invasive species-specific CCD campaign. Although this study has focused on angling within GB, it needs to be recognised that the angling pathway is potentially a global one. With limited biogeographic boundaries between many countries in continental Europe (Rahel and Olden 2008), the potential two-way cross-border movement of INNS by anglers could be significant for many countries. As a result, British anglers travelling abroad could also unintentionally introduce new populations of INNS into water bodies in the destination country. The findings of this study are therefore highly relevant to any country that receives a high volume of British anglers including Ireland and France. This is clearly exemplified by the recent outbreak of Crayfish plague (Aphanomyces astaci) in the Republic of Ireland. Considered a last refuge for many native European freshwater species, Ireland is an Ark site for White clawed crayfish (Austropotamobius pallipes). Until recently there were no reported occurrences of the invasive Signal crayfish (P. leniusculus) or the crayfish plague that P. leniusculus carries. However, in 2017, the presence of the plague was confirmed in the River Suir, County Tipperary, Republic of Ireland, and at time of writing had spread into four different catchments. No signal crayfish have been found so the source of the plague is unknown. There have been some suggestions that it may have been introduced on damp equipment (kayaks, nets, pleasure boats, waders). However, as there are many different users of these catchments, the original source of the introduction cannot be verified. Further research into the ability of pathogens to survive on equipment, and investigations into the presence of invasive species in private fisheries, sailing clubs or other water bodies will help to disentangle the potential sources of different groups of species or pathogens by each pathway.
Since the launch of the CCD campaign in 2011, the percentage of anglers undertaking biosecurity after every trip has almost doubled. Although changes to other recreational water users are unknown, this suggests that the campaign has been successful in increasing awareness of invasive species and encouraging the public to undertake biosecurity measures. The observed success of the CCD campaign as reported in this study, can be used to inform the angling PAP promoting the use of biosecurity as an invasive management tool. These plans are pathway-specific and outline the main policy and management approaches available for the various stakeholders involved. In addition to this, the findings of this study are also applicable to other freshwater pathways where biosecurity is being used as a management technique. This includes the use of recreational boat and kayak activity. Exchanges of best practice between different countries and recreational users could therefore be highly effective in reducing the risk of spread of invasive species.
Further work is required to determine what, if any, invasive species are present in European fishing lakes, and to assess the ability of INNS to survive car trips from Europe back to GB. The findings of this work indicate that angling could be an important pathway for the movement of aquatic INNS, particularly from Western Europe into GB.
The research was supported by a studentship from the UK Natural Environment Research Council (Grant No. NE/L002485/1) as part of the London NERC Doctoral Training Partnership, and a CASE partnership with the Angling Trust. The author would like to thank the Angling Trust for their advice and support in the development of the survey.
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