Received: 18 December 2017 | Revised: 4 May 2018 | Accepted: 27 June 2018 DOI: 10.1002/ece3.4385

ORIGINAL RESEARCH

Gastropods alien to South Africa cause severe environmental harm in their global alien ranges across habitats

David Kesner1 | Sabrina Kumschick1,2

1Department of Botany & Zoology, Centre for Invasion Biology, Stellenbosch University, Abstract Matieland, South Africa Alien gastropods have caused extensive harm to biodiversity and socioeconomic sys- 2 Invasive Species Programme, South African tems like agriculture and horticulture worldwide. For conservation and management National Biodiversity Institute, Kirstenbosch National Botanical Gardens, Claremont, purposes, information on impacts needs to be easily interpretable and comparable, South Africa and the factors that determine impacts understood. This study aimed to assess gas-

Correspondence tropods alien to South Africa to compare impact severity between species and under- Sabrina Kumschick, Centre for Invasion stand how they vary between habitats and mechanisms. Furthermore, we explore the Biology, Department of Botany & Zoology, Stellenbosch University, Matieland, relationship between environmental and socioeconomic impacts, and both impact South Africa. measures with life-­history traits. We used the Environmental Impact Classification for Email: [email protected] Alien Taxa (EICAT) and Socio-­Economic Impact Classification for Alien Taxa (SEICAT) Funding information to assess impacts of 34 gastropods alien to South Africa including evidence of impact South African National Department of Environmental Affairs; National Research from their entire alien range. We tested for correlations between environmental and Foundation; DST-NRF Centre of Excellence socioeconomic impacts per species, and with fecundity and native latitude range for Invasion Biology; South African National Biodiversity Institute using Kendall’s tau tests. Kruskal–Wallis tests were used to compare impact magni- tude among mechanisms and habitats, respectively. This study presents the first ap- plication of EICAT and SEICAT for invertebrates. There was no correlation between environmental impacts and socioeconomic impacts. Habitats did not differ regarding the severity of impacts recorded, but impacts via disease transmission were lower than other mechanisms. Neither fecundity nor native range latitude was correlated with impact magnitude. Despite gastropods being agricultural and horticultural pests globally, resilience of socioeconomic systems makes high impacts uncommon. Environmental systems may be vulnerable to gastropod impacts across habitats, hav- ing experienced multiple local extinctions of wetland island snail fauna. South Africa stands out as the only continental country that follows this trend. The knowledge gained on severity and nature of gastropod impacts is useful in risk assessment, which can aid conservation management. To make impact assessments more realistic, we suggest alternative ways of reporting impacts classified under EICAT and SEICAT.

KEYWORDS environmental impact, environmental impact classification for alien taxa, Gastropoda, impact assessment, resilience, risk analysis, socioeconomic impact, socio-economic impact classification for alien taxa

This is an open access article under the terms of the Creative Commons Attribution License, which permits use, distribution and reproduction in any medium, provided the original work is properly cited. © 2018 The Authors. Ecology and Evolution published by John Wiley & Sons Ltd.

 www.ecolevol.org | 8273 Ecology and Evolution. 2018;8:8273–8285. 8274 | KESNER and KUMSCHICK

1 | INTRODUCTION impact magnitudes across habitats and impact mechanisms. This has been done for various taxa, with some mechanisms showing to Alien species introductions continue to be a major driver of global be more important than others. For example, alien birds, amphib- change (Banks, Paini, Bayliss, & Hodda, 2015; Hulme, 2015). Alien ians, and fish cause more severe impacts via predation compared impacts on native systems are diverse in magnitude and nature, with other mechanisms (Evans et al., 2016; Kumschick et al., 2015; causing alterations to environments and socioeconomic networks Measey et al., 2016). An investigation of impact severity by habitat (Jeschke et al., 2014). The complexity of alien impacts makes them type is yet to be undertaken. difficult to understand, let alone manage (Keller & Kumschick, 2017; To increase not only our basic understanding of patterns re- Ricciardi, Hoopes, Marchetti, & Lockwood, 2013; Simberloff et al., lated to how impact magnitude differs between taxa and regions, 2013). Recent targets aimed at controlling harmful aliens and pre- it has been suggested that life-­history traits could aid moving to- venting their spread and impacts have been imposed globally, such ward a more predictive understanding of impacts, notwithstand- as the Aichi Target 9 that aims to control or eradicate priority spe- ing novel introductions (Kumschick et al., 2014). Such analyses cies by 2020 (CBD, 2013). Such targets will be challenging to achieve have been undertaken for a wide array of taxa (Evans et al., 2016; without a better understanding of alien impact across taxa and Kumschick et al., 2013; Nentwig, Kühnel, & Bacher, 2010; Novoa, habitats. Kumschick, Richardson, Rouget, & Wilson, 2016). According to the Gastropods are a taxonomic class that represents significant impact equation given by Parker et al. (1999), abundance is pro- problem as aliens, causing a multitude of environmental and so- portional to severity of impact of invaders, under the rationale cioeconomic impacts in many habitats. In Hawai’i, they have been that any biomass controlled by an invader represents resources implicated as a major threat to native plants (Joe & Daehler, 2008) no longer available to natives. Therefore, the ability of an alien and snails (Curry et al., 2016; Meyer & Cowie, 2010), and have been to reproduce rapidly and attain higher abundances should cor- suggested to harm native species in aquatic habitats (Darwall, Smith, relate with their impacts. This has been supported by significant Tweddle, & Skelton, 2009; Miranda & Perissinotto, 2012). Further, correlations between impact and fecundity for some taxa, namely many gastropods have been the cause of significant problems in ag- mammals and mollusks (Keller, Drake, & Lodge, 2007; Nentwig riculture (Barker, 2002; Coupland & Baker, 1995; Nash & Hoffmann, et al., 2010). High fecundity has been cited as a characteristic of 2012), resulting in economic losses by reducing yield and leading to many harmful gastropods (Charwat et al., 1995; Nash & Hoffmann, rejection of exports (Charwat, Davies, & Fraser, 1995; Cowie, Hayes, 2012; Rumi, Sánchez, & Ferrando, 2010), and mollusks with higher Tran, & Meyer, 2008; Moran, Gotlib, & Yaakov, 2004). Moreover, fecundity have been shown to have higher probabilities of causing they have been implicated as playing a role in the transmission of environmental and economic damage in the US great lakes (Keller diseases to humans (Senanayake, Pryor, Walker, & Konecny, 2003). et al., 2007). Given the complex nature of alien impacts, the need for universal Ecological flexibility is also expected to play an important role metrics to quantify impacts on environmental and socioeconomic with regard to impact because species that can live under diverse systems is evident. These have been provided by various impact environmental circumstances may sustain higher population den- scoring schemes, including the Environmental Impact Classification sities and occupy larger areas (Nentwig et al., 2010). The size of a for Alien Taxa (EICAT; Blackburn et al., 2014; Hawkins et al., 2015) native range should be proportional to the diversity of habitats in and more recently the Socio-­Economic Impact Classification for which a species can persist and therefore increase the likely sim- Alien Taxa (SEICAT; Bacher et al., 2017). These schemes provide ilarity between native and alien ranges (Kumschick et al., 2013). standardized methods to compare impacts across taxa and habi- Moreover, the likelihood of a species being transported, dis- tats (Evans, Kumschick, & Blackburn, 2016). A convenient property persed, and causing impact in novel ranges is higher if a species is of these schemes is that their impact classification frameworks are more widely distributed (Moodley, Geerts, Richardson, & Wilson, similar to the IUCN Red List (Kumschick et al., 2017), and EICAT 2013; Novoa et al., 2016). The latitude range of a species’ native has recently been adopted by the IUCN as a framework for impact range has been used as a measure of ecological flexibility and has scoring of alien taxa (https://portals.iucn.org/congress/motion/014). shown to correlate with impact for birds and mammals (Kumschick This allows for alien impact metrics to be seamlessly integrated into et al., 2013) as well as cactaceae (Novoa et al., 2016), suggesting existing management and policy procedures (Bacher et al., 2017). that this may be an important trait that correlates with alien im- Environmental and socioeconomic impacts have been shown to be pact magnitude. similar in severity for a wide array of taxa (mammals: Kumschick, Given the wide variety of alien gastropod impacts globally, it is Bacher, & Blackburn, 2013; arthropods, plants, and fish: Kumschick of relevance to assess these within impact classification schemes, et al., 2015), but there are exceptions (amphibians: Bacher et al., as well as identify potential patterns with respect to the severity 2017; birds: Kumschick et al., 2013). of their impacts. This can aid the prioritization of management in Impacts are highly context-­dependent, and they can differ be- countries and regions where information on impact is limited, as in tween recipient habitats and over time (e.g., Kumschick et al., 2014). South Africa. More generally, this knowledge may be integrated into Impact scoring schemes can aid in understanding generalizability risk analysis tools, ultimately aiding in the identification of effective and context dependency of impacts, for example, by comparing management actions (Keller & Kumschick, 2017). Here, we present KESNER and KUMSCHICK | 8275 the first global assessment of environmental and socioeconomic im- Minor (MN), Moderate (MO), Major (MR), Massive (MV) (Hawkins pacts of alien gastropods, by applying the EICAT and SEICAT scor- et al., 2015; for descriptions of each category, see Table 1). The re- ing schemes to the gastropods alien to South Africa. Because South maining three categories, Data Deficient (DD), No Alien Population Africa has experienced introductions of globally problematic alien (NA) and Not Evaluated (NE), do not reflect the impact status of an gastropods across aquatic and terrestrial habitats (Barker, 2002; alien, but describe cases where there is a lack of adequate informa- Griffiths & Picker, 2011; Herbert, 2010; Kappes, Delgado, Alonso, tion on impact or no need to quantify it. An alien may receive multi- & Ibáñez, 2009; Perera & Valderrama, 2010), it provides a repre- ple EICAT scores, depending on the amount and depth of literature sentative case study upon which to base a global analysis of alien found on its impact. Each EICAT score is assigned a mechanism, de- gastropod impact. We test whether environmental impact severi- scribing the nature of impact. EICAT has twelve such mechanisms, ties of alien gastropods are correlated with their socioeconomic im- these being competition, predation, hybridization, transmission of pacts, and whether there are differences in impact severity among diseases to native species, parasitism, poisoning/toxicity, biofouling, habitats and impact mechanisms, respectively. Further, we assess grazing/herbivory/browsing, chemical, physical or structural impact whether fecundity and native range size are correlated with gastro- on ecosystem, and interaction with other alien species (Hawkins pod impacts. Lastly, we are interested in whether there is a potential et al., 2015). publication bias toward more studies being performed on species SEICAT is similar to EICAT, having an identical impact classifi- achieving higher maximum impact scores, which could influence the cation framework. However, instead of using the scale of biologi- overall species classifications as suggested in the guidelines for using cal organization impacted as a means of quantifying environmental the two schemes. impact, it uses the scale of human activity impacted as a common metric to evaluate impact on human well-­being (Bacher et al., 2017). For example, a Minor impact (MN) is described as individual people 2 | METHODS experiencing difficulties in taking part in an activity, which can be detected through income loss or health problems. A Massive impact A list of 34 gastropods alien to South Africa was compiled from (MV) is the local disappearance of an activity from the area that an Griffiths and Picker (2011) and Herbert (2010) (Table 1). The na- alien invades (termed a “regime shift”). As with EICAT, SEICAT classi- tive range of each species was identified in accordance with pub- fies each alien by its maximum potential impact. Analogous to EICAT lished literature, including the following sources: Terrestrial Mollusc mechanisms, SEICAT has four main categories termed “constituents Tool (http://idtools.org/id/mollusc/index.php); Invasive Species of human well-­being”: health; safety; material and immaterial goods Compendium (https://www.cabi.org/isc/); Encyclopaedia of Life for good life; and social, spiritual, and cultural relations (Bacher et al., (http://eol.org/); and the Carnegie Museum of Natural History web- 2017). site (http://www.carnegiemnh.org/science/mollusks/index.html; for Scoring under both schemes is based on the best available evi- the list of native ranges as well as the literature used, see Supporting dence, and scores can change if more information on an alien taxon Information Table S1 and Appendix S1). becomes available (Blackburn et al., 2014). EICAT and SEICAT make A literature search including publications up to August 2017 was use of an identical confidence rating system giving an indication of conducted for each species, using Google Scholar and Scopus, with the probability of the assessment being correct and assigning each the scientific binomial species name as the search term. A filter was score a confidence level of low, medium or high based on the reliabil- applied to Scopus, which included the following fields: “Agricultural ity of the source, scale of the study and other factors (Bacher et al., and Biological Sciences,” “Medicine, Immunology and Microbiology,” 2017; Hawkins et al., 2015). “Environmental Science,” “Veterinary, Pharmacology, Toxicology and We assigned environmental and socioeconomic impacts iden- Pharmaceutics” and “Multidisciplinary.” Titles and abstracts were tified from the literature to the EICAT and SEICAT classification screened regarding their relevance for gastropod impacts, and the schemes respectively (lists of the literature sources used are given search considered complete when the literature begun to repeat it- in Supporting Information Appendix S2 and S3). Each impact re- self, no further information on impact was found (usually within the cord was assigned a habitat based on where the impact occurred as first 100 search results), or the search engine ran out of results. per the Hawkins et al. (2015) EICAT habitat classification scheme. Impacts identified under synonymous species names were included. Studies from the global alien range were included, but studies de- 2.1 | Impact classification schemes scribing impacts in the native range of a species were not scored EICAT has eight categories into which an alien can be assigned under EICAT, except for cryptogenic species. Regardless of a species’ (Hawkins et al., 2015). Each category is defined by verbal descrip- alien/native status, all socioeconomic impacts identified were scored tions that make EICAT robust toward assessor bias, and universally under SEICAT. This is because artificial habitats are becoming in- applicable across taxa. Five categories describe successive impact creasingly homogenized globally (McKinney, 2006), making impacts scenarios involving increasing scales of native biological organization in the native artificial systems adequate surrogates for potential affected and hence increasing impact magnitude. These categories socioeconomic impacts in invaded ranges. This was confirmed by a (in order of increasing impact) are as follows: Minimal Concern (MC), nonpaired Wilcoxon test showing no difference between all records 8276 | KESNER and KUMSCHICK (Continues) 2 9 5 9 1 1 5 35 SEICAT no. publications 18 24 12 11 10 12 High SEICAT confi - dence Low High Low Medium High High High Medium Low High Low Low Medium ­ being good life; Social, spiritual and cultural relations good life good life; Social, spiritual and cultural relations good life; Social, spiritual and cultural relations good life; Social, spiritual and cultural relations Health; Material and immaterial goods for Constituent(s) of human well- Material and immaterial goods for good life Health; Material and immaterial goods for Material and immaterial goods for good life Material and immaterial goods for good life Health; Material and immaterial goods for Health; Material and immaterial goods for Material and immaterial goods for good life Health; Material and immaterial goods for Material and immaterial goods for good life Material and immaterial goods for good life Health Material and immaterial goods for good life Health MN SEICAT maximum impact DD MN MN DD MO MO MN MN MN MN MN DD MN MN MN DD MN 9 EICAT no. publications 6 36 3 12 7 5 8 3 5 7 6 3 3 9 3 4 1 Low EICAT confi - dence Low Low Low Low Low Low Low Low Low Low Low Low Low Low Low Low Low

Predation

Transmission of diseases to native species; species species Predation Competition Competition Competition Mechanism(s) Predation Competition Transmission of diseases to native Grazing/herbivory/browsing; Competition Competition Grazing/herbivory/browsing Grazing/herbivory/browsing Transmission of diseases to native Grazing/herbivory/browsing Grazing/herbivory/browsing Grazing/herbivory/browsing; Grazing/herbivory/browsing; Grazing/herbivory/browsing; Predation Predation Competition Grazing/herbivory/browsing; EICAT maximum impact MR MN MN MR MR MR MN MO MN MO MO MO MO MO MO MO MN MN panormitanum Species draparnaudi Oxychilus similaris Bradybaena reticulatum Deroceras Tarebia granifera Helisoma duryiHelisoma Theba pisana Cochlicella barbara Cochlicella Deroceras laeve aspersum Cornu Deroceras Lehmannia nyctelia flavus Limacus Limax maximus Limax gagates Milax alliarius Oxychilus Oxychilus cellarius Oxychilus marmorata Aplexa Arion intermedius Arion ResultsTABLE 1 of the EICAT and SEICAT assessments for gastropods in order of decreasing EICAT maximum impact KESNER and KUMSCHICK | 8277

- the activ all

species; impacts, an to

of

one Information 7 7 9 3 1 2 related SEICAT no. publications 11 15 least at of Supporting MC—discernible disappearance in

sizes Medium SEICAT confi - dence Medium High High Low Low Low Low publications of follows: as available is population number in MV—irreversible

and scores ­ being described are scores activity; assign

to an

MO—declines of SEICAT

used for Confidence reduced; is Impacts literature disappearance

the reported. good life good life; Social, spiritual and cultural relations good life Material and immaterial goods for good life Constituent(s) of human well- Health; Material and immaterial goods for Health; Material and immaterial goods for Material and immaterial goods for good life Material and immaterial goods for good life Health; Material and immaterial goods for Social, spiritual and cultural relations Material and immaterial goods for good life on individuals deficient. of impact MR—local

sizes;

information DD—data maximum DD DD DD DD MO DD DD SEICAT maximum impact MN MN MN DD MN MN MC DD MC MN—fitness the activity

to Detailed to

extinctions; refer or individuals; impact. to EICAT no. publications 3 2 1 2 3 2 1 3 ­ being MO—change

well- maximum composition deleterious EICAT confi - dence Medium Low Low Low Low Low Low Low reduced; with

human not is

of but community people to

impacts, changes individual

of

mechanism/constituent ­ being the Predation Competition

mechanisms/constituents MC—discernible only and MV—irreversible species; species species; species species species not Mechanism(s) Transmission of diseases to native Transmission of diseases to native Predation Competition Transmission of diseases to native Transmission of diseases to native Transmission of diseases to native Transmission of diseases to native MN—well-

follows: as species; impacts persons; one

classifications DD DD DD EICAT maximum impact DD MN MC DD DD DD MN MN DD MN MN MN MC described least species’ at are a Impact individual of

on to

EICAT deficient. for available extinctions deleterious

Impacts . not DD—data

Lauria cylindracea Lauria Thais blanfordi Thais Discus rotundatus Species valentiana Lehmannia arboreus Zonitoides vermiculata Eobania lubricella cf. Cochlicopa lubrica cf. Cochlicopa Gyraulus chinensis Littorina saxatilis Littorina columella Lymnaea Arion hortensis Arion Physa acuta Physa Radix rubiginosa Radix Vallonia costata pulchella Vallonia 1 (Continued) TABLE Appendix and S1 S2. Note information ity; MR—local but 8278 | KESNER and KUMSCHICK found for socioeconomic impact scores in the native (N = 117) and Kendall’s tau correlation tests were conducted to assess the rela- alien range (N = 59; W = 3402, p = 0.82). Only primary references, tionships between fecundity and environmental and socioeconomic except for one case where the direct quotation was provided and the impacts respectively. The same correlations with impacts were under- primary reference was inaccessible, were included. taken with native range latitude. We again used both, maximum and For species that were assigned impact scores, further literature median impact scores (see above). Due to fecundity values spanning and database searches were conducted for data on their fecundity. two orders of magnitude, they were log transformed for analysis. This was done using the same databases that were used for native Kendall’s tau correlation tests were further used to assess the relation- range information. When searching the literature, the scientific bi- ship between EICAT and SEICAT maximum scores and the number of nomial species name followed by “fecundity” was used as the search publications found per species, respectively, to test if species which term. We further consulted gastropod experts for additional liter- are better-­studied record higher impacts (cf. Kumschick et al., 2017). ature on fecundity (for fecundity data and the literature used, see All analyses were performed in R (version 3.2.1; R Core Team 2015). Supporting Information Table S1 and Appendix S1). According to Carlton (1999), a wide variety of mollusk species have had their native geographic ranges reshaped by human activ- 3 | RESULTS ity, making their exact native ranges difficult to identify. This was reflected in the fact that many of the native ranges identified for a A total of 26 species were assigned EICAT scores and 22 species species were not identical between different sources. This was not were assigned SEICAT scores, with the remaining species being DD problematic when applying EICAT scores because there was no case (Table 1). The highest impacting species under EICAT were Oxychilus where impacts were recorded in areas that may be deemed dubi- draparnaudi (predation), Helisoma duryi, Tarebia granifera, and Theba ously native. However, to obtain native range latitude data, it was pisana (all competition), all recording MR impacts. For SEICAT, the necessary to explicitly identify the native range of each species. highest impact was MO, recorded by Theba pisana, Cochlicella bar- Hence the most inclusive native range identified was taken as the bara, and Eobania vermiculata all affecting material and immaterial “true” native range, with the intention of maximizing overlap with its goods for good life. Of the evaluated species, 20 were assigned veritable indigenous distribution. The explicit geographic borders of scores under both schemes. Environmental and socioeconomic im- these ranges were identified in accordance with various information pacts were not correlated for neither maximum (Kendall’s tau = 0.35; sources (provided in Supporting Information Appendix S1). To ob- P = 0.093) nor median (Kendall’s tau = 0.06; p = 0.765) scores. tain native range latitude data, the Global Biodiversity Information Environmental impact magnitude did not differ among habitats Facility (GBIF) database (https://www.gbif.org/) was used. This was (Kruskal–Wallis; χ2 = 2.39; df = 3; p = 0.49). The most common habi- done by calculating the difference between the highest and lowest tat in which gastropod impacts were recorded was wetlands, with 38 decimal latitude occurrences in the native range for each species. records, as well as having the highest number of upper tier impacts (MO or higher; Figure 1a). Environmental impacts were significantly different among mechanisms (Kruskal–Wallis; χ2 = 53.30; df = 3; 2.2 | Analyses p < 0.001). The post hoc test showed that impacts under the “trans- For the analyses, all DD entries were removed from the dataset mission of diseases” mechanism were significantly lower than those and the five impact levels for both schemes converted into numeric recorded under any other mechanism tested, and there was a trend variables, with numbers 1 to 5 corresponding to the five impact cat- toward competition impacts being larger than the other mechanisms egories (e.g., 1 for MC and 5 for MV respectively; as per Kumschick (Figure 1b). Competition was found to be the most common mecha- et al., 2017). To assess whether environmental and socioeconomic nism by which gastropods cause impact, as well as having the highest impacts were correlated, Kendall’s tau correlation test was con- number of upper tier impacts, more than double that of the second ducted to allow for comparison of ordinal responses. We separately highest mechanism (Figure 1b). analyzed maximum impacts across all records to account for the The most commonly impacted habitat regarding socioeconomic “worst case scenario” and median impacts to account for the range impact was “Artificial – Terrestrial” with 140 observations, repre- in impacts recorded. senting 94.6% of socioeconomic impacts for which habitats were To compare impact magnitude among mechanisms and habitat identified. This was the only habitat with upper tier socioeconomic types respectively, Kruskal–Wallis rank sum tests were performed impacts. In comparison with environmental impacts, all habitats re- using all impacts recorded in the study for the former, and all re- corded upper tier impacts, with the most severe environmental im- cords for which habitats were identified for the latter. We excluded pact in the “Artificial – Terrestrial” habitat being MR. mechanisms and habitats with less than seven impact records. Data on fecundity and native range latitude were available for Additionally, we performed pairwise comparisons between mecha- 11 species and 25 species respectively. Fecundity did not correlate nisms post hoc using a Dunn’s test, with p-­values adjusted using the with maximum environmental (Kendall’s tau = −0.38; p = 0.152) or Benjamini–Hochberg method (Benjamini & Hochberg, 1995). These socioeconomic impact (Kendall’s tau = 0.36; p = 0.217), nor with analyses could not be conducted for SEICAT scores due to limited median impacts (environmental: Kendall’s tau = −0.33; p = 0.224; data availability. socioeconomic: Kendall’s tau = −0.04; p = 0.9). Similar results KESNER and KUMSCHICK | 8279

(a) 80 taxonomic group to a growing list of universally comparable alien im- 9 MC pact assessments (Bacher et al., 2017; Evans et al., 2016; Kumschick 70 MN t et al., 2017). Information on socioeconomic and/or environmental 60 MO impact was available for most species included in this study (82.4%), which is comparable to other taxa (arthropods: 77.9%; birds: 84.6%; 50 11 MR 10 3 fish: 91.4%; mammals: 97%; plants: 93.8% Kumschick et al., 2015; 40 14 but see Measey et al., 2016 for amphibians: 41%). This indicates that 2 2 11 cords per habita 30 gastropod impacts are well researched, further reinforced by a high

Re average number of publications per studied species for environmen- 20 7 % 6 tal (5.6) and socioeconomic (8.9) impacts (Bacher et al., 2017; Evans 1 1 1 2 10 et al., 2016). The fact that gastropods’ socioeconomic impacts are 0 better-­studied than their environmental impacts is likely due to their Artificial Forest GrasslandWetland global status as agricultural and horticultural pests (here included (b) under “Material and immaterial goods for good life”; Barker, 2002; 70 a a b a Hollingsworth & Armstrong, 2003; Keiser, Häberli, & Stamp, 2012; 24 m 60 Nash & Hoffmann, 2012; Simms, Ester, & Wilson, 2006), which pro- 14 vides economic incentive to study them. This is reflected in the vast 50 20 14 amount of research effort put into mitigating agricultural and hor- 40 16 15 9 ticultural impacts by gastropods (Charwat et al., 1995; Coupland & 9 30 Baker, 1995; Desbiolles, Ballantyne, & Richards, 2003; Jeong, Lee, Hong, Shin, & Yun, 2012; Nash & Hoffmann, 2012). An example is a 20 8 cords per mechanis 4 research program in Australia, supported by the Australian grain in-

Re 3 10 dustry in 2000. This aimed solely at modifying existing crop harvest-

% 2 ing technology to reduce snail contamination, namely by Cochlicella 0 CompetitionPredation Disease Grazing barbara and Theba pisana, to harvested grain (MO impact: Coupland transmission & Baker, 1995; Desbiolles et al., 2003). Indeed, agricultural and hor- ticultural impacts are the most common means by which gastropods FIGURE 1 Distribution of impact records and severity across (a) harm society, representing 70% of SEICAT scores. However, these habitats and (b) mechanisms. Actual number of records indicated in small numbers on each bar. Differences in impact magnitude were impacts are generally relatively low only affecting individual persons analyzed using a Kruskal–Wallis test (see main text for results), rather than societal structure at large (Table 1). and letters indicate significant differences in impact magnitude A potential explanation for the relatively low impacts recorded as assessed with a Dunn test (competition predation: Z = 1.85, is that artificial socioeconomic systems may be more resilient to p = 0.07; competition disease transmission: Z = 7.11, p < 0.001; impact than environmental systems. Cities, for example, have been predation disease transmission: Z = 4.59, p < 0.001; competition grazing: Z = 2.01, p = 0.06; predation grazing: Z = 0.20, p = 0.84; described as extraordinarily resilient to change (Allenby & Fink, disease transmission grazing: Z = 7.11, p < 0.001) 2005; Fiksel, 2006). Socioeconomic resilience has been described as taking effect at the community level, such that socioeconomic sys- tems remain inert despite individual people making up these systems were found for native range latitude: neither maximum environ- experiencing change (Adger, 2000). For example, an agricultural cor- mental (Kendall’s tau = −0.14; p = 0.397) or socioeconomic impact poration that oversees many farms may experience harvesting prob- (Kendall’s tau = −0.26; p = 0.152), nor median impacts (environ- lems and yield losses due to gastropod contamination, which would mental: Kendall’s tau = −0.23; p = 0.18; socioeconomic: Kendall’s result in difficulties experienced by laborers in carrying out their tau = −0.32; p = 0.09) were correlated with it. jobs and potentially experience income reductions (MN impact). Higher impacting species were found to have a higher number of However, due to the aggressive response of agricultural science and publications underpinning their impacts (EICAT: Kendall’s tau = 0.60; management in researching and implementing solutions, gastropod p = <0.001; SEICAT: Kendall’s tau = 0.38; p = 0.035). For EICAT, this contamination would very seldom escalate to a point whereby liq- remained significant after removing a high-­leverage observation, uidation or abandonment of farms is necessary (MO or higher im- Tarebia granifera (Kendall’s tau = 0.56; p = <0.001). pact; e.g., Charwat et al., 1995; Fabian et al., 2012; Hollingsworth, Follett, & Armstrong, 2003; Prystupa, Holliday, & Webster, 1987; Simms et al., 2006; Wilson, Hughes, Hamacher, Barahona, & Glen, 4 | DISCUSSION 1996). This description of socioeconomic resilience is reflected by the high number of impacts on the well-­being of individuals (MN), This study has successfully categorized the global impacts of South but very few resulting in declines or abandonment of human ac- African alien gastropods into EICAT and SEICAT, adding a novel tivities (MO or higher). Relatively low socioeconomic impacts have 8280 | KESNER and KUMSCHICK also been recorded for mammals (Hagen & Kumschick, 2018) and country recorded this extent of upper tier impacts by Tarebia granif- amphibians (Bacher et al., 2017), except in two cases where cultural era—only Venezuela recorded a single MR impact (Pointier & Giboda, practices of indigenous communities were detrimentally affected by 1999). It evidently represents a severe threat to South African na- the alien species (dogs contributing to decline of vultures, which af- tive wetland invertebrate fauna, as it has shown to be for many is- fects burial rituals: Prakash et al., 2003; cane toads affecting bush land nations’ wetlands. South Africa may not have the managerial tucker hunting in Australia: Van Dam, Walden, & Begg, 2002). On resources to deal with an invader that is geographically widespread that note, it is important to state that our study only shows evidence over the eastern and northern parts of the country (Appleton, Forbes, of impact in developed countries due to lacking records from less & Demetriades, 2009), so it is probable that this threat may persist affluent regions, and it is unclear if low impacts to agriculture is a into the foreseeable future. Our data show that Tarebia granifera is a general rule in developing countries with less scientific and mana- major threat to native wetland fauna globally. Even though we found gerial resources. Despite South Africa being a developing country, no difference in impact magnitude between habitats, wetlands were it has a well-­developed agricultural sector, and recorded only MN the most commonly impacted and had the most upper tier impacts impacts to agriculture in this study (e.g., Herbert, 1997), and showed (Figure 1a), suggesting that gastropods are most likely to cause severe an aggressive management response to gastropod pests (Herbert & impacts within this habitat. This reinforces wetland habitats status as a Sirgel, 2001). global conservation priority (Dawson, Berry, & Kampa, 2003). Environmental impacts on the other hand are severe for many Despite gastropods showing no severe impacts via disease trans- species, and the absence of a correlation between SEICAT and EICAT mission (Figure 1b), one species, Zonitoides arboreus, has been shown scores might indicate they are generally of greater magnitude than to be an intermediate host of a disease that has caused deaths of socioeconomic impacts. However, comparing the two measures di- captive species (classified as a socioeconomic impact; Walden et al., rectly assumes scale equivalence between the two schemes, and 2017). This suggests that the potential for higher tier impacts via dis- even though the two systems follow the same general structure and ease transmission is evident in the gastropods. Similarly, gastropods share many common traits (i.e., nonlinear impact levels based on or- were found to be agents of disease transmission to humans (Ash, ders of magnitude, a common currency each throughout the impact 1976; Boray, 1978; Kim, Hayes, Yeung, & Cowie, 2014; Senanayake levels) it needs to be further evaluated whether the same impact et al., 2003), the most prominent disease being eosinophilic menin- levels should be seen as equal. We encourage a more thorough dis- gitis, caused by infection with Angiostrongylus cantonensis, a para- cussion of the issue of scale equivalence as it would greatly benefit sitic nematode of which various gastropods are intermediate hosts. the prioritization process for resource allocation and management, Schistosomiasis was also prominent in this study, known to be a highly but this is beyond the scope of this study. pathogenic human disease that can result in mortality (Burke et al., It is generally well known that aliens can inflict enormous envi- 2009). However, the studies describing human death did not specify ronmental impacts (Blackburn, Cassey, Duncan, Evans, & Gaston, particular gastropod species that vector the disease; therefore, these 2004; Karatayev, Burlakova, Karatayev, & Padilla, 2009; Mack could not be assessed under SEICAT. As such, none of the impacts on et al., 2000; Pimentel, Zuniga, & Morrison, 2005; Savidge, 1987). human health were upper tier impacts (SEICAT classifies human death Gastropods are no exception to this, with many species in this as MO impact). This raises potential concerns regarding the classifica- study recording high impacts involving local extinctions. Theba tion of impacts via disease transmission (see also Measey et al., 2016), pisana, and Helisoma duryi were implicated in causing MR impacts and it should be further explored how the direct impact of the disease to beach-­dwelling snails and snails inhabiting artificial drains re- can be disentangled from the impact caused by its transmission. spectively (Christie et al., 1981; Rumi et al., 2010). Moreover, It was estimated in 1989 that more than 4 million people were various gastropods have been consistently related to declines in infected with schistosomiasis in South Africa (Utroska et al., 1990). endemic island snail fauna populations, namely in Hawai’i, New Given that attempted control programs have been largely unsuc- Zealand and the Canary Islands (Curry & Yeung, 2013; Curry cessful (Magaisa, Taylor, Kjetland, & Naidoo, 2015), this figure is et al., 2016; Kappes et al., 2009; Mahlfeld, 2000; Meyer & Cowie, likely an underestimate for the current situation. It is likely that the 2010). This is potentially due to the uniqueness and vulnerability alien gastropods that were reported as vectors of the disease in this of island habitats (Mueller-­Dombois & Loope, 1990). One gastro- study (Aplexa marmorata and Radix rubiginosa), and which both occur pod, Tarebia granifera, was implicated in causing local extinctions in South African schistosomiasis risk areas (Appleton & Miranda, (MR) to native snails in wetlands in Puerto Rico (Giboda, Malek, & 2015; Magaisa et al., 2015), play a role in transmission to humans Correa, 1997), Venezuela (Pointier & Giboda, 1999), South Africa in South Africa, despite no disease transmission socioeconomic im- (De Kock & Wolmarans, 2008; Miranda & Perissinotto, 2014), and pacts being recorded there. Angiostrongylus cantonensis has been Cuba (Karatayev et al., 2009). found in South Africa in rats in KwaZulu-­Natal (Archer, Appleton, South Africa may be particularly vulnerable to high impacts by Mukaratirwa, & Hope, 2011). Despite a lack of evidence of infection Tarebia granifera, as it was the only species to record upper tier im- in humans in South Africa, it is likely, as in other Southern Hemisphere pacts in this country, with several pieces of evidence showing declines countries (e.g., Brazil, Australia), multiple cases of human infection to native populations (e.g., Jones et al., 2017; Miranda & Perissinotto, transmitted by South African alien gastropods were recorded in 2012; Miranda, Perissinotto, & Appleton, 2011). No other continental this study (Caldeira et al., 2007; Morassutti, Thiengo, Fernandez, KESNER and KUMSCHICK | 8281

Sawanyawisuth, & Graeff-­Teixeira, 2014; Rambo, Agostini, & Graeff-­ declines to the Hawai’ian snail fauna (Curry & Yeung, 2013; Curry Teixeira, 1997; Senanayake et al., 2003). Furthermore, there are mul- et al., 2016; Meyer & Cowie, 2010). The difficulty in identifying true tiple species alien to South Africa, all which occur in KwaZulu-­Natal native distributions due to human influence (Carlton, 1999) may be (Appleton & Miranda, 2015; Herbert, 2010), that have been shown confounded with the native range latitude correlations. For example, to vector the disease (Cornu aspersum, Limax maximus, Bradybaena Helisoma duryi had one native range indicated as Florida (Madsen, similaris, Deroceras laeve, Physa acuta, Limacus flavus, Zonitoides ar- 1985) and another as North America (Madsen & Frandsen, 1989). boreus, Deroceras reticulatum, Lehmannia valentiana, and Oxychilus Using a more inclusive approach, the native range sizes of this and alliarius). It is unclear to what degree these alien gastropods may other species may have been inflated. pose a disease threat to humans in South Africa, and if their erad- The fact that environmental and socioeconomic impact magni- ication would benefit public health, as other native or non-­native tudes were positively correlated to the number of publications sug- species may simply provide vectors. Further research into this issue gests one of two scenarios: First, there might be a publication bias, is needed. Nonetheless, it is unlikely that developing countries with and the maximum scores for species that are underrepresented in a lack of management resources and other urgent socioeconomic the literature are not a true reflection of their impact. Second, re- problems will have the capacity to manage the multiple alien gastro- search may focus on species that have greater impacts, therefore pods that pose a disease threat to humans. research effort reflects a species true impact. The latter scenario On another note, the fact that competition was shown to be the is supported by Pyšek et al. (2008), showing that research tends to most common mechanism by which gastropods cause impacts, as focus on species that are the most relevant to the environment/so- well as having the highest number of severe impacts suggests that ciety. This probably applies to this study, due to the species being on alien gastropods are more likely to cause significant harm to native average well represented in the literature (Bacher et al., 2017; Evans gastropods than to other taxa. et al., 2016). Moreover, socioeconomic impacts are particularly likely It is of interest that gastropods and birds, two very distant taxo- to have been noticed, because humans are directly affected. nomic groups, converge on similar probabilities (~0.3) of causing upper Generally, EICAT and SEICAT scores could be derived from all tier (MO or higher) environmental impacts overall (Evans et al., 2016). impact records found for gastropods, which shows the applicability This raises the question whether the proportion of severe impacts of the scoring schemes across taxa, especially given this was only caused by harmful alien species globally is the same across taxa. Should the third application of SEICAT following amphibians (Bacher et al., this be supported by further research, it may provide scope for univer- 2017) and some mammals (Hagen & Kumschick, 2018). However, the sal alien impact predictions, which will be significant for various risk scoring schemes may have room for improvement. For example, one assessment approaches (Keller & Kumschick, 2017). This highlights the score recorded for Tarebia granifera was described as a trophic cas- need for further application of EICAT to different taxonomic groups. cade (Hill, Jones, Hill, & Weyl, 2015), and there was no mechanism Our results do not support the general importance ascribed to describe this under EICAT. This was assigned the “structural im- to gastropod fecundity for their impacts (Barker, 1991; De Kock & pact on ecosystems” mechanism. Furthermore, EICAT methodology Wolmarans, 2008; Keller et al., 2007; Rumi et al., 2010). Rumi et al. dictates that maximum scores are the only indication of the severity (2010) describe a local extinction (MR) caused by Theba pisana as a of impact. We additionally used median values for our analyses to result of its high reproductive rate (having the second highest fe- account for the range in impact magnitudes recorded and suggest cundity, >1,500 eggs/female/year, Supporting Information Table S1), that each study should assess which measure is most suitable for its however the species with the highest fecundity, Physa acuta (>2,500) purpose. Furthermore, we suggest that EICAT and SEICAT should only reached a score of MN (Table 1). These conflicting results may consider incorporating the likelihood of a high score being realized be due to the context dependency of alien introductions. For exam- into the overall quantification of the impact of a species. Despite ple, gastropod fecundities have been shown to fluctuate with tem- these limitations, the analyses undertaken in this study shed light perature and moisture (Brackenbury & Appleton, 1991; Hadfield, on the nature and context dependency of gastropod impacts. This 1989; Kozlowski, 2000; Nash & Hoffmann, 2012), and perhaps these has great relevance to many risk assessment approaches, which can species have not found habitats conducive to maximum reproduc- ultimately aid conservation management. Further studies should tive output. Given the limited availability of fecundity information apply these schemes to multiple novel taxa, allowing for potential (11 values), it would be interesting to test if this, and the absence of generic patterns to be identified, which would greatly improve the any correlations with impact, might change with more data. understanding of alien impacts in an ever-­changing biological realm. The absence of a correlation between native range latitude and environmental impacts is surprising, being contrary to the findings ACKNOWLEDGMENTS for birds and mammals alien to Europe (Kumschick et al., 2013), and cactaceae (Novoa et al., 2016). Given the complex nature of alien We acknowledge Rueben Keller for providing some fecundity data, impact (Simberloff et al., 2013) there is reason to believe that native and John Measey, Thomas Evans, Susan Canavan, Matthew Mayne, range latitude indeed has no relation to impact, at least for gastro- and Wesley Hartmann for helpful discussions on the analyses. We pods. A good example of this is the genus Oxychilus, whose species thank Jenny Leonard for editing an earlier draft of this manuscript. DK have narrow native range latitudes, but have caused significant would like to thank the South African National Research Foundation 8282 | KESNER and KUMSCHICK for funding. SK acknowledges funding from the South African National Barker, G. M. (2002). Gastropods as Pests in New Zealand Pastoral Department of Environmental Affairs through its funding of the South Agriculture, with Emphasis on Agriolimacidae, Arionidae and Milacidae. In G. M. Barker (Ed.), Molluscs as crop pests (pp. 361–423). Wallingford, African National Biodiversity Institute’s Invasive Species Programme, UK: CAB International. https://doi.org/10.1079/9780851993201.0000 and the DST-­NRF Centre of Excellence for Invasion Biology. Benjamini, Y., & Hochberg, Y. (1995). Controlling the false discovery rate: A practical and powerful approach to multiple testing. Journal of the Royal Statistical Society Series B Methodological, 57, 289–300. CONFLICT OF INTEREST Blackburn, T. M., Cassey, P., Duncan, R. P., Evans, K. L., & Gaston, K. J. None declared. (2004). Avian extinction and mammalian introductions on oceanic islands. Science, 305(5692), 1955–1958. https://doi.org/10.1126/ science.1101617 Blackburn, T. M., Essl, F., Evans, T., Hulme, P. E., Jeschke, J. M., Kühn, AUTHORS’ CONTRIBUTION I., … Bacher, S. (2014). A unified classification of alien species Both authors conceptualized the study and revised the manuscript. based on the magnitude of their environmental impacts. PLoS Biology, 12(5), e1001850. https://doi.org/doi: 10.1371/journal. DK collected and analyzed the data and led the writing of the manu- pbio.1001850 script with inputs from SK. Boray, J. C. (1978). The potential impact of exotic Lymnaea spp. on fasci- oliasis in Australasia. Veterinary Parasitology, 4, 127–141. https://doi. org/10.1016/0304-4017(78)90004-3 DATA ACCESSIBILITY Brackenbury, T. D., & Appleton, C. C. (1991). Effect of controlled tem- peratures on gametogenesis in the gastropods Physa acuta (Physidae) All data used in this study are available in the main manuscript or and Bulinus tropicus (Planorbidae). Journal of Molluscan Studies, 57, attached in the Supporting Information. 461–469. https://doi.org/10.1093/mollus/57.4.461 Burke, M. L., Jones, M. K., Gobert, G. N., Li, Y. S., Ellis, M. K., & McManus, D. P. (2009). Immunopathogenesis of human schis- ORCID tosomiasis. Parasite Immunology, 31, 163–176. https://doi. org/10.1111/j.1365-3024.2009.01098.x Sabrina Kumschick http://orcid.org/0000-0001-8034-5831 Caldeira, R. L., Mendonça, C. L. G. F., Goveia, C. O., Lenzi, H. L., Graeff- Teixeira, C., Lima, W. S., … Carvalho, O. D. S. (2007). First record of molluscs naturally infected with Angiostrongylus cantonensis REFERENCES (Chen, 1935) (Nematoda: Metastrongylidae) in Brazil. Memórias do Instituto Oswaldo Cruz, 102, 887–889. https://doi.org/doi: 10.1590/ Adger, W. N. (2000). Social and ecological resilience: Are they re- S0074-02762007000700018 lated? Progress in Human Geography, 24(3), 347–364. https://doi. Carlton, J. T. (1999). Molluscan invasions in marine and estuarine com- org/10.1191/030913200701540465 munities. Malacologia, 41, 439–454. Allenby, B., & Fink, J. (2005). Toward inherently secure and resilient so- Convention on Biological Diversity (CBD) (2013). Aichi biodiversity tar- cieties. 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Supporting Information

Table S1: Trait variables for all 34 species included in this study. Data only shown if available. Native range latitudes are in decimal degrees.

Native range Fecundity Species Native range latitude [eggs/female/year] Aplexa marmorata South America

Arion hortensis Western and southern Europe 15.15

Arion intermedius Central and western Europe 12.69

Bradybaena similaris southeast Asia and Indonesia 25.00

Cochlicella barbara Mediterranean 12.29

Cochlicopa cf. lubrica Europe, Northern America

Cochlicopa cf. lubricella Europe, Asia, North America

Cornu aspersum southern and western Europe 24.32 430

Deroceras laeve Holarctic (high latitudes) 44.08 612

Deroceras Mediterranean 3.97 612 panormitanum

Deroceras reticulatum Europe 29.54 612

Discus rotundatus Europe

Eobania vermiculata Mediterranean region 14.74

Gyraulus chinensis South East Asia

Helisoma duryi North America 11.71 100

Lauria cylindracea Western Europe, Mediterranean

Lehmannia nyctelia N Africa, Central and SE Europe

Lehmannia valentiana Iberian Peninsula 2.98

Limacus flavus Europe 23.16

Limax maximus Europe, North Africa, and Asia 38.40 223 minor (western palearctic)

Littorina saxatilis Eastern North Atlantic 19.59

Lymnaea columella North America 29.33 619

Milax gagates Mediterranean 0.60 100

Oxychilus alliarius Western Europe 15.18 2

Native range Fecundity Species Native range latitude [eggs/female/year]

Oxychilus cellarius Western Europe 10.77

Oxychilus draparnaudi Europe, North Africa, and Asia 35.78 minor Physa acuta North America 30.29 2598

Radix rubiginosa Indo-China and Indonesia 27.33

Tarebia granifera India, Southeast Asia, the 30.62 213 Philippines, Japan. Hawaii

Thais blanfordi Tropical Indo-Pacific

Theba pisana Mediterranean, western 27.49 1525 European and north African coastal distribution Vallonia costata Europe, Eastern USA

Vallonia pulchella Holarctic (high latitudes) 45.00

Zonitoides arboreus Canada, Central America, 46.15 Caribbean

3

Appendix S1: Literature sources for native range and fecundity information

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Nash, M. A., & Hoffmann, A. A. (2012). Effective invertebrate pest management in dryland cropping in southern Australia: The challenge of marginality. Crop protection, 42, 289-304. doi:http:/dx.doi.org/10.1016/j.cropro.2012.06.017 Oteros, J. (2014). Modelización del ciclo fenológico reproductor del olivo (Doctoral dissertation). University of Córdoba, Córdoba, Spain. Picker, M. D., & Griffiths, C. L. (2017). Alien animals in South Africa–composition, introduction history, origins and distribution patterns. Bothalia-African Biodiversity & Conservation, 47, 1-19. Pilsbry, H. A. (1946). Land mollusca of North America (North of Mexico), Vol II: Part 1. [Monographs]. Academy of Natural Sciences of Philadelphia, 480-483. Roth, B., & Sadeghian, P. S. (2006). Checklist of the land snails and slugs of California. California, CA: Santa Barbara Museum of Natural History. Snow, D. W., & Perrins, C. M. (1998). The Birds of the Western Palearctic. Oxford, UK: Oxford University Press. Solem, A. (1964). New records of New Caledonian nonmarine mollusks and an analysis of the introduced mollusks. Pacific Science, 8, 130-137. United Nations Statistics Division, (2015, May). Standard Country and Area Codes Classifications (M49). Retrieved from https://unstats.un.org/unsd/methodology/m49/. Waldén, H. W. (1961). On the variation, nomenclature, distribution and taxonomic position of Limax (Lehmannia) valentianus FÉRUSSAC (Gastropoda: Pulmonata). Arkiv för Zoologi, 15, 71-96. Wiktor, A. (1987). Milacidae (Gastropoda, Pulmonata): Systematic monograph. Warsaw, Poland: Państwowe Wydawnictwo Naukowe. Wiktor, A. (2001). Deroceras (Deroceras) panormitanum (Lessona et Pollonera, 1882)-a new introduced slug species in Poland (Gastropoda: Pulmonata: Agriolimacidae). Folia Malacologica, 9. 155-157.

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Appendix S2: Literature used to score gastropod environmental impacts under EICAT

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Gouyon, P. H., Fort, P. H., & Caraux, G. (1983). Selection of seedlings of Thymus vulgaris by grazing slugs. Journal of Ecology, 71, 299-306. Gracenea, M., & González-Moreno, O. (2002). Life cycle of Brachylaima mascomai n. sp.(Trematoda: Brachylaimidae), a parasite of rats in the Llobregat Delta (Spain). Journal of Parasitology, 88, 124-133. doi:https://doi.org/10.1645/00223395(2002)088[0124:LCOBMN]2.0.CO;2 Gutierrez, A. et al., (1997). Relationship of the prosobranch snails Pomacea paludosa, Tarebia granifera and Melanoides tuberculata with the abiotic environment and freshwater snail diversity in the central region of Cuba. Malacological Review, 30, 39-44. Hickford, M. J., Cagnon, M., & Schiel, D. R. (2010). Predation, vegetation and habitat- specific survival of terrestrial eggs of a diadromous fish, Galaxias maculatus (Jenyns, 1842). Journal of Experimental Marine Biology and Ecology, 385, 66-72. doi:10.1016/j.jembe.2010.01.010 Hill, J. M. et al., (2015). Comparisons of isotopic niche widths of some invasive and indigenous fauna in a South African river. Freshwater Biology, 60, 893-902. doi:10.1111/fwb.12542 Holland, K. D., Mcdonnell, M. J., & Williams, N. S. (2007). Abundance, species richness and feeding preferences of introduced molluscs in native grasslands of Victoria, Australia. Austral Ecology, 32, 626-634. doi:10.1111/j.1442- 9993.2007.01749.x Joe, S. M. (2006). Impact of alien slugs on native plant seedlings in a diverse mesic forest, O ‘ahu, Hawai ‘i, and a study of slug food plant preferences (Unpublished master’s thesis). University of Hawaii at Manoa, Honolulu, Hawaii. Joe, S. M., & Daehler, C. C. (2008). Invasive slugs as under-appreciated obstacles to rare plant restoration: Evidence from the Hawaiian Islands. Biological Invasions, 10, 245-255. doi:10.1007/s10530-007-9126-9 Jones, R. W. et al., (2017). The abundance of an invasive freshwater snail Tarebia granifera (Lamarck, 1822) in the Nseleni River, South Africa. African Journal of Aquatic Science, 42, 75-81. doi:10.2989/16085914.2017.1298984 Kappes, H. et al., (2009). Native and introduced gastropods in laurel forests on Tenerife, Canary Islands. Acta Oecologica, 35, 581-589. doi:10.1016/j.actao.2009.05.004 Karatayev, A. Y. et al., (2009). Introduction, distribution, spread, and impacts of exotic freshwater gastropods in Texas. Hydrobiologia, 619, 181-194. doi:10.1007/s10750- 008-9639-y Kim, J. R. et al., (2014). Diverse gastropod hosts of Angiostrongylus cantonensis, the rat lungworm, globally and with a focus on the Hawaiian Islands. PLoS One, 9(5), e94969. doi:10.1371/journal.pone.0094969 Kralka, R. A., & Samuel, W. M. (1984). Experimental life cycle of Protostrongylus boughtoni (Nematoda: Metastrongyloidea), a lung worm of snowshoe hares, Lepus americanus. Canadian Journal of Zoology, 62, 473-479. Lankester, M. W., & Anderson, R. C. (1968). Gastropods as intermediate hosts of Pneumostrongylus tenuis Dougherty of white-tailed deer. Canadian Journal of Zoology, 46, 373-383. Lankester, M. W., & Peterson, W. J. (1996). The possible importance of wintering yards in the transmission of Parelaphostrongylus tenuis to white-tailed deer and 8

moose. Journal of Wildlife Diseases, 32, 31-38. doi:https://doi.org/10.7589/0090- 3558-22.4.582 Larned, S. T., Chong, C. T., & Punewai, N. (2001). Detrital fruit processing in a Hawaiian stream ecosystem. Biotropica, 33, 241-248. Lidicker, W. Z. (1976). Experimental manipulation of the timing of reproduction in the California vole. Researches on Population Ecology, 18, 14-27. Lovett, A. L., & Black, A. B. (1920). The Gray Garden Slug: With notes on allied forms. Station Bulletin, 170, 1-43. Mackerras, M. J., & Sandars, D. F. (1955). The life history of the rat lung-worm, Angiostrongylus cantonensis (Chen)(Nematoda: Metastrongylidae). Australian Journal of Zoology, 3, 1-21. Madsen, H. (1979). Further laboratory studies on the interspecific competition between Helisoma duryi (Wetherby) and the intermediate hosts of Schistosoma mansoni Sambon: Biomphalaria alexandrina (Ehrenberg) and B. camerunensis (Boettger). Hydrobiologia, 66, 181-192. Madsen, H. (1979). Preliminary observation on the role of conditioning and mechanical Interference with egg masses and Juveniles in the competitive relationships Between Helisoma Duryi (Wetherby) and the Intermediate host of Schistosoma Mansoni Sambon: Biomphalaria Camerunensis (Boettger). Hydrobiologia, 67, 207- 214. Madsen, H. (1985). The effect of Helisoma duryi on the cercarial production of Schistosoma mansoni-infected Biomphalaria alexandrina: Evaluation of chemical interferences and direct competition. Parasitology Research, 71, 71-77. Madsen, H., & Frandsen, F. (1979). Studies on the interspecific competition between Helisoma duryi (Wetherby) and Biomphalaria camerunensis (Boettger). Size-weight relationships and laboratory competition experiments. Hydrobiologia, 66, 17-23. Mahlfeld, K. (2000). Impact of introduced gastropods on molluscan communities, northern North Island. Conservation Advisory Science Notes (No. 277). Department of Conservation, Wellington. Mahlfeld, K. et al., (2012). The conservation status of New Zealand terrestrial Gastropoda excluding Powelliphanta. New Zealand Entomologist, 35, 103-109. doi:10.1080/00779962.2012.686313 March, J. G. et al., (2002). Effects of freshwater shrimp assemblages on benthic communities along an altitudinal gradient of a tropical island stream. Freshwater Biology, 47, 377-390. Mead, A. et al., (2011). Introduced and cryptogenic marine and estuarine species of South Africa. Journal of Natural History, 45, 2463-2524. doi:10.1080/00222933.2011.595836 Meyer III, W. M., & Cowie, R. H. (2010). Feeding preferences of two predatory snails introduced to Hawaii and their conservation implications. Malacologia, 53, 135-144. Meyer III, W. M., & Yeung, N. W. (2011). Trophic relationships among terrestrial molluscs in a Hawaiian rain forest: Analysis of carbon and nitrogen isotopes. Journal of Tropical Ecology, 27, 441-445. doi:10.1017/S02 6646 74110000 5 8 Meyer-Lassen, J., & Madsen, H. (1989). The effect of varying relative density and varying food supply on interspecific competition between Helisoma duryi and Bulinus truncatus (Gastropoda, Planorbidae). Journal of Molluscan Studies, 55, 89- 96. 9

Miranda, N. A. F, & Perissinotto, R. (2012). Stable isotope evidence for dietary overlap between alien and native gastropods in coastal lakes of northern KwaZulu-Natal, South Africa. PLoS One, 7(2), e31897. doi:10.1371/journal.pone.0031897 Miranda, N. A. F, & Perissinotto, R. (2014). Benthic assemblages of wetlands invaded by Tarebia granifera (Lamarck, 1822)(Caenogastropoda: Thiaridae) in the iSimangaliso Wetland Park, South Africa. Molluscan Research, 34, 40-48. doi:http://dx.doi.org/10.1080/13235818.2013.866177 Miranda, N. A. F., & Perissinotto, R. (2014). Effects of an alien invasive gastropod on native benthic assemblages in coastal lakes of the iSimangaliso Wetland Park, South Africa. African Invertebrates, 55, 209-228. Miranda, N. A. F., Perissinotto, R., & Appleton, C.C. (2010). Salinity and temperature tolerance of the invasive freshwater gastropod Tarebia granifera. South African Journal of Science, 106(3/4), 01-07. doi:10.4102/sajs.v106i3/4.156 Miranda, N. A. F., Perissinotto, R., & Appleton, C.C. (2011). Feeding dynamics of the invasive gastropod Tarebia granifera in coastal and estuarine lakes of northern KwaZulu-Natal, South Africa. Estuarine, Coastal and Shelf Science, 91, 442-449. doi:10.1016/j.ecss.2010.11.007 Miranda, N. A. F, Perissinotto, R., & Appleton, C.C. (2011). Population structure of an invasive parthenogenetic gastropod in coastal lakes and estuaries of Northern KwaZulu-Natal, South Africa. PLoS One, 6(8), e24337. doi:10.1371/journal.pone.0024337 Mitchell, A. J., & Brandt, T. M. (2003, April). Thermal limits of redrimmed melania Melanoides tuberculata,(Gastropoda: Prosobranchia: Thiaridae): Implication for control and distribution of a snail that vectors a gill trematode causing serious infection in fish. In Annual Eastern Fish Health Workshop (Vol. 52). Monson, R. A., & Post, G. (1972). Experimental transmission of Protostrongylus stilesi to bighorn-mouflon sheep hybrids. The Journal of Parasitology, 58, 29-33. Morgan, J. W. (1997). The effect of grassland gap size on establishment, growth and flowering of the endangered Rutidosis leptorrhynchoides (Asteraceae). Journal of Applied Ecology, 34, 566-576. Moslemi, J. M. et al., (2012). Impacts of an invasive snail (Tarebia granifera) on nutrient cycling in tropical streams: The role of riparian deforestation in Trinidad, West Indies. PLoS One, 7(6), e38806. doi:10.1371/journal.pone.0038806 Mountainspring, S. et al., (1990). Ecology, behavior, and conservation of the Poo-uli (Melamprosops phaeosoma). The Wilson Bulletin, 102, 109-122. Nollen, P. M., & Murray, H. D. (1978). Philophthalmus gralli: Identification, growth characteristics, and treatment of an oriental eyefluke of birds introduced into the continental United States. The Journal of Parasitology, 64, 178-180. Odendaal, L. J., Haupt, T. M., & Griffiths, C. L. (2008). The alien invasive land snail Theba pisana in the West Coast National Park: Is there cause for concern?. Koedoe, 50, 93-98. Perera, A. A. V., & Valderrama, S. P. (2010). Endemic Freshwater molluscs of Cuba and their conservation status. Tropical Conservation Science, 3, 190-199. Perera, D.P.G., Yong, C.M., & Ferrer, L.J. (1991). The biological control of Fossaria cubensis, the intermediate host of Fasciola hepatica, in 2 localities with different control agents. Revista Cubana de Medicina Tropical, 43, 17-20. 10

Perera, G. et al., (1995). Ecological structure and factors regulating the population dynamics of the freshwater snail populations in Hanabanilla Lake, Cuba. Malacological Review, 28, 63-69. Phillips, C. T., Alexander, M. L., & Howard, R. (2010). Consumption of eggs of the endangered fountain darter (Etheostoma fonticola) by native and nonnative snails. The Southwestern Naturalist, 55, 115-117. Pointier, J.P., & Giboda, M. (1999). The case for biological control of snail intermediate hosts of Schistosoma mansoni. Parasitology Today, 15, 395-397. Prentice, M.A. (1983). Displacement of Biomphalaria glabrata by the snail Thiara granifera in field habitats in St. Lucia, West Indies. Annals of Tropical Medicine & Parasitology, 77, 51-59. Raw, J. L., Miranda, N. A. F., & Perissinotto, R. (2013). Chemical cues released by an alien invasive aquatic gastropod drive its invasion success. PLoS One, 8(5), e64071. doi:10.1371/journal.pone.0064071 Raw, J. L., Miranda, N. A. F., & Perissinotto, R. (2015). Chemical cues released by heterospecific competitors: Behavioural responses of native and alien invasive aquatic gastropods. Aquatic Sciences, 77, 655-666. doi:10.1007/s00027-015-0409- 4 Rollo, C.D. (1983). Consequences of competition on the reproduction and mortality of three species of terrestrial slugs. Researches on Population Ecology, 25, 20-43. Rollo, C.D. (1983). Consequences of competition on the time budgets, growth and distributions of three species of terrestrial slugs. Researches on Population Ecology, 25, 44-68. Rondelaud, D. (1977). Résultats et problèmes posés par l'introduction de mollusques Zonitidae dans quelques biotopes à Limnées tronquées en Indre et Haute-Vienne [Results and problems set by the introduction of Zonitidae snails in some biotopes of Lymnaea trancatula Müller in Indre and Haute-Vienne, France (author's transl]. Annales de Parasitologie Humaine et Comparee, 52, 521-530. Rondelaud, D. et al., (2006). The control of Galba truncatula (Gastropoda: Lymnaeidae) by the terrestrial snail Zonitoides nitidus on acid soils. Biological Control, 39, 290-299. doi:https://doi.org/10.1016/j.biocontrol.2006.07.015 Rumi, A., Sánchez, J., & Ferrando, N. S. (2010). Theba pisana (Müller, 1774) (Gastropoda, Helicidae) and other alien land molluscs species in Argentina. Biological Invasions, 12, 2985-2990. doi:10.1007/s10530-010-9715-x Samson, J., & Holmes, J. C. (1985). Modes of entry of first stage larvae of Protostrongylus stilesi and P. rushi (Nematoda: Metastrongyloidea) in the snail intermediate host Vallonia pulchella. Canadian Journal of Zoology, 63, 2481-2482. Samson, J., & Holmes, J. C. (1985). The effect of temperature on rates of development of larval Protostrongylus spp.(Nematoda: Metastrongyloidea) from bighorn sheep, Ovis canadensis canadensis, in the snail Vallonia pulchella. Canadian Journal of Zoology, 63, 1445-1448. Samuel, W. M., Platt, T. R., & Knispel-Krause, S. M. (1985). Gastropod intermediate hosts and transmission of Parelaphostrongylus odocoilei, a muscle-inhabiting nematode of mule deer, Odocoileus h. hemionus, in Jasper National Park, Alberta. Canadian Journal of Zoology, 63, 928-932. Shakeel, M. A., & Mowat, D. J. (1992). The potential transmission of clover rot, Sclerotinia trifoliorum Erikss., by slugs. Grass and Forage Science, 47, 199-202. 11

Smith, V.R. (2007). Introduced slugs and indigenous caterpillars as facilitators of carbon and nutrient mineralisation on a sub-Antarctic island. Soil Biology and Biochemistry, 39, 709-713. doi:10.1016/j.soilbio.2006.09.026 Spratt, D.M., Haycock, P., & Walter, E.L. (2001). Life history and pathogenesis of Gallegostrongylus australis (Nematoda: Angiostrongylidae) in Muridae. Parasite, 8, 115-125. doi: http://dx.doi.org/10.1051/parasite/2001082115 Stockdale-Walden, H. D. et al., (2015). Angiostrongylus cantonensis in introduced gastropods in southern Florida. Journal of Parasitology, 101, 156-159. Upshall, S.M., Burt, M.D.B., & Dilworth, T.G. (1986). Parelaphostrongylus tenuis in New Brunswick: The parasite in terrestrial gastropods. Journal of Wildlife Diseases, 22, 582-585. doi:https://doi.org/10.7589/0090-3558-22.4.582 Van Oosterhout, C. et al., (2013). Invasive freshwater snails provide resource for native marine hermit crabs. Aquatic Invasions, 8, 185-191. doi:http://dx.doi.org/10.3391/ai.2013.8.2.06 Vargas, M., Gomez, J., & Perera, G. (1991). Geographic expansion of Marisa cornuarietis and Tarebia granifera in the Dominican Republic. Journal of Medical and Applied Malacology, 3, 69-72. Vsevolodov, B.P., & Soboleva, T.N. (1981). Morphobiological characteristics of Hasstilesia ovis (Trematoda: Brachylaimidae) and the pathomorphological changes it causes in sheep intestines. Parazitologiia, 15, 415-419. Wardle, D.A., & Barker, G.M. (1997). Competition and herbivory in establishing grassland communities: Implications for plant biomass, species diversity and soil microbial activity. Oikos, 80, 470-480. Wardle, D.A. et al., (1998). Can comparative approaches based on plant ecophysiological traits predict the nature of biotic interactions and individual plant species effects in ecosystems?. Journal of Ecology, 86, 405-420. Zhongzhang, T., & Chongti, T. (1977). The Biology and Epidemiology of Eurytrema Coelomaticum (Giard et Billet, 1892) and Eurytrema Pancreaticum (Janson, 1889) in Cattle and Sheep in China [J]. Acta Zoologica Sinica, 3, 004.

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Appendix S3: Literature used to score gastropod socio-economic impacts under SEICAT Abdel-Aty, A. S., & Abdel-Megeed, A. (2014). Molluscicidal activity of Some cyanide derivatives. Asian Journal of Chemistry, 26, 7837-7842. doi:http://dx.doi.org/10.14233/ajchem.2014.17982 Abdelgaleil, S. A. (2010). Molluscicidal and insecticidal potential of monoterpenes on the white garden snail, Theba pisana (Muller) and the cotton leafworm, Spodoptera littoralis (Boisduval). Applied Entomology and Zoology, 45, 425-433. doi:10.1303/aez.2010.425 Aghazadeh, M. et al., (2015). A survey of Angiostrongylus species in definitive hosts in Queensland. International Journal for Parasitology: Parasites and Wildlife, 4, 323-328. doi:http://dx.doi.org/10.1016/j.ijppaw.2015.06.003 Airey, W.J. (1987). Laboratory studies on damage to potato tubers by slugs. Journal of Molluscan Studies, 53, 97-104. Ali, S.M., Yousef, N.M., & Nafady, N.A. (2015). Application of biosynthesized silver nanoparticles for the control of land snail Eobania vermiculata and some plant pathogenic fungi. Journal of Nanomaterials, 2015, 1-10. doi:http://dx.doi.org/10.1155/2015/218904 Alicata, J. E., & McCarthy, D. D. (1964). On the incidence and distribution of the rat lungworm Angiostrongylus cantonensis in the Cook Islands, with observations made in New Zealand and Western Samoa. Canadian Journal of Zoology, 42, 605- 611. Altieri, M.A. et al., (1982). Biological control of Limax maximus and Helix aspersa by indigenous predators in a daisy field in central coastal California. Acta Oecologica. Oecologia Applicata, 3, 387-390. Appleton, C. C., & Nadasan, D. S. (2002). First report of Tarebia granifera (Lamarck, 1816)(Gastropoda: Thiaridae) from Africa. Journal of Molluscan Studies, 68, 399- 402. Ash, L. R. (1976). Observations on the role of mollusks and planarians in the transmission of Angiostrongylus cantonensis infection to man in New Caledonia. Revista de Biología Tropical, 24, 163-74. Baker, G.H. (1989). Damage, population dynamics, movement and control of pest helicid snails in southern Australia. [Monograph]. British Crop Protection Council, 175-185. Baker, G. H. (2008). The population dynamics of the mediterranean snails Cernuella virgata, Cochlicella acuta (Hygromiidae) and Theba pisana (Helicidae) in pasture– cereal rotations in South Australia: A 20-year study. Australian Journal of Experimental Agriculture, 48, 1514-1522. doi:https://doi.org/10.1071/EA08031 Baker, G. H., Beckett, S., & Thammavongsa, B. (2012). Are the European snails, Theba pisana (Müller, 1774)(Helicidae), Cernuella virgata (da Costa, 1778) and Cochlicella acuta (Müller, 1774)(Hygromiidae) attracted by potential food odours?. Crop Protection, 42, 88-93. doi:https://doi.org/10.1016/j.cropro.2012.05.021 Baker, G. H., & Hawke, B. G. (1990). Life history and population dynamics of Theba pisana (Mollusca: Helicidae) in a cereal-pasture rotation. Journal of Applied Ecology, 27, 16-29. 13

Baker, G. H., & Vogelzang, B. K. (1988). Life history, population dynamics and polymorphism of Theba pisana (Mollusca: Helicidae) in Australia. Journal of Applied Ecology, 25, 867-887. Baldock, F.C., & Arthur, R.J. (1985). A survey of fascioliasis in beef cattle killed at abattoirs in southern Queensland. Australian Veterinary Journal, 62, 324-326. Banha, F., Marques, M., & Anastácio, P. M. (2014). Dispersal of two freshwater invasive macroinvertebrates, Procambarus clarkii and Physella acuta, by off‐road vehicles. Aquatic Conservation: Marine and Freshwater Ecosystems, 24, 582-591. doi:10.1002/aqc.2453 Barker, G.M. (1989). Slug problems in New Zealand pastoral agriculture. [Monograph]. British Crop Protection Council, 59-68. Barker, G.M. (1991). Slug density‐seedling establishment relationships in a pasture renovated by direct drilling. Grass and Forage Science, 46, 113-120. Barker, G.M. (2002). Gastropods as pests in New Zealand pastoral agriculture, with emphasis on Agriolimacidae, Arionidae and Milacidae. In G.M. Barker (Ed.), Molluscs as crop pests (pp. 361-423). Wallingford, UK: CAB International. Barker, G. M., & Addison, P. J. (1992). Pest status of slugs (Stylommatophora: Mollusca) in two New Zealand pastures. Crop Protection, 11, 439-442. Barker, G. M., & Efford, M. G. (2004). Predatory gastropods as natural enemies of terrestrial gastropods and other invertebrates. In G.M. Barker (Ed.), Natural enemies of terrestrial molluscs (pp. 279-403). Wallingford, UK: CAB International. Barnes, H. F., & Weil, J. W. (1945). Slugs in gardens: Their numbers, activities and distribution. Part 2. The Journal of Animal Ecology, 14, 71-105. Bartsch, P., & Quick, M. E. (1926). An anatomic study of Zonitoides arboreus Say. Journal of Agricultural Research, 32, 783-791. Basch, P. F. (1965). Completion of the life cycle of Eurytrema pancreaticum (Trematoda: Dicrocoeliidae). The Journal of Parasitology, 51, 350-355. Boray, J. C. (1978). The potential impact of exotic Lymnaea spp. on fascioliasis in Australasia. Veterinary Parasitology, 4, 127-141. Boray, J.C., Fraser, G.C., Williams, J.D., & Wilson, J.M. (1985). The occurrence of the snail Lymnaea columella on grazing areas in New South Wales and studies on its susceptibility to Fasciola hepatica. Australian Veterinary Journal, 62, 4-6. Brooks, A. S. et al., (2005). A laboratory‐based comparison of a molluscicide and an alternative food source (red clover) as means of reducing slug damage to winter wheat. Pest Management Science, 61, 715-720. doi:10.1002/ps.1056 Bunnag, T. et al., (1983). Schistosoma incognitum and its zoonotic potential role in Phitsanulok and Phichit provinces, northern Thailand. The Southeast Asian Journal of Tropical Medicine and Public Health, 14, 163-170. Butcher, A. R. (2003). Brachylaima cribbi n. sp.(Digenea: Brachylaimidae): Taxonomy, life-cycle kinetics and infections in animals and humans (Unpublished doctoral dissertation). The University of Adelaide, Adelaide, Australia. Butcher, A. R. et al., (2002). Brachylaima cribbi (Digenea: Brachylaimidae): Scanning electron microscopical observations of the life-cycle stages. Journal of Helminthology, 76, 207-215. doi:10.1079/JOH2002119 14

Butcher, A. R., & Grove, D. I. (2001). Description of the life-cycle stages of Brachylaima cribbi n. sp.(Digenea: Brachylaimidae) derived from eggs recovered from human faeces in Australia. Systematic Parasitology, 49, 211-221. Cabaret, J. (1988). Natural infection of land-snails by protostrongylids on a pasture grazed by sheep in the Rabat area of Morocco. Veterinary Parasitology, 26, 297- 304. Cadiz, F. J., & Gallardo, C. S. (2007). Arion intermedius (Gastropoda: Stylommatophora); first record of this introduced slug in Chile, with notes on its anatomy and natural history. Revista Chilena de Historia Natural, 80(1), 99-108. Caldeira, R. L. et al., (2007). First record of molluscs naturally infected with Angiostrongylus cantonensis (Chen, 1935)(Nematoda: Metastrongylidae) in Brazil. Memórias do Instituto Oswaldo Cruz, 102, 887-889. doi:http://dx.doi.org/10.1590/S0074-02762007000700018 Capinera, J. L., & White, J. (2011). Terrestrial snails affecting plants in Florida (Publication No. EENY-497). Department of Entomology, University of Florida. Carvalho, O. D. S. et al., (2012). Angiostrongylus cantonensis (Nematode: Metastrongyloidea) in molluscs from harbour areas in Brazil. Memórias do Instituto Oswaldo Cruz, 107, 740-746. doi:http://dx.doi.org/10.1590/S0074- 02762012000600006 Castiellejo, J., Seijas, I., & Villoch, F. (1996, September). Slug and snail pests in Spanish crops and their economical importance. In Slug & snail pests in agriculture: Proceedings of a Symposium, British Crop Protection Council, University of Kent, Canterbury, UK. Chang, C. P. (1990). Evaluation of chemical and exclusion methods for control of Bradybaena similaris (Ferussac) on grapevine in Taiwan. Agriculture, Ecosystems & Environment, 31, 85-88. Charlton, J. F. L. (1978). Slugs as a possible cause of establishment failure in pasture legumes oversown in boxes. New Zealand Journal of Experimental Agriculture, 6, 313-317. Charwat, S.M., & Davies, K.A. (1999). Laboratory screening of nematodes isolated from South Australia for potential as biocontrol agents of helicid snails. Journal of Invertebrate Pathology, 74, 55-61. Charwat, S.M., Davies, K.A., & Fraser, H. (1995). Nematodes as biocontrol agents of helicid snails. (RIRDC Project No. UA-31A, Publication No. 01/03). Rural Industries Research and Development Corporation. Clemente, N.L. et al., (2008). Biological studies and phenology of the slug Deroceras reticulatum (Müller, 1774)(Pulmonata: Stylommatophora). Invertebrate Reproduction & Development, 52, 23-30. doi:10.1080/07924259.2008.9652268 Córdoba, V., & León, S. (2010). Effects of agroecological and conventional handling in slug populations in lettuce in Tenjo, Cundinamarca (Colombia). Acta Biológica Colombiana, 15, 115-128. Coupland, J. B., & Baker, G. (1995). The potential of several species of terrestrial Sciomyzidae as biological control agents of pest helicid snails in Australia. Crop Protection. 14, 573-576. Coupland, J. B., Espiau, A., & Baker, G. (1994). Seasonality, longevity, host choice, and infection efficiency of Salticella fasciata (Diptera: Sciomyzidae), a candidate for the biological control of pest helicid snails. Biological Control, 4, 32-37. 15

Davis, A.J. (1989). Effects of soil compaction on damage to wheat seeds by three pest species of slug. Crop Protection, 8, 118-121. Dawkins, G., Luxton, M., & Bishop, C. (1985). Transmission of liquorice rot of carrots by slugs. Journal of Molluscan Studies, 51, 83-85. Desbiolles, J., Ballantyne, T., & Richards, M. (2003). Harvesting snail infested grain crops part I: Snail dislodge bar designs and performance. In G. Quick (Ed.) International Conference on Crop Harvesting and Processing (ASAE Publication Number 701P1103e). Louisville, Kentucky USA: American Society of Agricultural and Biological Engineers. Elliott, L.P. (1969). Certain bacteria, some of medical interest, associated with the slug Limax maximus. Journal of Invertebrate Pathology, 15, 306-312. Eshra, E.H. (2014). Toxicity of methomyl, copper hydroxide and urea fertilizer on some land snails. Annals of Agricultural Sciences, 59, 281-284. doi:http://dx.doi.org/10.1016/j.aoas.2014.11.017 Fabian, Y. et al., (2012). Diversity protects plant communities against generalist molluscan herbivores. Ecology and Evolution, 2(10), 2460-2473. doi:10.1002/ece3.359 Faull, B.W. (1987). Bovine fascioliasis in the Manawatu: Epidemiology and farmer awareness. New Zealand Veterinary Journal, 35, 72-74. Ferguson, C. M., Barratt, B. I. P., & Jones, P. A. (1988). Control of the grey field slug (Deroceras reticulatum (Muller)) by stock management prior to direct-drilled pasture establishment. The Journal of Agricultural Science, 111, 443-449. Fox, L., & Landis, B. J. (1973). Notes on the predaceous habits of the gray field slug, Deroceras laeve 1 2. Environmental Entomology, 2, 306-307. Gaitán‐Espitia, J. D. et al., (2012). Repeatability of energy metabolism and resistance to dehydration in the invasive slug Limax maximus. Invertebrate Biology, 131, 11- 18. Glen, D. et al., (2005). Assessing the risk of slug damage to oilseed rape and the need for control measures. IOBC wprs Bulletin, 28, 75-78. Gould, H. J. (1961). Observations on slug damage to winter wheat in East Anglia, 1957–1959. Plant Pathology, 10, 142-146. Gouyon, P.H., Fort, P.H., & Caraux, G. (1983). Selection of seedlings of Thymus vulgaris by grazing slugs. Journal of Ecology, 71, 299-306. Grewal, P.S. et al., (2003). Parasitism of molluscs by nematodes: Types of associations and evolutionary trends. Journal of Nematology, 35, 146-156. Guo, Y. H. et al., (2014). Investigation on the species distribution and infection status of host snails of Angiostrongylus cantonensis in Shanghai. Chinese Journal of Parasitology & Parasitic Diseases, 32, 455-458. Hammond, R. B. et al., (1999). Slugs in conservation tillage corn and soybeans in the eastern corn belt. Journal of Entomological Science, 34, 467-478. Herbert, D. G. (1997). The terrestrial slugs of KwaZulu-Natal: Diversity, biogeography and conservation (Mollusca: Pulmonata). Annals of the Natal Museum, 38, 197- 239. Herbert, D. G., & Sirgel, W.F. (2001). The recent introduction of two potentially pestiferous alien snails into South Africa and the outcomes of different pest 16

management practices: An eradication and a colonization: Research in action. South African Journal of Science, 97(7-8), 301-304. Hollingsworth, R. G., & Armstrong, J. W. (2003). Effectiveness of products containing metaldehyde, copper or extracts of yucca or neem for control of Zonitoides arboreus (Say), a snail pest of orchid roots in Hawaii. International Journal of Pest Management, 49, 115-122. Hollingsworth, R.G., Armstrong, J.W., & Campbell, E. (2002). Pest control: Caffeine as a repellent for slugs and snails. Nature, 417, 915-916. Hollingsworth, R. G., Follett, P. A., & Armstrong, J. W. (2003). Effects of irradiation on the reproductive ability of Zonitoides arboreus, a snail pest of orchid roots. Annals of Applied Biology, 143, 395-399. Hollingsworth, R.G., & Sewake, K.T. (2002). The orchid snail as a pest of orchids in Hawaii (Research Report No. MP-1). University of Hawaii at Manoa, Honolulu, Hawaii: College of Tropical Agriculture and Human Resources. Horsák, M., Dvořák, L., & Juřičková, L. (2004). Greenhouse gastropods of the Czech Republic: Current stage of research. Malakológiai Tájékoztató, 22, 141-147. Hussein, H. I. et al., (1994). Uscharin, the most potent molluscicidal compound tested against land snails. Journal of Chemical Ecology, 20, 135-140. Idris, A. B., & Abdullah, M. (1997). The phorid fly, Megaselia scalaris (Loew), as a candidate for managing molluscicide-resistant round snail, Bradybaena similaris (Ferussas). Resistant Pest Management, 9, 28-29. Ingram, J.W. (1931). Soil animals attacking sugar cane. Journal of Economic Entomology, 24, 866-869. Jeong, K. J. et al., (2012). Effective control of slug damage through tobacco extract and caffeine solution in combination with alcohol. Horticulture, Environment, and Biotechnology, 53, 123-128. doi:10.1007/s13580-012-0100-9 Kaya, H.K., & Mitani, D.R. (1999). Molluscicidal nematodes for the biological control of pest slugs (Slosson Report No. 2000-2001, 1-4). Keiser, A., Häberli, M., & Stamp, P. (2012). Quality deficiencies on potato (Solanum tuberosum L.) tubers caused by Rhizoctonia solani, wireworms (Agriotes spp.) and slugs (Deroceras reticulatum, Arion hortensis) in different farming systems. Field Crops Research, 128, 147-155. doi:10.1016/j.fcr.2012.01.004 Kim, J. R. et al., (2014). Diverse gastropod hosts of Angiostrongylus cantonensis, the rat lungworm, globally and with a focus on the Hawaiian Islands. PLoS One, 9(5), e94969. doi:10.1371/journal.pone.0094969 Koch, R., Jäckel, B., & Plate, H. P. (2000). Controlling pest slugs: New methods and the verification of their effects. Gesunde Pflanzen, 52, 1-10. Kozłowski, J. (2012). The significance of alien and invasive slug species for plant communities in agrocenoses. Journal of Plant Protection Research, 52, 67-76. Kralka, R.A., & Samuel, W.M. (1984). Experimental life cycle of Protostrongylus boughtoni (Nematoda: Metastrongyloidea), a lung worm of snowshoe hares, Lepus americanus. Canadian Journal of Zoology, 62, 473-479. Lahmar, S., Cabaret, J., & Cheniti, T. (1990). Land snails and periods at high risk for protostrongylid infection on a sheep-grazed pasture of northeast Tunisia. Veterinary Parasitology, 36, 105-115. 17

Lange Jr, W. H., & Macleod, G. F. (1941). Metaldehyde and calcium arsenate in slug and snail baits. Journal of Economic Entomology, 34, 321-322. Lima, W. D. S. et al., (2009). Occurrence of Fasciola hepatica (Linnaeus, 1758) infection in Brazilian cattle of Minas Gerais, Brazil. Revista Brasileira de Parasitologia Veterinária, 18, 27-30. doi:10.4322/rbpv.01802006 López, L. P., Romero, J., & Velásquez, L. E. (2008). Paramphistomidae isolation from dairy cows and its intermediate host (Lymnaea truncatula and Lymnaea columella) in a dairy farm in western Colombian high tropical region. Revista Colombiana de Ciencias Pecuarias, 21, 9-18. Lovett, A.L., & Black, A.B. (1920). The gray garden slug: with notes on allied forms. Station Bulletin, 170, 1-43. Maat‐Bleeker, F. et al., (1995). Vineyard snail allergy possibly induced by sensitization to house‐dust mite (Dermatophagoides pteronyssinus). Allergy, 50, 438-440. Madsen, H., & Frandsen, F. (1989). The spread of freshwater snails including those of medical and veterinary importance. Acta Tropica. 46, 139-146. Moran, S., Gotlib, Y., & Yaakov, B. (2004). Management of land snails in cut green ornamentals by copper hydroxide formulations. Crop Protection, 23, 647-650. doi:10.1016/j.cropro.2003.11.004 Morassutti, A. L. et al., (2014). Eosinophilic meningitis caused by Angiostrongylus cantonensis: An emergent disease in Brazil. Memórias do Instituto Oswaldo Cruz, 109, 399-407. doi:http://dx.doi.org/10.1590/0074-0276140023 Moreira, V. L. C. et al., (2013). Endemic angiostrongyliasis in the Brazilian Amazon: Natural parasitism of Angiostrongylus cantonensis in Rattus rattus and R. norvegicus, and sympatric giant African land snails, Achatina fulica. Acta Tropica, 125, 90-97. doi: https://doi.org/10.1016/j.actatropica.2012.10.001 Nash, M. A., & Hoffmann, A. A. (2012). Effective invertebrate pest management in dryland cropping in southern Australia: The challenge of marginality. Crop Protection, 42, 289-304. doi:http://dx.doi.org/10.1016/j.cropro.2012.06.017 Oliveira, A. P. et al., (2015). Angiostrongylus cantonensis infection in molluscs in the municipality of São Gonçalo, a metropolitan area of Rio de Janeiro, Brazil: Role of the invasive species Achatina fulica in parasite transmission dynamics. Memórias do Instituto Oswaldo Cruz, 110, 739-744. doi:http://dx.doi.org/10.1590/0074- 02760150106 Oliveira, C. D., Vasconcellos, M. C., & Pinheiro, J. (2008). The population density effects on the reproductive biology of the snail Bradybaena similaris (Férussac, 1821)(Mollusca, Gastropoda). Brazilian Journal of Biology, 68, 367-371. doi:http://dx.doi.org/10.1590/S1519-69842008000200018 Pinder, L. C. V. (1974). The ecology of slugs in potato crops, with special reference to the differential susceptibility of potato cultivars to slug damage. Journal of Applied Ecology, 11, 439-451. Pinto-Guillaume, E. M. (2002). Mollusks from the Villa of Livia at Prima Porta, Rome: The Swedish Garden Archaeological Project, 1996-1999. American Journal of Archaeology, 106, 37-58. Pinto-Guillaume, E. M. (2008). Molluscs from the Villa of Livia revisited. The Archaeo+ Malacology Group Newsletter, 11, 1-13. Pinto, H. A., Brant, S. V., & de Melo, A. L. (2014). Physa marmorata (Mollusca: Physidae) as a natural intermediate host of Trichobilharzia (Trematoda: 18

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