Jacob Schurkman1
Irma Tandingan De Ley
Rory Mc Donnell
Adler R. Dillman- 1Department of Nematology, University of California, Riverside, Riverside, CA, United States
- 2Department of Entomology, University of California, Riverside, Riverside, CA, United States
- 3Department of Crop and Soil Science, Oregon State University, Corvallis, OR, United States
Three species of Phasmarhabditis were recovered from 75 nurseries and garden centers in 28 counties in California during fall and winter 2012–2021. A total of 18 mollusk species were recovered, most of them invasive. Nematodes were identified by sequencing the D2-D3 expansion segments of the large subunit (LSU or 28S) rRNA. Based on these surveys, P. californica was the most widespread species (37 isolates, 53.6% recovery); followed by P. hermaphrodita (26 isolates; 37.7% recovery); P. papillosa and a closely related P. papillosa isolate (6 isolates; 8.7% recovery). Nematode isolates were mainly collected from four invasive slugs (Deroceras reticulatum, D. laeve, Arion hortensis agg, Ambigolimax valentianus) and snails (Oxychilus spp. and Discus spp.). Results suggest that P. californica and P. hermaphrodita share an ecological niche in Northern, Central, Coastal, and Southern California, north of Los Angeles County.
Introduction
The United States harbors a significant diversity of invasive species (Pimentel et al., 2005). They serve as a threat to the country’s natural biodiversity since the introduction of invasive species is one of the leading causes of global biodiversity decline (Mckinney and Lockwood, 1999; Clavero and Garcia-Berthou, 2005; Butchart et al., 2010; Gladstone and Bordeau, 2020). While the distribution of numerous invasives have been tracked, some taxonomic groups have been largely neglected, notably terrestrial gastropod species, many species of which are of agricultural and horticultural interest (Barker, 2002; Pyšek et al., 2008; Lowry et al., 2012; Gladstone and Bordeau, 2020).
Many invasive terrestrial gastropods in the United States are present on the west coast, especially in California, Oregon, Washington, and Hawaii, where most gastropod surveys have been conducted. For example, in California, it is estimated that there are approximately 279 species of terrestrial gastropods, 37 of which are invasive (Roth and Sadeghian, 2003). These gastropods were likely introduced via the horticultural trade when gastropods residing on plant products were delivered to western states (Cowie et al., 2008; Bergey et al., 2014).
Some of these introduced gastropods are considered among the most pestiferous slugs and snails. These species include Deroceras reticulatum (Müller 1774), Arion hortensis (Ferrusac 1819), and Cornu aspersum (Müller 1774) (Mc Donnell et al., 2009). For example, C. aspersum can reduce some California citrus fruit crop yields by 40–50% and occasionally up to 90–100% in years of high rainfall (Pappas and Carman, 1961; Sakovich, 2002). Terrestrial gastropods do not only cause direct physical damage to plants, but they can also spread disease. They have been found to serve as vectors for pathogens like Alternaria brassicicola (Saccardo 1880), and members of the family Peronosporaceae, and other plant-pathogenic fungi (Wester et al., 1964; Hasan and Vago, 1966; Turchetti and Chelazzi, 1984). Some gastropod species have also been found to harbor human pathogens. It has been postulated that some slugs and snails have been partially responsible for spinach and other salad crop recalls due to the discovery of Campylobacter spp. and Escherichia coli (Migula 1895) in the feces of sampled gastropods (Sproston et al., 2006; Raloff, 2007). Multiple terrestrial gastropods have also been found to carry Angiostrongylus cantonensis (Chen 1935), the causative agent for eosinophilic meningitis (Lindo et al., 2004; Teem et al., 2013; Iwanowicz et al., 2015).
Invasive terrestrial gastropods can also be detrimental to sensitive ecosystems. Multiple wetlands and marshes are threatened by invasive gastropod species because they thrive in these environments with a lack of natural predators (Cowie, 1998; Silliman et al., 2005). The invasive gastropods are capable of quick propagation and can reach large populations within a relatively short period of time. These large invasive populations result in a lack of resources for other endemic organisms which cannot compete with the invasives (Cowie, 1998; Silliman et al., 2005). Additionally, some native snail species have disappeared due to the introduction of the carnivorous snail Euglandia rosea (Ferrusac, 1821) (Cowie, 1998; Silliman et al., 2005). Horticultural and agricultural trade across the world brings danger to endemic organisms. To prevent invasive gastropods from being introduced through horticultural and agricultural trade, effective methods of pest control must be utilized.
The most common method of gastropod pest control is the use of molluscicides. One of the most widely used molluscicides is metaldehyde formulated as pelleted baits. These baits attract gastropods and upon ingestion are rapidly hydrolyzed to acetaldehyde, which causes the animal to produce excess mucus, dehydrate, and ultimately die (Triebskorn et al., 1998; Castle et al., 2017). However, these baits have variable efficacy due to a range of factors including weather conditions, different levels of attractiveness, and failure of a gastropod to consume enough bait (Crowell, 1967). Also, metaldehyde baits, along with most other molluscicides, are not targeted methods of pest control. Metaldehyde baits can harm a variety of different organisms including dogs, humans, and other organisms upon consumption (Castle et al., 2017). For example, ranking below chocolate ingestion, metaldehyde poisoning is the second most common cause of poisoning in canines (Cope et al., 2006). In mammals, metaldehyde is an irritant to the skin, eyes, mucous membranes, throat, and respiratory tract (Castle et al., 2017). The active ingredient may be leached at points of application and found in downstream river catchments at a level that can cause harm to non-target populations away from the application site (Gillman et al., 2012).
Parasitic nematodes within the genus Phasmarhabditis can be effective biological control agents against pestiferous gastropods with more targeted results compared to molluscicides (Rae et al., 2007). There are currently 16 nominal species of Phasmarhabditis worldwide (Wilson et al., 1993; Azzam, 2003; Huang et al., 2015; Nermut et al., 2016a,b; Tandingan De Ley et al., 2016; Ivanova and Spiridonov, 2017; Nermut et al., 2017; Pieterse et al., 2017; Ross et al., 2018; Pieterse, 2020; Zhang and Liu, 2020; Ivanova and Spiridonov, 2021). All species tested for their biological control potential have been shown to specifically target and kill gastropods, providing protection to a variety of crops (Wilson et al., 1993; Rae et al., 2007; Mc Donnell et al., 2018b,Mc Donnell et al., 2020; Nermut et al., 2020; Tandingan De Ley et al., 2020). Phasmarhabditis hermaphrodita is the most well-known and well-studied member of the genus. It is a facultative parasite that feeds on bacteria and can live saprobically or necromenically on gastropods or their feces (Tan and Grewal, 2001). P. hermaphrodita has seen success as a biological control agent across Europe as the commercially available product Nemaslug®. The species has undergone non-target testing with various species of earthworms, as well as native, non-pest European slugs and snails (Wilson et al., 2000; Grewal et al., 2003; Rae et al., 2005; Nardo et al., 2010). It did not cause mortality in any of the non-target species tested, suggesting that it is a safer alternative in Europe to traditional molluscicides, which are lethal to many organisms other than gastropods.
Until recently Phasmarhabditis had not been isolated within the United States. Therefore, due to agricultural policies, such as the National Environmental Policy Act (Montgomery, 2011), the commercialized Eurasian strain was not approved for use within the United States and as of 2021, it is still not commercially available in the United States. To find a viable biological control agent for gastropods in the United States, gastropod-nematode surveys within the country were performed to find a local species of nematode capable of causing mortality in slugs and snails. Three different surveys from 2000 to 2010 were performed to search for a gastropod biological control agent in the United States (Grewal et al., 2000; Kaya and Mitani, 2000; Ross et al., 2010). Most of the surveys looked for the presence of Phasmarhabditis, but they also searched for a variety of other nematode species found within gastropods and assessed their virulence. None of the surveys recovered any Phasmarhabditis species or other candidates for a gastropod biological control agent. However, over the past 8 years three species of Phasmarhabditis have been confirmed in California and one has been found in Oregon (Tandingan De Ley et al., 2014, 2016; Mc Donnell et al., 2018a). Thus, these local populations of Phasmarhabditis species should be the focus of future gastropod biological control research in the United States.
The first series of surveys which lead to the discovery of three Phasmarhabditis species in the United States in 2014 were conducted from 2012 to 2017 in California nurseries and garden centers. They were performed to search for potential biocontrol agents of invasive snails or slugs and to determine the distribution of parasitic nematodes including Phasmarhabditis. The species identified were P. hermaphrodita, P. papillosa, and a newly described species P. californica (Tandingan De Ley et al., 2014, 2016). As the next step, we evaluated the potential use of the local strains as biological control agents against invasive pestiferous gastropods in California (Tandingan De Ley et al., 2020).
Additional surveys were performed in 2018–2021 to determine the presence and distribution of gastropods and their associated Phasmarhabditis species, and to determine if the genus is widely established throughout the state. This series of extensive gastropod-nematode surveys is the first in the state of California. Such surveys have the potential to identify previously unknown nematode-gastropod relationships or identify new species of nematodes with biocontrol potential. These types of discoveries have been seen in other surveys performed across the globe (Ross et al., 2012; Tandingan De Ley et al., 2014; Mc Donnell et al., 2018a; Brophy et al., 2020). In this survey, we aimed to determine the presence and distribution of Phasmarhabditis nematodes and the diversity of gastropods in nurseries and garden centers throughout California.
Materials and Methods
Collection and Maintenance of Gastropods
We conducted gastropod surveys in 75 nurseries and garden centers during fall and winter months between 2012 and 2021 throughout California, covering at least 2 nurseries in each of the 28 counties surveyed. For ease of reference, the state was divided into three geographical areas: Northern California, Central California, and Southern California (Table 1 and Supplementary Figure 1). During the course of these surveys, 6,590 gastropod specimens were collected and brought back to the Insectary and Quarantine Facility and Departments of Entomology and Nematology at UC Riverside under CDFA Permits 2942 (2012–2018) and 3449 (2018–2022).
Table 1. Shows the California counties which were surveyed for gastropods and Phasmarhabditis.
Gastropods were collected from nurseries and garden centers for a total of 1 person-hour per visit. For example, if 2 people were sampling, each person’s collection time would be 30 min. The gastropods were removed and collected from underneath potted plants, foliage, or plant trays on the ground using clean metal spatulas, and then immediately stored in plastic containers lined with moistened paper towels and covered with punctured lids (to maintain aeration). These containers were placed inside a cooler and at the end of each sampling day, the collected gastropods were sorted into 540 ml deli containers lined with a moistened paper towel and contained organic carrot pieces for food. The gastropods were sorted phenotypically by species, and the deli containers were labeled accordingly, and kept in coolers. Gastropods from different nurseries were kept in separate deli containers. The deli containers were cleaned every other day and were provided with a new moist paper towel and fresh organic carrot pieces. After each survey trip was completed, the gastropods were examined again to ensure they were identified correctly. In order to accurately identify gastropods, we used the methods described in Mc Donnell et al. (2009). We also had years of experience identifying California gastropods based off of the guide and received verification of our identifications by collaborating with gastropod expert Rory McDonnell. Once the gastropods were sorted correctly in the lab, relevant information was recorded and summarized, tracking the dates of collection, as well as the life history of the gastropods (e.g., when they were killed, viewed for infection, or whether they were infected). The gastropods were kept in the lab at room temperature with continued fresh changes of paper towel and organic carrot discs every other day. Each gastropod that died was given an accession number and immediately transferred to plated 1.1% plain agar (1 L: 10 g agar, 900 ml H2O) in order to obtain nematodes in seed culture, as described in Tandingan De Ley et al. (2014). To encourage better growth of nematodes, we modified the method and used nematode growth medium [NGM; 1 L: 3 g NaCl, 20 g Agar, 2.5 g Peptone, 975 ml deionized H2O, 10 ml Uracil (2 g/L) were added to a liter of deionized water, autoclaved, and let cool, to which were added 25 ml filtered KPO4, 1 ml filtered MgSO4, 1 ml CaCl2, and 1 ml Cholesterol 5 mg/ml)]. As surveys progressed in 2018, and in the interest of time, speed, and laboratory space, we modified our nematode recovery method, following the protocol of Wilson et al. (2016), i.e., decapitating slugs in batches and immediately placing them on NGM. This shortened our gastropod maintenance period, likely with the same outcome because gastropods infected with Phasmarhabditis were assumed to have harbored the nematode at the collection site. However, if Phasmarhabditis was transmitted within the laboratory, it is likely that the transmission only occurred across conspecifics collected at the same collection site since these gastropods were kept in the same container.
The gastropod-nematode surveys conducted between 2012–2017 and 2018–2021 were analyzed separately due to differences of collection time and survey methods. During the 2018–2021 survey, non-Phasmarhabditis nematodes were identified from host gastropods whereas this was not done in the 2012–2017 survey as a search for biocontrol candidates was targeted at finding Phasmarhabditis spp. and determining their distribution in California nurseries and garden centers. Each of the surveys also covered different counties throughout California, where the 2012–2017 survey often covered more nurseries and garden centers within each county, sometimes surveying the same nurseries multiple times. The 2018–2021 survey only surveyed each nursery once, and mostly covered two nurseries or garden centers per county (Table 1 and Supplementary Figure 1). While the methodology of collecting gastropods remained the same throughout each of the surveys, the separate analyses of the two allows for the assessment of gastropod diversity and abundance across time and allows for results to be interpreted upon each method.
Nematode Recovery and Molecular Analyses
At least 5 individual nematodes that emerged from slug cadavers were picked from seed culture plates and grown on individual NGM plates, kept at 17°C. These plates of uniparental strains were labeled as single nematode isolations and were designated a unique accession number. Preliminary examination was done through a stereomicroscope, using morphological traits e.g., the presence of large phasmids and vulval body position, to identify suspected Phasmarhabditis. After suspects were identified, at least 2 individual nematodes from each single nematode isolation were prepared for PCR and DNA sequencing of the ribosomal RNA (D2-D3 domains of the large subunit or LSU), as described in Tandingan De Ley et al. (2014). When necessary, the small subunit (SSU) was also sequenced following the same protocols. Contigs were assembled and compared by BLAST with published sequences in GenBank using CodonCode Aligner (CodonCode Corp., 58 Beech Street, Dedham, MA, United States) to verify their identity or determine if sequences were unique.
Results
Gastropod Survey
A total of 18 different gastropod species were recovered from all surveys. Sixteen of the 18 species recovered were invasive species, representing 99.8% of the total individuals collected (Figure 1). These include: Arion hortensis (Ferrusac 1819), Arion distinctus (Mabille 1869), Arion rufus (Linnaeus 1758), Arion subfuscus (Draparnaud 1805), Cornu aspersum (Müller 1774), Deroceras laeve (Müller 1774), Deroceras reticulatum (Müller 1774), Deroceras invadens (Reise et al., 2011), Discus spp., Ambigolimax valentianus (Ferussac 1821), Sucinnea spp., Oxychilus spp., Milax gagates (Lessona and Pollonera 1882), Boettgerilla pallens (Simroth 1912), Cochlicopa lubrica (Müller 1774), Rumina decollata (Linnaeus 1758), Prophysaon andersoni (Cockerell 1890), and Limacus flavus (Linnaeus 1758) (Figures 1–3). Both surveys from 2012 to 2017 and 2018 to 2021 recovered far more slug species (12) than snail species (6) (Figure 1). The two surveys, although completed over different years and with some differences between the counties visited and the nematodes which were chosen to be identified, were approximately congruent with a few notable disparities. The earlier survey obtained a greater number of D. reticulatum specimens in Southern California nurseries compared to the later survey (28.12% vs. 6.17%). Discus spp. were recorded during the later survey but were not collected during 2012–2017 (Figure 1). Also, the earlier gastropod surveys yielded a larger abundance of D. invadens across all areas of California. Each of the surveys also demonstrated that A. valentianus was the predominant gastropod species in nurseries. However, the second most common species collected during the 2012–2017 survey was D. reticulatum, while D. laeve was the second most common species during the 2018–2021 campaign. In general, more gastropod individuals were found at nurseries in Northern California than in other areas of California and fewer gastropod species were recovered in Southern California, indicating a possible decrease in gastropod abundance in a southward direction throughout the state (Figures 1–3).
Figure 1. Percent recovery of terrestrial gastropods from different geographical regions of California during the 2012–2017 and 2018–2021 surveys. Surveys were performed during late fall or winter. Survey methods included 1 human hour searching for gastropods throughout each nursery. Collected gastropods were sorted by species and were taken back to the laboratory for later verification of species identity.
Figure 2. Abundance and species richness of terrestrial gastropods collected in each California county surveyed between 2018 and 2021. Surveys were performed during late fall or winter. Survey methods included 1 human hour searching for gastropods throughout each nursery. Collected gastropods were sorted by species and were taken back to the laboratory for later verification of species identity.
Figure 3. Abundance and species richness of terrestrial gastropods collected in nurseries in each California county surveyed between 2012 and 2017. Surveys were performed during late fall or winter. Survey methods included 1 human hour searching for gastropods throughout each nursery. Collected gastropods were organized by species and were taken back to the laboratory for later verification of species identity.
Phasmarhabditis Survey
A total of 69 Phasmarhabditis isolates were collected from all surveys. Phasmarhabditis californica was the most widespread species (37 isolates, 53.6% of all Phasmarhabditis recovered); followed by P. hermaphrodita (26 isolates; 37.7% recovery); P. papillosa and a P. papillosa closely related isolate (6 isolates; 8.7% recovery) (Table 2). The sequence of the D2-D3 expansion segment of 28S rDNA of this isolate was uploaded to Genbank (accession ID OL455007). Isolates were recovered from 5 invasive slug species: D. reticulatum (54%), D. laeve (25%), A. hortensis agg (5.7%), A. valentianus (8.7%) and two snails, Oxychilus spp. (5.8%) and Discus spp. (1.4%) (Table 2). Interestingly, isolates of Phasmarhabditis were mostly collected from D. reticulatum (53.6%), which was not the most abundant gastropod species found throughout the state. Only 8.7% of the isolates were collected from the most common gastropod, A. valentianus (Figures 1–3). However, about 78% of all isolates were collected from gastropod species within the genus Deroceras (Table 2).
Table 2. Phasmarhabditis species including hosts, sampling locations and morphological/genetic characterization from surveys performed between 2012 and 2021.
Phasmarhabditis isolates were collected and identified from Northern, Central, and Southern California. They were found in about 46% of all California counties surveyed. Results suggest that P. californica and P. hermaphrodita share an ecological niche throughout Northern CA and Central CA, whereas P. papillosa is mostly present by itself in Southern California. However, an unidentified close relative of P. papillosa was found in Monterey County (Central California) (Figure 4). Other nematode species were also recovered and identified from the surveys performed between 2018 and 2021. However, the non-Phasmarhabditis isolates are not representative of nematode diversity throughout California nurseries. This is because Phasmarhabditis was targeted, and only a select few nematodes from gastropod cadavers or seed cultures which did not morphologically resemble Phasmarhabditis were identified using 28S D2-D3 rDNA sequencing. Criteria for nematodes to be selected when they did not resemble Phasmarhabditis were not completely randomized. Nematodes which were not commonly observed (i.e. not a species of Caenorhabditis) were always selected for identification. Across locations, the most abundant non-Phasmarhabditis species identified was Caenorhabditis elegans, followed by C. remanei and Rhabditophanes spp. (Table 3). Other nematode species which are not typically considered to be associated with gastropods were also discovered. For example, Cruzia americana, a known opossum parasite, was discovered in a collected gastropod host (Li, 2019; Table 3). Some gastropod species that did not yield any associated Phasmarhabditis were found to have a variety of other associated nematode species (Table 4). A. valentianus had the most diverse nematode associations that included A. dentiferum, Bursilla spp., C. elegans, C. remanei, C. tonkinensis, and Rhabditophanes spp. (Table 4). However, this may well be the result of the larger sample size we obtained of A. valentianus compared to the other gastropod species. All nematode species identified can be found in Supplementary Table 1, as well as the host species they were discovered in. The locations in which all non-Phasmarhabditis nematodes were identified can be found in Supplementary Figure 2.
Figure 4. Phasmarhabditis species recovery and distribution among 28 California counties surveyed between 2012 and 2021. Species were identified by sequencing the D2–D3 expansion segments of the large subunit (LSU or 28S) ribosomal RNA and contigs compared by BLAST with published sequences in GenBank. 1Isolate closely related to Phasmarhabditis papillosa.
Table 3. Shows all recovered nematodes other than Phasmarhabditis during the California gastropod survey between 2018 and 2021.
Table 4. Shows the species of nematodes (other than Phasmarhabditis) present in the cadavers of host gastropods found throughout gastropod surveys performed between 2018 and 2021.
Discussion
This was the first extensive gastropod and nematode survey performed throughout California. The surveys from 2012 to 2017 and 2018 to 2020 combined covered a total of 28 counties and resulted in the collection of 18 different gastropod species from 6,590 specimens. A total of 69 Phasmarhabditis isolates were collected. The most common gastropod species recovered was A. valentianus. According to this survey, invasive slug and snail species are more common than native gastropod species in California nurseries. Gastropod abundance decreased as we moved southward through California (Figures 1–3). This could be due to the desert and chapparal climates which occur in most of the southern sections of California, while Northern California climates include more precipitation. Slugs are prone to desiccation; therefore, lower survival rates in these climate conditions are plausible (Sternberg, 2000).
Phasmarhabditis species were found throughout all three geographic areas of California (Northern, Central, and Southern). Three species were identified throughout the state, P. hermaphrodita, P. californica, and P. papillosa. Also, one isolate was recovered in Monterey County which seems to be a close relative to or a variant of P. papillosa (Figure 4); with morphological characteristics diagnostic to the species. However, based on genetic analyses of the D2-D3 expansion segments of rRNA, it varies by 2 transitions, 1 ambiguity, 1 transversion, and 2 insertions/deletions (Thymine instead of Cytosine in nucleotide positions 46 and 67; C/T instead of Cytosine in position 140, Adenine instead of a Cytosine in position 261, and 2 indels on positions 346 and 347, respectively). Surveys in Oregon showed the same 3 Phasmarhabditis species, and interestingly, P. hermaphrodita was recovered from a slug in a Brassica field in Salem, OR, suggesting it may also be present in the wider agricultural environment (Howe et al., 2020). In California, our surveys focused solely on nurseries and garden centers because (1) horticulture is one of the most valuable agricultural industries in the state (2) slugs and snails are major pests in the industry and (3) transportation of plants to and from retail nurseries presumably causes gastropods to be moved around the state over great distances than would otherwise be possible. The nurseries themselves could therefore be focal locations for exposure of invasive slug and snail species to a greater diversity of gastropod associated nematodes than is likely to occur in production fields or greenhouses. Based on the Oregon finding, it is likely that these gastropod-infecting nematodes may have also found their way as hitchhikers into agricultural and horticultural fields and backyard gardens in California. However, that has yet to be determined as these production areas were not covered in our surveys.
Additionally, recent studies based on mitochondrial DNA COI gene phylogenies, showed that Phasmarhabditis hermaphrodita U.S. isolates and strains (including isolates from the CA 2012 to 2017 survey and OR surveys) had haplotypes that were nearly identical to P. hermaphrodita collected in the United Kingdom for commercialization of Nemaslug®. They were placed together in an intraspecific monophyletic clade with the Nemaslug® strain (Howe et al., 2020). We can hypothesize that P. hermaphrodita found in the United States likely came from areas where Nemaslug® was used in Europe. Invasion of California and Oregon probably came about from agricultural trade with interstate movement of infected soil and/or slugs/snails. The invasive slugs from Europe and some of the specimens found in this survey likely came with these same nematodes of near-identical haplotypes. It is equally likely that the nematodes came to California on slugs many years ago before the commercialization of Nemaslug®, and they have stayed in the region by infecting Deroceras slugs and other suitable host pest slugs which are now established in California. In the study by Howe et al. (2020), available P. californica strains at that time were also studied. As with P. hermaphrodita, all P. californica haplotypes (CA, United States; United Kingdom; and New Zealand) belonged to one single, strongly supported clade. Interestingly, P. californica shares the same geographical niche and host gastropod species as P. hermaphrodita from Northern to Southern California. However, P. papillosa seems to only inhabit areas of Southern California (Figure 4).
Some gastropod species were more commonly infected with Phasmarhabditis than others. The gastropod host A. valentianus, which was the most frequently found gastropod, only accounted for about 8.5% of the Phasmarhabditis isolates collected. A. valentianus may have a more developed immune response to parasitic nematodes compared to other slugs, however, this has yet to be determined. The majority of Phasmarhabditis nematodes collected from the survey were collected from D. reticulatum. The host D. reticulatum accounted for about 55% of all Phasmarhabditis nematodes collected. In total, the genus Deroceras accounted for about 74.1% of the identified Phasmarhabditis nematodes (Table 2). D. reticulatum is a common slug pest across Europe, especially in areas near Ireland and the United Kingdom where Nemaslug® was originally discovered (Kerney, 1999). This serves as additional evidence that an infected invasive species of gastropod from Europe likely brought Phasmarhabditis to the United States where the relationship between the gastropod hosts remained.
Multiple gastropods collected throughout the survey were infected and/or associated with a diverse array of nematodes (other than Phasmarhabditis) (Supplementary Table 1 and Tables 3, 4). C. elegans and C. remanei were the most prominent nematodes found within gastropod hosts. These nematodes are not uncommon in gastropods, and though the interaction between C. remanei and gastropods has not been thoroughly explored, C. elegans is thought to have a phoretic association with gastropods (Caswell-Chen et al., 2005; Ross et al., 2012; Petersen et al., 2015; Rae, 2017; Sudhaus, 2018). C. elegans is also known to have phoretic associations with some species of earthworms and arthropods (Kiontke and Sudhause, 2006; Brophy et al., 2020). Other interesting nematode species were also discovered during the California surveys including Cosmocercoides tonkinensis, which is not commonly associated with gastropod hosts (Supplementary Table 1 and Tables 3, 4; Sudhaus, 2018). C. tonkinensis has only been described in reptiles (Tran et al., 2015). However, for another member of the genus, Cosmocercoides dukae, mollusks are a known host (Anderson, 1960). A survey done in 2014 which identified P. hermaphrodita in California also recovered species other than Phasmarhabditis within gastropod hosts. Some of these species included Alloionema appendiculatum (a common parasite of slugs), C. elegans, C. briggsae, a new species A. similis, and species of Oscheius (Tandingan De Ley et al., 2014; Holovachov et al., 2016). Our non-Phasmarhabditis results share in some of these genus recoveries, except for Alloionema spp. (Table 3). The absence of this genus throughout both surveys spanning from 2012 to 2021 is unexpected and intriguing since it was discovered in past surveys in similar locations (Laznik et al., 2010).
The occurrence of P. hermaphrodita and other species of the genus in North America has regulatory implications for potential biocontrol strategies against non-native slug and snail species that are pests of agriculture on this continent. Since the nematode occurs throughout the state, its use in a similar manner to Nemaslug® may be a feasible option. Its use could potentially save the California specialty crop industry about 64 million dollars, and is therefore worth exploring as a biological control option (Supplementary Table 2). The recovery of Phasmarhabditis from local plant nurseries and garden centers throughout California was not entirely surprising as these are considered transport hubs for non-native gastropod species (Bergey et al., 2014). It is not known if Phasmarhabditis exists in the natural environment throughout California where horticultural practices do not take place. In order to better understand the presence of Phasmarhabditis in the state, further surveillance is required in horticultural and agricultural field production areas, as well as natural ecosystems. Also, additional non-target and target host experiments with Phasmarhabditis are required to have a deeper understanding of how these potential biological control agents will affect the local ecosystem where they would likely be introduced. Additionally, host experimentation should be performed in mesocosms or other field-like conditions to determine efficacy.
Data Availability Statement
The datasets presented in this study can be found in online repositories. The names of the repository/repositories and accession number(s) can be found below: Mendeley Data, V2, doi: 10.17632/dwxh3bmmcb..
Author Contributions
JS carried out nematode studies and identification, conceptualized, planned, and carried out the survey, identified gastropods, maintained gastropods and nematodes and created records for all specimens, performed nematode genetic identification work, and wrote and designed the manuscript. ITD conceptualized, planned, carried out, and supervised the nematode genetic studies and identification, secured fundings, performed the survey for gastropods and nematodes throughout California, and assisted in the writing and development of the manuscript. KA assisted in genetic identification and maintenance of gastropods and nematodes. TP provided guidance and secured funding throughout early stages of the project. RM performed survey for all gastropods throughout California between 2012 and 2017, assisted in gastropod identification during the surveys between 2018 and 2020, secured funding, and assisted in the development of the manuscript. AD secured funding, managed the project, and assisted in the development of the manuscript. All authors contributed to the article and approved the submitted version.
Funding
This research was made possible through grants from the California Department of Food and Agriculture (CDFA) Specialty Crop Block Grant Programs 2012-2015 SCB12059 and 2015-2018 SCB15053, the United States Department of Agriculture Specialty Crop Multi-state Program (USDA-SCMP), in partnership with CDFA (2018-2022 grant #12509488), and generous gift from the CANERS Foundation through California Association of Nurseries and Garden Centers (GANGC) as well as the Plant California Alliance) (2019-2022).
Conflict of Interest
ITD, RM, and TP, declare that they are co-inventors on a patent entitled Mollusk-killing Biopesticide (WO2017059342A1).
The remaining authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.
Publisher’s Note
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Acknowledgments
We are grateful to Paul De Ley for loan of his equipment and his reading and editing of the manuscript, Robin Veasey and Sarinah Simons for assistance with gastropod colony maintenance; undergraduate laboratory assistants Sandy Lopez, Felecia Gu, Salomon Alvarado, Jasmine Stamps, Kamren Manalo, and Maral Ansari, for assistance in nematode culture maintenance and identification; and the grants they (Sandy Lopez, Salomon Alvarado, and Jasmine Stamps) received from California Alliance for Minority Participation (CAMP) Program.
Supplementary Material
The Supplementary Material for this article can be found online at: https://www.frontiersin.org/articles/10.3389/fpls.2022.856863/full#supplementary-material
Supplementary Figure 1 | California counties (28) surveyed for terrestrial gastropods and gastropod-associated nematodes from 2012 to 2021.
Supplementary Figure 2 | Locations which non-Phasmarhabditis were found throughout the gastropod surveys conducted between 2018 and 2021.
References
Anderson, R. C. (1960). On the Development and Transmission of Cosmocercoides Dukae of Terrestrial Molluscs in Ontario. Can. J. Zool. 38, 801–825. doi: 10.1139/z60-084
Azzam, K. M. (2003). Description of the nematode Phasmarhabditis tawfiki n. sp. isolated from Egyptian terrestrial snails and slugs. Egyptian German Soc. Zool. 42, 79–88.
Bergey, E. A., Figueroa, L. L., Mather, C. M., Martin, R. J., Ray, E. J., Kurien, J. T., et al. (2014). Trading in snails: plant nurseries as transport hubs for non-native species. Biol. Invasions 16, 1441–1451. doi: 10.1007/s10530-013-0581-1
Brophy, T., McDonnell, R. J., Howe, D. K., Denver, D. R., Ross, J. L., and Luong, L. T. (2020). Nematodes associated with terrestrial slugs in the Edmonton region of Alberta, Canada. J.Helminthol. 94:e200. doi: 10.1093/nar/gkx1095
Butchart, S. H., Walpole, M., Collen, B., Van Strien, A., Scharlemann, J. P., Almond, R. E., et al. (2010). Global Biodiversity: Indicators of Recent Declines Linked references are available on JSTOR for this article: Recent Declines Global Biodiversity?: Indicators of. Science 328, 1164–1168.
Castle, G. D., Mills, G. A., Gravell, A., Jones, L., Townsend, I., Cameron, D. G., et al. (2017). Review of the molluscicide metaldehyde in the environment. Environ. Sci. 3, 415–428. doi: 10.1039/c7ew00039a
Caswell-Chen, E. P., Chen, J., Lewis, E. E., Douhan, G. W., Nadler, S. A., and Carey, J. R. (2005). Revising the standard wisdom of C. elegans natural history: ecology of longevity. Sci. Aging Knowl. Environ. 40:30. doi: 10.1126/sageke.2005.40.pe30
Clavero, M., and Garcia-Berthou, E. (2005). Invasive species are a leading cause of animal extinctions. Trends Ecol. Evol. 20:110. doi: 10.1016/j.tree.2005.01.003
Cope, R. B., White, K. S., More, E., Holmes, K., Nair, A., Chauvin, P., et al. (2006). Exposure-to-treatment interval and clinical severity in canine poisoning: A retrospective analysis at a Portland Veterinary Emergency Center. J. Vet. Pharmacol. Therapeut. 29, 233–236. doi: 10.1111/j.1365-2885.2006.00730.x
Cowie, R. H. (1998). Patterns of introduction of non-indigenous non-marine snails and slugs in the Hawaiian Islands. Biodivers. Conserv. 7, 349–368. doi: 10.1023/A:1008881712635
Cowie, R. H., Hayes, K. A., Tran, C. T., and Meyer, W. M. III (2008). The horticultural industry as a vector of alien snails and slugs: widespread invasions in Hawaii. Int. J. Pest Manage. 54, 267–276. doi: 10.1080/09670870802403986
Crowell, H. H. (1967). Slug and Snail Control with Experimental Poison Baits. J. Econom. Entomol. 60, 1048–1050. doi: 10.1093/jee/60.4.1048
Gillman, S., Brown, P., Burgess, D., Bickle, B., Zyndul, A., and Chapman, C. (2012). “Pesticides in the river Ugie-developing a catchment management approach to protect a drinking water source,” in The Dundee Conference - Crop Protection in Northern BritainAt: Dundee, (Netherland: Elsevier), 31–36.
Gladstone, N. S., and Bordeau, T. A. (2020). Spatiotemporal patterns of non-native terrestrial gastropods in the contiguous United States. NeoBiota 152, 133–152. doi: 10.3897/neobiota.57.52195
Grewal, S. K., Grewal, P. S., Brown, I., Tan, L., Hammond, R. B., and Gaugler, R. (2000). “First North American survey for the recovery of nematodes associated with mollusks,” in Proceedings of the Society of Nematologists 39th Annual Meeting, (Quebec City: Quebec).
Grewal, S. K., Grewal, P. S., and Hammond, R. B. (2003). Susceptibility of North American Native and Non-native Slugs (Mollusca: Gastropoda) to Phasmarhabditis hermaphrodita (Nematoda: Rhabditidae). Biocont. Sci. Technol. 13, 119–125. doi: 10.1080/0958315021000054449
Hasan, S., and Vago, C. (1966). Transmission of Alternaria brassicicola by slugs. Plant Dis. Rep. 50, 764–767.
Holovachov, O., Bostrom, S., Tandingan De Ley, I., McDonnell, R. J., Alvarado, S., et al. (2016). Alloionema similis n. sp., a genetically divergent sibling species of A. appendiculatum Schneider, 1859 (Rhabditida: Alloionematidae) from invasive slugs in California, USA. Syst. Parasitol. 93, 877–898. doi: 10.1007/s11230-016-9668-2
Howe, D. K., Ha, A. D., Colton, A., Tandingan De Ley, I., Rae, R. G., et al. (2020). Phylogenetic evidence for the invasion of a commercialized European Phasmarhabditis hermaphrodita lineage into North America and New Zealand. PLoS One 15:e237249. doi: 10.1371/journal.pone.0237249
Huang, R. E., Ye, W., Ren, X., and Zhao, Z. (2015). Morphological and molecular characterization of Phasmarhabditis huizhouensis sp. nov. (Nematoda: Rhabditidae), a new rhabditid nematode from South China. PLoS One 10:e144386. doi: 10.1371/journal.pone.0144386
Ivanova, E. S., and Spiridonov, S. E. (2017). Phasmarhabditis meridionalis sp. n. (Nematoda: Rhabditidae) from a land snail Quantula striata (Gastropoda: Dyakiidae) from southern Vietnam. J. Nematol. 25, 129–140.
Ivanova, E. S., and Spiridonov, S. E. (2021). Phasmarhabditis quinamensis sp. n. (Nematoda: Rhabditidae) from tropical terrestrial gastropods in southern Vietnam. Nematology 1, 1–15.
Iwanowicz, D. D., Sanders, L. R., Schill, W. B., Xayavong, M. V., da Silva, A. J., Qvarnstrom, Y., et al. (2015). Spread of the rat lungworm (Angiostrongylus cantonensis) in giant african land snails (Lissachatina fulica) in Florida, USA. J. Wildl. Dis. 51, 749–753. doi: 10.7589/2014-06-160
Kaya, H. K., and Mitani, D. R. (2000). Molluscicidal Nematodes for Biological Control of Pest Slugs. Slosson Report 1999–2000 1–4.
Laznik, Ž, Ross, J. L., and Trdan, S. (2010). Massive occurrence and identification of the nematode Alloionema appendiculatum Schneider (Rhabditida: Alloionematidae) found in Arionidae slugs in Slovenia. Acta Agri. Slovenica 95, 43–49.
Li, L. (2019). Redescription of Cruzia americana Maplestone, (1930) (Nematoda: Kathlaniidae) a parasite of Didelphis virginiana (Kerr) (Mammalia: Didelphidae) in the USA. Syst. Parasitol. 96, 433–440. doi: 10.1007/s11230-019-09853-z
Lindo, J. F., Escoffery, C. T., Reid, B., Codrington, G., Cunningham-Myrie, C., and Eberhard, M. L. (2004). Fatal autochthonous eosinophilic meningitis in a Jamaican child caused by Angiostrongylus cantonensis. Am. J. Trop. Med. Hygiene 70, 425–428. doi: 10.4269/ajtmh.2004.70.425
Lowry, E., Rollinson, E. J., Laybourn, A. J., Scott, T. E., Aiello-Lammens, M. E., Gray, S. M., et al. (2012). Biological invasions: a field synopsis, systematic review, and database of the literature. Ecol. Evol. 13, 182–196. doi: 10.1002/ece3.431
Mc Donnell, R. J., Tandingan De Ley, I., and Paine, T. D. (2018b). Susceptibility of neonate Lissachatina fulica (Achatinidae: Mollusca) to a U.S. strain of the nematode Phasmarhabditis hermaphrodita (Rhabditidae: Nematoda). Biocont. Sci. Technol. 28, 1091–1095. doi: 10.1080/09583157.2018.1514586
Mc Donnell, R. J., Colton, A. J., Howe, D. K., and Denver, D. R. (2020). Lethality of four species of Phasmarhabditis (Nematoda: Rhabditidae) to the invasive slug, Deroceras reticulatum (Gastropoda: Agriolimacidae) in laboratory infectivity trials. Biological Control [preprint] doi: 10.1016/j.biocontrol.2020.104349
Mc Donnell, R. J., Lutz, M. S., Howe, D. K., and Denver, D. R. (2018a). First report of the gastropod-killing nematode, Phasmarhabditis hermaphrodita, in Oregon, USA. J. Nematol. 50:77. doi: 10.21307/jofnem-2018-014
Mc Donnell, R. J., Paine, T. D., and Gormally, M. J. (2009). Slugs: A Guide to the Invasive and Native Fauna of California. California: UCANR Publications.
Mckinney, M. L., and Lockwood, J. L. (1999). Biotic homogenization: a few winners replacing many losers in the next mass extinction. Trends Ecol. Evol. 14, 450–453. doi: 10.1016/s0169-5347(99)01679-1
Montgomery, M. E. (2011). “Understanding Federal Regulations as Guidelines for Classical Biological Control Programs,” in Implementation and Status of Biological Control of the Hemlock Wooly Adelgid, eds B. Onken and R. Reardon (Morgantown, WV: U.S. Department of Agriculture), 25–40.
Nardo, E. A. B., Sindermann, A. B., Grewal, S. K., and Grewal, P. S. (2010). Non-Susceptibility of Earthworm Eisenia fetida to the Rhabditid Nematode Phasmarhabditis hermaphrodita, a Biocontrol Agent of Slugs. Biol. Sci. Technol. 14, 93–98. doi: 10.1080/0958315031000151693
Nermut, J., Holley, M., and Puza, V. (2020). Phasmarhabditis hermaphrodita is not the only slug killing nematode. Microbial Nematode Control Invertebrate Pests 150, 152–156.
Nermut, J., Puza, V., Mekete, T., and Mracek, Z. (2016a). Phasmarhabditis bonaquaense n. sp. (Nematoda: Rhabditidae), a new slug-parasitic nematode from the Czech Republic. Zootaxa 4179, 530–546. doi: 10.11646/zootaxa.4179.3.8
Nermut, J., Puza, V., and Mracek, Z. (2016b). Phasmarhabditis apuliae n. sp. (Nematoda: Rhabditidae), a new rhabditid nematode form milacid slugs. Nematology 18, 1095–1112. doi: 10.1163/15685411-00003017
Nermut, J., Puza, V., Mekete, T., and Mracek, Z. (2017). Phasmarhabditis bohemica n. sp. (Nematoda: Rhabditidae), a slug-parasitic nematode from the Czech Republic. Nematology 19, 93–107.
Pappas, J. L., and Carman, G. E. (1961). Control of European Brown Snail in Citrus Groves in Southern California with Guthion and Metaldehyde Sprays. J. Econ. Entomol. 54, 152–156. doi: 10.1093/jee/54.1.152
Petersen, C., Hermann, R. J., Barg, M. C., Schalkowski, R., Dirksen, P., Barbosa, C., et al. (2015). Travelling at a slug’s pace: Possible invertebrate vectors of Caenorhabditis nematodes. BMC Ecol. 15:19. doi: 10.1186/s12898-015-0050-z
Pieterse, A. (2020). Phasmarhabditis kenyaensis n. sp. (Nematoda: Rhabditidae) from the slug, Polytoxon robustum, in Kenya. Nematology 23, 229–245. doi: 10.1163/15685411-bja10040
Pieterse, A., Malan, A. P., and Ross, J. L. (2017). Nematodes that associate with terrestrial molluscs as definitive hosts, including Phasmarhabditis hermaphrodita (Rhabditida: Rhabditidae) and its development as a biological molluscicide. J. Helminthol. 91, 517–527. doi: 10.1017/S0022149X16000572
Pimentel, D., Zuniga, R., and Morrison, D. (2005). Update on the environmental and economic costs associated with alien-invasive species in the United States. Ecol. Econ. 52, 273–288. doi: 10.1016/j.ecolecon.2004.10.002
Pyšek, P., Richardson, D. M., Pergl, J., Jarosik, V., Sixtova, Z., and Weber, E. (2008). Geographical and taxonomic biases in invasion ecology. Trends Ecol. Evol. 23, 237–244. doi: 10.1016/j.tree.2008.02.002
Rae, R. (2017). The gastropod shell has been co-opted to kill parasitic nematodes. Sci. Rep. 7:4745. doi: 10.1038/s41598-017-04695-5
Rae, R., Verdun, C., Grewal, P. S., Robertson, J. F., and Wilson, M. J. (2007). Biological control of terrestrial molluscs using Phasmarhabditis hermaphrodita-progress and prospects. Pest Manage. Sci. 63, 1153–1164. doi: 10.1002/ps.1424
Rae, R. G., Robertson, J., and Wilson, M. J. (2005). Susceptibility of indigenous UK earthworms and an invasive pest flatworm to the slug parasitic nematode Phasmarhabditis hermaphrodita. Biocontrol Sci. Technol. 15, 623–626. doi: 10.1080/09583150500086870
Raloff, J. (2007). Lettuce liability. Programs to keep salad germ-free, raise wildlife, and conservation concerns. Sci. News 172, 362–364. doi: 10.1002/scin.2007.5591722310
Ross, J., Pieterse, A., Malan, A. P., and Ivanova, E. S. (2018). Phasmarhabditis safricana n. sp. (Nematodea: Rhabditidae), a parasite of the slug Deroceras reticulatum from South Africa. Zootaxa 4420, 391–404. doi: 10.11646/zootaxa.4420.3.5
Ross, J. L., Ivanova, E. S., Severns, P. M., and Wilson, M. J. (2010). The role of parasite release in invasion of the USA by European slugs. Biol. Invasions 12, 603–610. doi: 10.1007/s10530-009-9467-7
Ross, J. L., Ivanova, E. S., Sirgel, W. F., Malan, A. P., and Wilson, M. J. (2012). Diversity and distribution of nematodes associated with terrestrial slugs in the Western Cape Province of South Africa. J. Helminthol. 86, 215–221. doi: 10.1017/S0022149X11000277
Roth, B., and Sadeghian, P. S. (2003). Checklist of the land snails and slugs of California, Santa Barbara: Santa Barbara Museum of Natural History, Contributions in Science.
Sakovich, N. J. (2002). “Integrated Management of Cantareus aspersus (Müller) (Helicidae) as a Pest of Citrus in California,” in G. M. Barker ed. Molluscs as Crop Pests. (Wallingford: CABI Publishing), 353. doi: 10.1079/9780851993201.0353
Silliman, B. R., Van De Koppel, J., Bertness, M. D., Stanton, L. E., and Mendelssohn, I. A. (2005). Drought, Snails, and Large-Scale Die-off of Southern U.S. Salt Marshes. Science 310, 1803–1806. doi: 10.1126/science.1118229
Sproston, E. L., Macrae, M., Ogden, I. D., Wilson, M. J., and Strachan, N. J. (2006). Slugs: Potential novel vectors of Escherichia coli O157. Appl. Environ. Microbiol. 72, 144–149. doi: 10.1128/AEM.72.1.144-149.2006
Sternberg, M. (2000). Terrestrial gastropods and experimental climate change: A field study in a calcareous grassland. Ecol. Res. 15, 73–81. doi: 10.1046/j.1440-1703.2000.00327.x
Sudhaus, W. (2018). Dispersion of nematodes (Rhabditida) in the guts of slugs and snails. Soil Organ. 90, 101–114. doi: 10.25674/4jp6-0v30
Tan, L., and Grewal, P. S. (2001). Infection behavior of the rhabditid nematode Phasmarhabditis hermaphrodita to the grey garden slug Deroceras reticulatum. J. Parasitol. 87, 1349–1354. doi: 10.1645/0022-3395(2001)087[1349:IBOTRN]2.0.CO;2
Tandingan De Ley, I., Holovachov, O., McDonnell, R. J., Bert, W., Paine, T. D., et al. (2016). Description of Phasmarhabditis californica n. sp. and first report of P. papillosa (Nematoda: Rhabditidae) from invasive slugs in the USA. Nematology 18, 175–193.
Tandingan De Ley, I., McDonnell, R. D., Lopez, S., Paine, T. D., and De Ley, P. (2014). Phasmarhabditis hermaphrodita (Nematoda: Rhabditidae), a potential biocontrol agent isolated for the first time from invasive slugs in North America. Nematology 16, 1129–1138. doi: 10.1163/15685411-00002838
Tandingan De Ley, I., Schurkman, J., Wilen, C., and Dillman, A. R. (2020). Mortality of the invasive white garden snail Theba pisana exposed to three U.S. isolates of Phasmarhabditis spp (P. hermaphrodita, P. californica, and P. papillosa). PLoS One 15:e228244. doi: 10.1371/journal.pone.0228244
Teem, J. L., Qvarnstrom, Y., Bishop, H. S., da Silva, A. J., Carter, J., White-Mclean, J., et al. (2013). The occurrence of the rat lungworm, Angiostrongylus cantonensis, in nonindigenous snails in the Gulf of Mexico region of the United States. Hawai’i J. Med. Pub. Health 72, 11–14.
Tran, B. T., Sato, H., and Van Luc, P. (2015). A new Cosmocercoides species (Nematoda: Cosmocercidae), C. tonkinensis n. sp., in the scale-bellied tree lizard (Acanthosaura lepidogaster) from Vietnmam. Acta Parasitol. 60, 407–416.
Triebskorn, R., Christensen, K., and Heim, I. (1998). Effects of orally and dermally applied metaldehyde on mucus cells of slugs (Deroceras reticulatum) depending on temperature and duration of exposure. J. Molluscan Stud. 64, 467–487. doi: 10.1093/mollus/64.4.467
Turchetti, T., and Chelazzi, G. (1984). Possible role of slugs as vectors of the chestnut blight fungus. Eur. J. For. Pathol. 14, 125–127. doi: 10.1111/j.1439-0329.1984.tb00161.x
Wester, R. E., Goth, R. W., and Webb, R. E. (1964). Transmission of downy mildew of lima beans by slugs. Phytopathology 54:749.
Wilson, M. J., Glen, D. M., and George, S. K. (1993). The rhabditid nematode Phasmarhabditis hermaphrodita as a potential biological control agent for slugs The Rhabditid Nematode Phasmarhabditis hermaphrodita as a Potential Biological Control Agent for Slugs. Biol. Sci. Technol. 3, 503–511. doi: 10.1080/09583159309355306
Wilson, M. J., Hughes, L. A., Hamacher, G. M., and Glen, D. M. (2000). Effects of Phasmarhabditis hermaphrodita on non-target molluscs. Pest Manage. Sci. 56, 711–716. doi: 10.1002/1526-4998(200008)56:8<711::aid-ps185>3.0.co;2-o
Wilson, M. J., Wilson, D. J., Aalders, L. T., and Tourna, M. (2016). Testing a new low-labour method for detecting the presence of Phasmarhabditis spp. in slugs in New Zealand. Nematology 18, 925–931.
Keywords: Phasmarhabditis californica, P. hermaphrodita, P. papillosa, invasive gastropods, nurseries
Citation: Schurkman J, Tandingan De Ley I, Anesko K, Paine T, Mc Donnell R and Dillman AR (2022) Distribution of Phasmarhabditis (Nematode: Rhabditidae) and Their Gastropod Hosts in California Plant Nurseries and Garden Centers. Front. Plant Sci. 13:856863. doi: 10.3389/fpls.2022.856863
Received: 17 February 2022; Accepted: 04 March 2022;
Published: 17 May 2022.
Edited by:
Shahid Siddique, University of California, Davis, United StatesReviewed by:
Pablo Castillo, Institute for Sustainable Agriculture (CSIC), SpainNatsumi Kanzaki, Forestry and Forest Products Research Institute, Japan
Copyright © 2022 Schurkman, Tandingan De Ley, Anesko, Paine, Mc Donnell and Dillman. This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.
*Correspondence: Adler R. Dillman, adlerd@ucr.edu