Introduction
Lobiopa insularis (Castelnau, 1840), a sap beetle (Coleoptera: Nitidulidae), is one of the most economically significant pests of commercial strawberry crops (Fragaria × ananassa Duchesne) (Fornari et al. 2013; Potter et al. 2013). The range of native habitats comprises almost all areas of North, Central, and South America (Lasoń and Przewozny 2009). In Argentina is a newly reported pest of strawberry (Greco et al. 2017) with damages reaching up to 46 % (affected fruits) in the horticultural area of La Plata, Buenos Aires province (D. Eliceche, pers. com).
These insects are generalist herbivores attacking not only strawberries but also tomato, peach, guava, apple, orange, and melon crops, among others; thus, undergoing population expansion when a given resource is abundant. They are strongly influenced to volatile plant compounds during fruit ripening or decay. Lin and Phelan (1991) demonstrated that seven volatile compounds (acetaldehyde, ethyl acetate, etanol, 1-propanol 2-methylpropanol 3-methylbutanol, 2-methylbutanol) attracted the sap beetles in the field. In addition to direct damage, L. insularis also serves as fungal dispersal agent, thus increasing yield losses (Dowd et al. 1995; Guimarães et al. 2009).
The larvae and adults feed on ripe fruit causing major damage to fresh-fruit. Females oviposit in the ground, and the larvae pupate within the first 10 cm (Cluigt et al. 2007). The long life span of adults (up to seven months) and high reproductive output, indicate the presence of several overlapping generations (Bortoli et al. 2014; Greco et al. 2017).
Control of L. insularis is based mainly on cultivation practices and chemical-insecticide applications (Botton et al. 2014; Myers 2014). Surpluses of these pesticides are generally dispersed into large areas, causing increased danger to the health of the human population and environment. Furthermore, such pesticide applications can also affect populations of beneficial insects (Nichols Estrada 2008).
Entomopathogenic nematodes (EPNs i. e., comprising the Steinernematidae and Heterorhabditidae) are a group of parasites causing death to insects, utilized in classical, conservation, and augmentative biological-control programs (Lacey et al. 2015). They present a combination of desirable attributes as bioregulators such as their wide host range, the ability to cause high insect mortalities, their environmental friendliness, their facile production at different scales by methods both in vivo and in culture, and the compatibility with various chemicals and other bioregulatory agents (Shapiro-Ilán and Dolinski 2012).
The associations with symbiotic pathogenic bacteria make EPNs highly virulent. The life cycle includes the non-feeding third-stage infective juveniles (IJs), or "Dauer" larvae, which is the only free-living stage, that gain access into the haemocel of host insects through natural body openings or by penetrating thin cuticles (Lewis et al. 2006). Once inside the host, a symbiotic bacterium is released in the haemolymph that proliferates and produces a wide range of toxins and hydrolytic exoenzymes that are responsible for the death (at 24-48 h post-infection) along with a degradation of the insect’s composition into a nutrient soup needed for the nematode’s growth and reproduction (Bowen et al. 1998). Nematodes complete one to three generations within the cadaver, and IJs exit to find new a hosts in response to declining nutrients. Nematodes of the genus Heterorhabditis always present a first generation of adult hermaphrodites and, usually, a second and third generation with males and bona-fide females (Vega and Kaya 2012).
Environmental conditions can reduce the efficacy of nematode IJs in controlling pests. Native species adapted to local climatic conditions, would be expected to be more likely to survive after release in a given target area (Campos-Herrera et al. 2008; Shapiro et al. 1999). Nevertheless, up to the present time, mainly nonnative strains have been used in nematode applications throughout the world since most of commercial species available have been isolated from either North America or Europe (Grewal and Peters 2005).
To date, no biological products ‒nematodes or otherwise‒ registered in Argentina for the control of L. insularis are available, and alternatives to chemical pesticides are needed. Thus, for the regulation of this pest, EPNs may be good biological control candidates.
The objectives of the work reported here was to identify an EPN of native pasture soils in the pampean region of Argentina and to evaluate its infectivity, development, and multiplication in the sap beetle L. insularis under laboratory conditions.
Materials and methods
Soil sampling and nematode extraction
Soil samples were collected in an organic farm in the location of Villa Elisa (34°51’12”S, 58°04’45”W; 9.87 meters above sea level) La Plata, Buenos Aires province, Argentina. This horticultural area is characterized by the intensive cultivation of fresh fruit and vegetable products and family farms where the main cultivated crops are tomato, celery, lettuce, peppers, strawberry, spinach, eggplant, and basil (Ferratto et al. 2010). Soils of this region are argiudol (Imbellone et al. 2010), the average annual temperature is 15.9 °C, and the annual rainfall is about 1,100 mm. Samples were taken with a shovel to a depth of 15 cm and transported to the laboratory for processing in plastic bags at room temperature.
Nematodes were extracted from the soil and maintained in the laboratory using the wax moth Galleria mellonella Linnaeus (Lepidoptera: Pyralidae) as a susceptible host (Woodring and Kaya 1998). Last-instar G. mellonella larvae were placed in 250 mL plastic containers (at ten larvae each) with moistened soil from the collected samples and maintained at room temperature (20 ± 3 °C). The insect larvae were checked daily for two weeks to observe mortality by EPNs. The dead insects were thoroughly rinsed in distilled water and placed in a modified White trap according to the procedure described by Stock and Goodrich-Blair (2012). This technique consists of setting a moistened filter paper on a watch glass inside a Petri dish with water covering the bottom, on which paper the bodies of the insects are placed. When nematode infection has occurred, the IJs migrate from the cadaver to the water (usually at 15-20 days post-exposure). The IJs collected in this manner were subsequently stored in cell-culture flasks at 18 ± 2 °C for eventual use in laboratory assays.
Nematode identification: Morphological and morphometric characters
The first generation of hermaphroditic females, the second of amphimictic females, males and IJs were used for morphological and morphometric studies. Adults were obtained by dissecting G. mellonella larvae infected by EPNs at different times i. e., between 3-4 (hermaphrodites), 5-7 (females and males) and 15-20 days (IJs). A total of 25 specimens from each developmental stage were considered for the determination of qualitative and quantitative data.
The nematodes thus obtained were killed in Ringer’s solution at 60 °C, placed in triethanolamine-formalin fixative (Kaya and Stock 1997), and solvent-dehydrated to anhydrous glycerin for mounting (Seinhorst 1959). The fixed specimens were used for drawings and measurements with the aid of a camera lucida mounted on a Zeiss microscope.
For examination by scanning electron microscopy, nematodes of different developmental stages were fixed in 3 % (v/v) aqueous glutaraldehyde buffer pH 7.2 for at least 48 h at 4-8 °C. The samples were then post-fixed with 2 % (w/v) osmium-tetroxide solution for 12 h at 25 °C, dehydrated in a graded-ethanol series, critical-point dried with liquid CO2, mounted on specimen stubs, and coated with gold (Nguyen and Smart 1995). Observations of the ultrastructure were then made with a JEOL JSM-100 scanning electron microscope.
The following morphometric data were analyzed: L, total body length; MBW, maximum body width; ABW, anal-body width; VBW, vulval-body width; EP, distance from anterior end to excretory pore; ES, distance from anterior end to base of esophagus; GuL, gubernaculum length; GuW, gubernaculum width; NR, nerve-ring position; STL, stoma length; STW, stoma width; SpL, spicule length; SpW, spicule width; TL, tail length, TRL, testis-reflection length; D, EP/ES; E, EP/TL; GS, GuL/SpL; V %, (L/length to vagina) x 100. In addition, for the IJs the following ratios were used: a, L/MBW; b, L/ES; c, L/TL; d, EP/ES; e, EP/TL (Table1). The tail measurements of the IJs did not include the extra cuticle sheath (cuticle of the second stage).
Character | Hermaprhroditic females | Amphimictic females | Males | Infective juveniles |
---|---|---|---|---|
L | 2,835.46 ± 482.72 | 1,646.34 ± 282.42 | 822.46 ± 83.16 | 616.75 ± 60.95 |
(2,160-3,840) | (1,251-2,286) | (711-972) | (505.04-675.12) | |
MBW | 117.64 ± 14.32 | 97.08 ± 11.89 | 46.89 ± 6.61 | 25.04 ± 1.6 |
(97.4-138.65) | (78.8-113.68) | (42.3-62.6) | (23.2-27.84) | |
STL | 8.91 ± 2.10 | 7.76 ± 1.36 | 5.22 ± 1.71 | - |
(6.25-11.6) | (6.96-11.6) | (2.35-4.28) | ||
STW | 8.16 ± 1.34 | 7.22 ± 0.69 | 4.264 ± 1.15 | - |
(5.87-9.28) | (6.96-9.28) | (2.35-6.9) | ||
NR | 88.95 ± 1.34 | 73.69 ± 13.56 | 66.39 ± 10.21 | - |
(69.6-118.7) | (58-104.4) | (39.9-81.2) | ||
EP | 157.65 ± 19.89 | 117.18 ± 20.88 | 110.17 ± 22.31 | 100.11 ± 12.34 |
(132.24-200) | (83.52-173.32) | (95.12-134.5) | (78.8-109.04) | |
ES | 152.58 ± 16.41 | 123.13 ± 10.04 | 116.07 ± 12.40 | 101.93 ± 14.46 |
(132.22-181.25) | (104.4-141.52) | (104.4-141.52) | (74.24-113.68) | |
TL | 47.87 ± 9.46 | 41.58 ± 0.39 | 27.95 ± 8.47 | 38.54 ± 14.3 |
(37.5-51.04) | (20.88-53.36) | (22.0-41.76) | (32.16-51.4) | |
ABW | 52.41 ± 17.80 | 48.36 ± 12.30 | 36.91 ± 10.97 | 18.63 ± 3.25 |
(37.12-63.45) | (27.84-69.6) | (27-8-44.08) | (15.08-27.84) | |
V | 42.15 ± 12.79 | 45.61 ± 2.69 | - | - |
(39.2-49.68) | ||||
TRL | - | - | 200.78 ± 77.98 | - |
(103.4-229.68) | ||||
SpL | - | - | 45.00 ± 4.76 | - |
(34.8-48.7) | ||||
SpW | - | - | 4.64 ± 0.66 | - |
(3.48-5.8) | ||||
GuL | - | - | 22.5 ± 6.49 | - |
(18.5-21.1) | ||||
GuW | - | - | 5.21 ± 1.37 | - |
(3.94-6.96) | ||||
GS (GuL/SpL) | - | - | 0.53 ± 0.13 | - |
(0.48-0.55) | ||||
SW (SpL/ABW) | - | - | 10.28 ± 2.09 | - |
(7.29-14.0) | ||||
E (EP/TL) | - | - | 4.32 ± 3.11 | - |
(2.96-5.65) | ||||
D (EP/ES) | - | - | 1.11 ± 0.18 | - |
(0.89-1.17) | ||||
L/TL | 35.62 ± 19.58 | |||
(21.36-44.18) | ||||
L/MBW | - | - | 19.31 ± 3.64 | - |
(13.5-22.97) | ||||
MBW/TL | - | - | 1.57 ± 1.09 | - |
(1.1-2.7) | ||||
Ratio a (L/MBW) | - | - | - | 23.76 ± 3.03 |
(22.2-26.2) | ||||
Ratio b (L/ES) | - | - | - | 6.19 ±1.2 |
(5.3-8.8) | ||||
Ratio c (L/TL) | - | - | - | 9.87 ± 3.63 |
(6.2-14.4) | ||||
Ratio d (EP/ES) | - | - | - | 0.99 ± 0.14 |
(0.62-1.07) | ||||
Ratio e (EP/TL) | - | - | - | 1.54 ± 0.39 |
(1.9-2.1) |
Molecular-genetic analysis
To confirm the identification of the nematodes a molecular-genetic approach was performed. Thus, genomic DNAs was extracted from pools of 30 third-stage infective juveniles (IJs), by standard protocols (Sambrooket al. 1989). Briefly, specimens were first homogenized in 250 µL of distilled water and then treated with 250 µL of lysis solution (10 mM Tris/HCl, pH 8; 10 mM EDTA, 0.25 % w/v SDS) containing 5 µg/µL proteinase K (Fermentas). Then, after the quality and quantity of the DNA was verified by electrophoresis and spectrophotometry (Nanodrop 1000, Thermo). The samples were used in polymerase-chain reactions (PCRs) to amplify a set of nuclear loci that contained the following sequences: the 18S-ribosomal-RNA gene (partial sequence), the internal transcribed spacers ITS 1, ITS 2, and the 5.8S and 28S fragments of the ribosomal-RNA gene. Primers used [ITS-F (5´-TTGAACCGGGTAAAAGTCG-3´) and ITS-R (5´-TTAGTTTCTTTTCCTCCGCT-3´)] were designed by means of a previously reported protocol (Maneesakorn et al. 2011) and the thermal profile (Verity thermal cycle, Applied Biosystem) included: 94 °C, 2 minutes (1 cycle); 92 °C, 15 seconds; 55 °C, 15 seconds; 72 °C, 1 minute (35 cycle); 72 °C, 5 minutes (1 cycle). The amplification products were separated by electrophoresis with molecular-weight standards used as a reference (PB-L, Argentina) and the corresponding DNAs isolated with the Zymoclean Gel DNA-recovery Kit (Zymo research) according to the manufacturer’s specifications. Next, the amplicons were cloned in Escherichia coli (strain Top 10) by ligation to the pGem-T-Easy vector (Promega). After bacterial-colony selection and plasmid isolation, the inserts were identified by automated Sanger sequencing using the universal primers Sp6 and T7 (Macrogen Services).
Evaluation of the EPNs against the sap beetles: Susceptibility of L. insularis stages to Heterorhabditis bacteriophora VEli
Insects were obtained from strawberry fields in La Plata (34°56’35”S, 58°5’30”W), Buenos Aires Province, Argentina. Adults and larvae were collected by using baited pitfall traps during the fruiting season and by examining plants and collecting ripe fruit. The pitfall traps consisted in a 0.5 L plastic cone, wide end up, nested inside a plastic cylinder with the latter buried to the mouth in the soil in the middle of a strawberry bed. The captured insects were later reared in the laboratory according to Blumberg et al. (1985) on the artificial diet used for Drosophila spp. (Demerec and Kaufman 1965) and maintained at 20 ± 2 °C at a relative humidity of 70 %. The taxonomic identification of the sap beetles was determined by Andrew R. Cline from Plant Pest Diagnostics Branch, California Department of Food and Agriculture, Sacramento, CA, USA.
The susceptibility of each stage of L. insularis was tested by separately exposing larvae, pupae, and adults (n = 10) to the EPNs. Each stage was put in a plastic container (200 ml) with sterile moistened clay soil (100 ml). The larvae and adults were placed on the surface of the soil and the pupae buried at a depth of 2 cm. To obtain parasitism over 60 %, a concentration of 10,000 IJs per container was used based on experiments by Glazer et al. (2007) against sap beetles. The number of individuals tested is shown in table 2. A control group with no nematodes was included in every assay. At 10 days after exposure of the sap beetles to the IJs, mortality was registered and the cadavers were placed in modified White traps to determine infectivity, emergence time and production of IJs for each stage. The number of days from the recorded mortality in the insects to the first emergence of the IJs was considered as the emergence time. The total production was determined by examination of the IJs in White traps at each interval of five days after the first appearance of the nematodes, until no further emergence was recorded. The total number was determined by the method of dilution: One ml of the initial suspension of IJs was diluted with 5 ml of distilled water, the suspension agitated vigorously, and 5 aliquots (1 ml) counted (Stock and Goodrich-Blair 2012).
The subsequent serial infectivity of IJs emerged from infected L. insularis was also evaluated. Tests were performed in 10-cm Petri dishes with ten G. mellonella larvae as a sensitive host and 1,000 IJs. Mortality was determined every 24 h and the dead insects placed in White traps to corroborate the emergence of nematodes from infected individuals. Six replicas were performed.
All assays were realized at 20 °C and at a relative humidity of 70 %.
Lethal-concentration determination (LC 50 and LC 90 )
The concentration needed for the EPNs to kill 50 % and 90 % of the L. insularis larvae (LC50 and LC90) were determined. Larvae were added to plastic 200-ml containers (n = 10) with autoclaved clay soil (100 ml) obtained from horticultural gardens along with concentrations of 0; 1,000; 5,000 and 10,000 IJs per container. Only larvae of L. insularis were considered for tests, for being the main target to control this pest with EPNs due to its high susceptibility and behavior in the field, falling to the ground and bury themselves to pupate. The number of individuals tested is shown in Table 3. The mortality was assessed 10 days post-exposure and the cadavers were placed in modified White traps to determine emergence of IJs. Total production of IJs and the time of emergence at each concentration were measured as was described previously for bioassays of susceptibility.
Parasitism by EPNs on adults of L. insularis in containers with strawberries as attractant food
To determine whether strawberries applied to the containers as food attractants of adults increase the susceptibility to EPNs, six containers with 10 adults each one were provided with a ripe strawberry and another six were left with no food (total adults: 120). A concentration of 10,000 JIs per container was used. Strawberries were obtained from plants grown in the greenhouse of the CEPAVE institute (Sweet Ann strain). They presented a size between 3 and 4 cm long and 75 % of the red fruit, value considered by the maturity index established by SENASA (National Agri-Food Quality and Health Service of Argentina) for mature fruits. A control group (n = 10) without nematodes was included in each assay. Mortality was registered at 10 days after exposure of the sap beetles, and the cadavers placed in modified White traps to determine IJ emergence and thus corroborate infectivity by the EPNs.
Data analyses
For the determination of the lethal concentrations (LC50 and LC90), a probit model that relates log10 (concentration) to the probit was used with the Ecotoxicology library (V 1.0.1), implemented in R, and the Probit EPA function that simulates the EPA's proven EERD (Ecological Exposure Research Division).
The infectivity of H. bacteriophora by concentration and stage were analyzed by binomial test of proportions. A global type I error of 0.05 was adjusted to 0.0169 by the experimentwise error rate, due to the three pairs of comparisons (3) to be tested (Lyman Ott and Longnecker 2010). To compare the production, the data were normalized by applying natural logarithm showing to be homoscedastic (Levene test with p-value = 0.7748) and then an analysis of variance (ANOVA) was used. A Kruskall - Wallis comparison was considered to detect differences between the medians of the emergency times, and assays of food attractants. Differences in median emergency between concentrations were detected by the Mann - Whitney - Wilcoxon test (Hollander et al. 2014).
Results
Identification of nematodes
The analyses of morphology and molecular genetics carried out enabled us to determine an isolate of H. bacteriophora. The strain was designated as VEli according to the sampling site of origin (i. e. Villa Elisa) being the first documentation of an EPN for that locale and the second for the Buenos Aires province.
The morphology proved to be similar to that described for other H. bacteriophora populations. The adults (in general) are with the head from truncate to slightly rounded; six different lips surround the mouth opening, each one bearing an inner labial papilla. At the base of each sub-dorsal and sub-lateral lip are two additional papillae representing an outer labial papilla and a cephalic papilla (Fig. 1D). The base of each lateral lip contains an elliptical amphidial opening and an outer labial papilla, while the stoma is mostly collapsed (Figs. 1C-D).
The females are variable in size, with an amphidelphic reproductive system that is reflexed past the vulval opening. The dioecious females are with a nonfunctional vulva for oviposition and a pointed tail (Figs. 2A-B). The hermaphroditic female is thin and elongated with a truncated anterior end, an open vulva functional for oviposition, and the anal region slightly protruding (Figs. 2C-D).
The males have a single reflexed testis, spicules paired and separate, the peloderan bursa supported by nine pairs of papillae: a small anterior pair, two pairs adjacent to the spicules, and six pairs distal to the anal opening. The latter six are in two sets of three (Figs. 1A-B).
The IJs have a head bearing a dorsal tooth (Fig. 2F); a cuticle with two double lateral lines; the body, with a tessellate pattern (Fig. 2F), covered by the enclosing second-stage cuticle; and the tail pointed (Fig. 2E).
Table 1 lists the morphologic measurements. Fertilized females were not considered for morphometric features due to the intra-uterine birth causing maternal death (endotokia matricida) a phenomenon common in rhabditid nematodes and typical for entomopathogenic nematodes of the Heterorhabditis genus (Figs. 2A, C).
The sequences of genomic-DNA fragments determined in the VEli strain ‒consisting of part of the 18S, ITS1, 5.8S, and ITS2 loci plus a portion of the 28S locus (901 bp including the PCR primers)‒ were registered in the Genbank public database (accession number: KJ575524). The subsequent bioinformatic analyses that we carried out enabled us to conclude that this nematode was an authentic isolate of Heterorhabditis bacteriophora.
Examined material
Heterorhabditis bacteriophora strain VELi. Hermaphrodites, females, males and IJs (=25). ARGENTINA. Buenos Aires province. Municipality of La Plata. Villa Elisa 34°51’12”S 58°04’45”W 9.87 masl 27-May-2014. Collected by Daiana Eliceche, and registered in the Museum of La Plata under the sample designation [MLP-He 6725].
Evaluation of the EPNs against the sap beetles: Susceptibility of L. insularis stages to Heterorhabditis bacteriophora VEli
The degree of infectivity in the three stages was significantly different (P < 0.0013). Infectivity was higher in larvae and pupae (77 ± 17 % and 64 ± 25 %, respectively) than in the adults (2.2 ± 1.1 %; Table 2). The cadavers presented purple color (Figs. 3A-F).
Lethal-concentration determination (LC 50 and LC 90 )
A mortality of 25-77 % was caused by H. bacteriophora VEli in L. insularis larvae at the three concentrations tested. The highest mortality was obtained at a concentration of 10,000 IJs per container (Table 3). The three comparisons showed a lower significance level than the one proposed by experimentwise (0.0169), therefore the infectivity was different in each concentration. The lethal concentration required to kill 50 and 90 % of the larvae (LC50 and LC90) over 10 days was 2,840 IJs/container (lower fiducial limit =268; upper fiducial limit= 5,130) and 23,743 IJs/container (lower fiducial limit = 11,952; upper limit= 597,190) respectively (Fig. 4; Table 4). The cadavers were always observed purple color.
Parasitism by EPNs on adults of L. insularis in containers with strawberries as attractant food
Low parasitism by EPNs was determined in containers with and without a supply of strawberries (10.00 ± 0.00 % and 2.2 ± 1.1 %, respectively). However, significant differences were observed (P = 0.019).
IJ-production capacity and EPN-emergence time
The total IJ production obtained from cadavers from different L. insularis stages and concentrations, ranged between 840 and 9,247 individuals, reaching maximum values in larvae at a concentration of 1,000 JIs per container (Tables 2, 3). However, analysis of variance did not indicate differences due to concentration (F = 0.4381, df = (2, 12), P = 0.6552) or stage (F = 0.1559, df = (2, 10), P = 0.8577).
The initiation of IJ emergence from the dead insects occurred between 11 and 22 days post-exposure for larvae, 20 and 30 days for pupae, and 21 and 25 days for adults (Table 2). In the larvae, emergence of IJs occurred during a less extended period of time than for the pupae or adults (Table 2).
A longer time interval was observed at a concentration of 10,000 JIs per container relative to the corresponding intervals for the lower concentrations (11-22 days, Table 3). The Kruskal - Wallis test, determined significant differences among the medians of the emergence times (χ2 = 6.33; df = 2; P = 0.04). Comparing scores of two with Mann - Whitney - Wilcoxon test adjusted significance of 0.0169, the only significant difference was between concentration of 5,000 and 10,000 (P = 0.01322) and between larvae and pupae (P = 0.429).
The JIs emerged from L. insularis were pathogenic in re-infections with a mean value of 70 ± 16 %, and produced new generations of IJs.
Discussion
Heterorhabditis bacteriophora populations have been recorded in a range of different habitats from Argentina (Stock 1995; Doucet and Bertollotti 1996; Doucet et al. 2001; Giayetto and Cichón 2006; Del Valle et al. 2013). In the Buenos Aires province, only a single record had been reported by Stock (1995) for the town of City Bell, but without records of molecular and morphometric data.
Geographical origin and habitat can influence nematode morphology. Studies on the morphometric variability can be useful in providing valuable information about the geographical and ecologic requirements for EPNs (Stock et al. 2000; 382 Lacey and Georgis 2012). Accordingly, morphological and morphometric features of the population of H. bacteriophora reported here are first for Buenos Aires province.
Because H. bacteriophora VEli killed L. insularis in all developmental stages, we consider this new isolate to be a potential biological control agent. EPNs were able to complete their life cycle in larvae, pupae, or adults, a capability that would improve the establishment and spread of the strain in its natural habitat. In all experiments, a change in the host body color (dark red to purple) caused by symbiotic bacteria was observed, thus confirming infection. Likewise, previous studies have demonstrated Heterorhabditis spp. to have high potential for use as a control agent for sap beetles (Carpophilus sp.) in a date-palm orchard and recorded a substantial reduction (50-70 %) in insect emergence in the field (Glazer et al. 2007).
A higher level of infectivity and longer period of emergence time was obtained in L. insularis larvae for the highest concentration (10,000 IJs per container), but a lower production of IJs was registered. The reason of the differences could be related to the level of infectivity obtained. A higher percentage of parasitism indicates that more nematodes have penetrated the host and are residing inside having to share the same resources. The more limited availability of nutrients per nematode likely interferes in its development thus resulting in a lower number of generations for the subsequent production of IJs. A limit in the supply of nutrients available to the nematode because of an interaction with the host immune system, and/or a reduced reproduction of symbiotic bacteria can result in a lower total generation of IJs inside a particular host (Forst and Clarke 2002).
The variation in the infectivity, time to first emergence, and total number of IJs between stages of L. insularis may also have resulted from differences in development time of the EPNs and differential susceptibility among the stages, as was observed for other insects (Koppenhofer and Fuzy 2004). A variety of reasons have been given to explain such observed differences, including the size, immune response, behavior, and nutritional condition of the host, such as the type of nutrients produced by the symbiotic bacteria (Shapiro et al. 1999).
Strategies for controlling sap beetles are farming practices and insecticide applications. A challenge in the production of strawberries is to obtain fruit with acceptable pesticide residue levels without compromising fruit quality or environmental sustainability.
EPNs have been used with varying degrees of success against pest insects that exit fruit and pupate in the soil. They are an environmentally safe means of pest management and may be an alternative to chemical insecticides (Lacey and Georgis 2012). However, EPNs are produced and marketed by only a few companies with mainly nonnative strains being used for applications. Strains adapted to local environmental and climatic conditions would offer distinct advantages for the management of local pests from the standpoint of adaptability and ecological compatibility (Lewis et al. 2006).
The results of our study indicate that EPNs effectively kill all L. insularis stages and complete their development in a time similar to that of other EPNs in other hosts. In addition, IJs emerging from L. insularis are infective, thus insuring the nematode’s maintenance in the field through subsequent reinfections.