Entomopathogenic nematodes (EPNs) of the Steinernematidae and Heterorhabditidae families are widely used as biological control agents that represent a promising alternative to replace pesticides (Labaude and Griffin, 2018), because of their ability to parasitize insects, being able to identify, locate, and infect a host and to kill it within 48 hr, as well as they are safe to vertebrates, plants, and other non-target organisms. Moreover, they can be applied by means of standard spraying equipment (Poinar, 1972; Hazir et al., 2003; Van Zyl and Malan, 2014), and can be propagated in mass either in vivo using host insects such as
EPNs life cycle has six states: egg, four juvenile stages, and adults: males, females, or hermaphrodites (Shapiro-Ilan et al., 2014). EPNs of the Steinernematidae family are characterized by symbiotic associations with bacteria of the genus
Because various environmental conditions can affect survival, reproductive potential, and virulence of EPNs, the use of native species for pest control is of great importance since they are better adapted to local environmental conditions than are foreign species (Campos-Herrera and Gutiérrez, 2009). Nevertheless, in a number of countries information on EPNs and their bacterial symbionts is scarce (De Brida et al., 2017). Colombia’s records of native EPNs, a tropical country with a large agricultural population and sector, do include
Soil samples were taken in the Toribío and Tacueyó reserves of the municipality of Toribío, in the Department of Cauca, Colombia, where EPNs have never been applied. These rural areas are located between 1,757 and 2,963 meters above sea level (m.a.s.l) where temperatures range between 13.9° and 20°C. Following the sampling method developed by Varón de Agudelo and Castillo (2001), 10 sampling sites in eight types of vegetation cover were selected: natural grassland (NG), pasture bordering annual crops (PBAC), natural forest (NF), first-growth American bamboo (
Composite soil samples taken from each site were mixed and stored at room temperature for 24 hr prior to testing for IJs using the insect baiting technique (Bedding and Akhurst, 1975). For this, six samples of 150 g of mixed soil were deposited in 200 cm3 plastic boxes. Then, five
The IJs isolated were stored in polyurethane foams at 10°C in the Biological Control laboratory and deposited in the Entomology collection of the Javeriana Museum of Natural History of the Pontificia Universidad Javeriana in Bogotá, Colombia.
Abundance of EPNs at sampled sites (positive sites for EPNs/total sites) and the recovery frequency of EPNs (positive samples for EPNs/total samples analyzed) were determined according to the type of vegetation cover (Liu and Berry, 1995) and expressed as a percentage.
Genomic DNA was extracted individually from females following the protocol described by Çimen et al. (2016). After lysis of the nematodes, protein content was separated using NaCl at a final concentration of 1.7 M and centrifuging at 3,000 g for 15 min at room temperature. Finally, the supernatant was transferred to another tube for alcohol precipitation of DNA.
Sequences of the following three taxonomic markers commonly used for nematodes were amplified by PCR and used for molecular identification: a fragment of the 18S rRNA sequence using primers SSU18A-4F: 5′-GCTTGTCTCAAAGATTAAGCCATGCATG-3′ and SSU26Rplus4: 5′-AAGACATTCTTGGCAAATGCTTTCG-3′ (Morise et al., 2012); a fragment that contained the sequences ITS1, 5.8S, and ITS2 using primers 18S: 5′-TTGATTACGTCCCTGCCCTTT-3′ and 26S: 5′-TTTCACTCGCCGTTACTAAGG-3′ (Vrain et al., 1992); and a rRNA 28S fragment that contained the D2/D3 expansion sequence using D2F: 5′-CCTTAGTAACGGCGAGTGAAA-3′ (Nguyen et al., 2006) and 536: 5′-CAGCTATCCTGAGGAAAC-3′ as primers (Stock et al., 2001).
For fragment amplification, 50 µl of PCR mixture was prepared using 1X NH4 Buffer (Bioline, England), 3 mM MgCl2, 0.2 mM dNTPs, and 0.5 µg/µl Bovine Serum Albumin (New England Biolabs, United States), 0.5 µM forward primer, 0.5 µM reverse primer, Taq DNA polymerase 2U (Bioline, England), and 100 to 200 ng of template DNA (Hominick et al., 1997; Stock et al., 2001).
The PCR protocol for the 18S fragment consisted of one initial denaturation cycle at 94°C for 2 min followed by 35 cycles at 94°C for 10 sec, 55°C for 30 sec, 68°C for 1 min (Morise et al., 2012), and a final extension at 68°C for 7 min. For the ITS and D2/D3 fragments, the PCR protocol consisted of one cycle of initial denaturation at 94°C for 7 min followed by 35 cycles at 94°C for 1 min, 1 min at the annealing temperature (ITS: 50°C and D2/D3: 55°C), 72°C for 1 min and a final extension at 72°C for 7 min (Çimen et al., 2016).
Amplification of all PCR products and their respective negative amplification controls were verified by 1% (w/v) agarose gel electrophoresis in 1X TBE buffer stained with 0.5 X Hydragreen (ACTGene, United States). PCR products were purified for sequencing with Wizard SV Gel and PCR clean-up system (Promega, United States). Three purified amplicons obtained from three independent DNA extractions were sequenced for each molecular marker. Sequencing of each amplicon was performed in both directions.
The six sequences obtained for each marker were visualized, aligned, and edited manually using MEGA X software (Kumar et al., 2018) in order to obtain a consensus sequence. Its identity was initially verified by means of the Basic Local Alignment Search Tool (BLAST) (Altschul et al., 1990) on the basis of the non-redundant (nr) database of the NCBI. Consensus sequences of all markers were deposited in GenBank (NCBI) under the accession numbers listed in Table 1.
Accession numbers of sequences used for phylogenetic analysis of the EPN isolated and its bacterial symbiont.
Gen | |||||
Species | 18S | ITS | 28S | ||
|
MK558002 ■ | MK558041 ■ | MK558056 ■ | ||
|
KJ636405 | AF121049 | KJ950293 | ||
|
KJ636393 | KU194614 | KU194619 | ||
|
KJ636413 | AF121050 | JF920963 | ||
|
KU180674 | AF122015 | GU177831 | ||
|
KT878311 | AF121048 | GU569045 | ||
|
KT878314 | KF241753 | KF241750 | ||
|
KT878310 | DQ375757 | KF289902 | ||
|
AJ417021 | AY230173 | AF331902 | ||
|
KT878316 | KT373856 | KT580949 | ||
|
LC157426 | GQ497741 | AF331897 | ||
|
FJ040425 | AY230159 | AF331899 | ||
|
– | FJ381666 | AY841762 | ||
|
– | FJ263673 | AY172023 | ||
|
– | GU174002 | GU177835 | ||
|
– | AF122021 | GU177828 | ||
|
– | MF663703 | MF693228 | ||
|
– | DQ221115 | AY253296 | ||
|
– | AF122016 | AF331909 | ||
|
– | GQ497167 | GU191462 | ||
|
– | AF122020 | AF331898 | ||
|
– | AF122018 | FJ263674 | ||
|
– | AF122017 | AF331895 | ||
|
– | KP325084 | KR815816 | ||
|
– | KC633095 | KC633096 | ||
|
– | FJ410327 | FJ666054 | ||
|
– | MF289981 | JX068823 | ||
|
– | FJ235125 | FJ235126 | ||
|
– | FJ410325 | FJ410326 | ||
|
– | AY230182 | GU177834 | ||
|
– | AY230166 | AF331889 | ||
|
– | AY230165 | AF331888 | ||
|
– | EF152568 | EF152569 | ||
|
– | MF039642 | EF520284 | ||
|
– | HQ416968 | KU194621 | ||
|
– | DQ314287 | DQ314289 | ||
|
– | AY787660 | GU395637 | ||
|
– | FJ235074 | MF540678 | ||
|
– | MG543848 | MG547579 | ||
|
– | MF919614 | KU187262 | ||
|
– | JF892546 | JQ795723 | ||
|
– | EU200356 | AY841761 | ||
|
X03680 | X03680 | X03680 | ||
|
– | – | AF331910 | ||
16S |
|
|
|
|
|
|
MK558196 ■ | MK570079 ■ | MK570081 ■ | MK570080 ■ | MK570082 ■ |
|
D78009 | NC_014228 | AF127333 | NC_014228 | CBJ88402 |
|
AY278675 | FJ831460 | FJ823415 | FJ840506 | FJ808999 |
|
X82252 | FJ831466 | FJ823426 | FJ840514 | FJ809005 |
|
DQ202310 | FJ831453 | FJ823400 | FJ840503 | FJ808989 |
|
D78010 | FJ831454 | FJ823409 | FJ840499 | FJ808995 |
|
AJ810295 | FJ831458 | FJ823416 | FJ840508 | FJ809002 |
|
AJ810294 | FJ831448 | FJ823398 | FJ840495 | FJ808992 |
|
AJ810292 | FJ831476 | FJ823424 | FJ840522 | FJ809018 |
|
AJ810293 | FJ831474 | FJ823418 | FJ840518 | FJ809017 |
|
AM040494 | FJ831470 | FJ823421 | FJ840520 | FJ809013 |
|
AY521244 | FJ831472 | FJ823422 | FJ840521 | FJ809015 |
|
DQ211709 | FJ831450 | FJ823402 | FJ840497 | FJ809001 |
|
DQ211710 | FJ831449 | FJ823399 | FJ840496 | FJ808991 |
|
DQ211719 | FJ831461 | FJ823410 | FJ840510 | FJ809010 |
|
DQ205450 | FJ831457 | FJ823413 | FJ840504 | FJ809004 |
|
DQ211716 | FJ831446 | FJ823404 | FJ840493 | FJ808994 |
|
DQ211715 | FJ831464 | FJ823417 | FJ840507 | FJ809003 |
|
DQ211713 | FJ831459 | FJ823414 | FJ840505 | FJ808990 |
|
DQ211717 | FJ831451 | FJ823403 | FJ840498 | FJ809000 |
|
DQ202309 | FJ831477 | FJ823425 | FJ840524 | FJ809020 |
|
DQ205447 | FJ831452 | FJ823401 | FJ840502 | FJ808998 |
|
GQ149086 | JQ348908 | JQ348906 | JQ348909 | PHM62307 |
|
HQ877464 | JF798399 | JF798401 | JF798400 | - |
|
HQ142625 | AB685733 | AB685736 | AB685734 | KMJ46808 |
|
KX602193 | KX602195 | KX602194 | KX602196 | OKP02162 |
|
KX602187 | KX602189 | KX602188 | KX602190 | OKP00696 |
|
AJ301681 | – | – | – | – |
|
– | FJ831497 | KT963835 | KT963845 | FJ817457 |
|
– | NC_010554 | X14870 | CAR43779 | CAR46384 |
The consensus sequences of all markers were subsequently aligned with sequences of various species of EPNs deposited in GenBank (Table 1) using MUSCLE (Edgar, 2004) in MEGA X software (Kumar et al., 2018). The alignment obtained was edited so that all sequences used for analysis were of the same length and same genetic region.
Then, phylogenetic trees were independently constructed for each marker. The Tamura–Nei model of maximum likelihood estimation (Tamura and Nei, 1993) with gamma distribution and 1,000 bootstraps was used for the 18S fragment, and the General Time Reversible model of maximum likelihood estimation (Nei and Kumar, 2000) with gamma distribution and 1,000 bootstraps was used for the ITS fragment. Unweighted Pair Group Method with Arithmetic Mean (UPGMA) (Sneath and Sokal, 1973) with gamma distribution and 1,000 bootstraps was used for the D2/D3 fragment of rRNA 28S.
Because of the small number of sequences available for the 18S marker in GenBank, the additional phylogenetic analysis of concatenated sequences was made only with ITS (601 nts) and D2/D3 (754 nts) fragments. This phylogenetic tree was constructed using UPGMA (Sneath and Sokal, 1973) (Tamura–Nei model of maximum likelihood estimation (Tamura and Nei, 1993) with gamma distribution and 1,000 bootstraps).
The susceptibility of
To corroborate whether mortality was due to EPNs and check for EPNs reproduction inside the insects, adults were dissected in Ringer solution (9 g/liter NaCl, 0.4 g/liter KCl, 0.4 g/liter CaCl2, 0.2 g/liter NaHCO3) (Merck, United States). Each bioassay was repeated three times over time.
Survival analysis of insects exposed to the EPNs was performed using Graphpad Prism 6.01 software (GraphPad Software, United States) using the Kaplan–Meier method (Kaplan and Meier, 1958). To identify any significant differences between treatments, we used analysis of variance (ANOVA) testing and multiple comparisons with the Tukey test using the area under the curve.
Bacterial symbiont was isolated from hemolymph of
The correspondence of bacterial isolates to what is expected for EPNs bacterial symbionts of the
Following injection, larvae were incubated at 26°C for 48 hr, after then, their coloration, mortality, and consistency were all checked.
To identify metabolic characteristics of the bacterial isolate, a colony of the bacteria was exposed to a 3% hydrogen peroxide solution (Sigma-Aldrich, United States) using sterile wooden sticks. Subsequently, a colony was taken from nutrient agar (Scharlab, Spain) after 48 hr growth at 26°C and then resuspended in 0.85% API NaCl medium (BioMérieux, France). The API 20E fast identification system (BioMérieux, France) was then used according to the manufacturer’s instructions and incubated at 26°C for 48 hr. After incubation, results were read and interpreted following the manufacturer’s instructions.
Bacterial genomic DNA was extracted following the CTAB-based DNA extraction protocol described by Feil et al. (2004). From the extracted DNA, a Multilocus Sequence Typing (MLST) analysis was performed with the partial sequences of five genes used as taxonomic markers. The following five sequences and primers were used: 16S rRNA using 16SP1 5′-GAAGAGTTTGATCATGGCTC-3′ and 16SP2 5′-AAGGAGGTGATCCAGCCGCA-3′ (Tailliez et al., 2006);
For molecular markers amplification, 25 µl of PCR mixture was prepared using 1X NH4 Buffer, 3 mM MgCl2, 0.2 mM dNTPs (Bioline, England), 0.5 µg/µl Bovine Serum Albumin (New England Biolabs, United States), forward primer and reverse primer for each 0.5 µM of taxonomic marker, Taq DNApolimerase 2U (Bioline, England) and 20 to 100 ng of bacterial DNA (Hominick et al., 1997; Tailliez et al., 2006).
The PCR protocol consisted of an initial denaturation at 94°C for 5 min, 30 cycles at 94°C for 30 sec, 30 sec at the annealing temperature of each pair of primers (16S: 64.9°C,
PCR products were purified for sequencing with Wizard SV Gel and PCR clean-up system (Promega, United States). Three independent amplicons were sequenced in both directions for each molecular marker.
The six sequences obtained for each marker were visualized, aligned, and edited manually using the MUSCLE tool (Edgar, 2004) in the MEGA X software (Kumar et al., 2018) in order to obtain the respective consensus sequence. The consensus sequence for 16S marker was initially identified by means of EzBioCloud (Yoon et al., 2017), while BLAST (Altschul et al., 1990) was used for initial identification of other markers. The consensus sequences of all markers were deposited in GenBank (NCBI) under the accession numbers registered in Table 1.
The consensus sequences of each marker were aligned with sequences of species deposited in GenBank (NCBI) using MUSCLE (Edgar, 2004) in MEGA X software (Kumar et al., 2018). The alignment obtained was edited so that all the sequences used in the analysis were of the same length and genetic region, and phylogenetic trees were constructed independently for each marker. Maximum likelihood estimation (Tamura–Nei model [Tamura and Nei, 1993] with gamma distribution, invariant sites (G + I), and 100 bootstraps) was used for the 16S fragment; maximum likelihood estimation (Kimura 2 model [Kimura, 1980] with gamma distribution, invariant sites (G + I), and 100 bootstraps) was used for the
In addition, the
Only 14 out of 240 soil samples (5.8% recovery frequency) were found to contain EPNs. They were all from two of the 10 sites sampled (20% abundance) (site 1: CC and site 2: NF) (Table 2). However, it was only possible to multiply and maintain the isolate that was found in the soils of site 2. Only dead IJs were found when larvae with symptons of NEPs from site 1 were dissected.
Isolation of EPNs according to types of vegetation cover at sampling sites.
Vegetation cover | Location | Altitude (m.a.s.l) | Soil temperature (°C) | Recovery frequency (%) | Larvae of |
Larvae of |
---|---|---|---|---|---|---|
Natural grassland (NG) | 02°58′43.2″ N |
2,963 | 13.9 | 0.0 | 0.0 | 0.0 |
Pasture bordering annual crops (PBAC) | 02°56′57,3″ N |
1,757 | 20.0 | 0.0 | 0.0 | 0.0 |
Natural forest (NF) | 02°56′0.99″ N 76°17′19.8″ W | 1,863 | 16.4 | 50.0 | 21.7 | 1.7 |
First-growth bamboo (FGAB) | 03°00′49.5″ N |
1,894 | 18.0 | 0.0 | 0.0 | 0.0 |
Coffee cultivation (CC) | 02°56′0.45″ N 76°17′19.1″ W | 1,852 | 16.6 | 8.3 | 3.3 | 1.7 |
Horticultural cultivation (HC) | 03°00′49.5″ N |
1,894 | 18.0 | 0.0 | 0.0 | 0.0 |
Strawberry cultivation (SC) | 02°58′43.2″ N |
2,963 | 13.9 | 0.0 | 0.0 | 0.0 |
Combined lulo and papaya cultivation (CLPC) | 02°56′0,39″ N |
1,820 | 18.5 | 0.0 | 0.0 | 0.0 |
In total, 1,200 larvae of each host insect were exposed to all soil samples, but only 2.5% of
Table 2 shows EPNs isolation data in relation to types of vegetation cover and host insects. Nematodes were recovered only at sites whose soil temperatures were close to 16.5°C. Also, in both sites where EPNs were found, more
After initial BLAST identification of the 18S, ITS, and 28S markers from the isolate recovered, 100% identity and coverage were obtained with
Phylogenetic tree of
Between 0 and 6.7% of
Susceptibility of two Hass avocado (
Adults and IJs of both
The bacterial symbionts of
Microscopic and macroscopic morphological characteristics of the bacterial symbiont,
As observed in the API biochemical gallery and under incubation conditions, the bacterial symbiont was negative for β-galactosidase, arginine-dihydrolase, lysine decarboxylase, ornithine decarboxylase, citrate assimilation, H2S production, urease, tryptophan deaminase, production of indole, acetoin production (Voges – Proskauer test), gelatinase, production of acid from glucose, mannitol, inositol, sorbitol, rhamnose, sucrose, melibiose, amygdalin, and arabinose.
The initial identification, using EzBioCloud for the 16S marker and BLAST searches of the nr database of the NCBI for other markers, showed greatest similarity to the respective
Phylogenetic tree of the bacterial symbiont
The recovery frequency gives an estimated of EPNs distribution between sampling points. This study found a low or uneven distribution of EPNs in the rural region evaluated in the municipality of Toribío in the department of Cauca, Colombia, which was evidenced in a low recovery frequency. Despite differences in habitats sampled and methodologies used for soil sampling and EPNs isolation, the recovery frequency obtained in this study was similar to that reported from soils of other Latin American countries such as México (6.6%, 4 positive samples out of 60) (Delgado-Gamboa et al., 2015) and Chile (7%, 97 positive samples out of 1,382) (Edgington et al., 2010), but different from others like Brazil (23.2%, 73 positive samples out of 315) (Foelkel et al., 2017).
In contrast, in this study only one isolate of
Regarding studies in Colombia, in terms of recovery frequency our result is similar to that reported by López-Núñez et al. (2007) who, in departments of Caldas, Quindío, Risaralda and Cundinamarca, found 3% of samples positive for EPNs (28 out of 945) corresponding to 26 isolates of
The differences between the recovery frequencies found in this study compared to the results of the other studies referenced from Latin America and Colombia could be due to that factors such as soil type, distribution of suitable hosts, physiological and behavioral adaptations are key factors affecting the distribution of EPN species (Adams et al., 2006; Stuart et al., 2006). However, some of these resources have heterogeneous distribution, therefore, nematode populations are highly aggregated (Ettema and Lal, 2006).
Despite EPNs were isolated at two kind of habitats; one cultivated site (CC) and at one natural habitat (NF), the greater recovery frequency of the second one indicates that, despite the fact that natural habitats contain greater diversity of insects controlled by one or another natural enemy, it is likely that at NF there is an ecological imbalance which favors the incidence of EPNs in this habitat where they were widely distributed in the soil (Campos-Herrera et al., 2007; Jaffuel et al., 2018). By the other hand, while monocultures may have greater availability of hosts susceptible to attack by EPNs, the continuous use of pesticides can limit availability and negatively affect presence of biocontrol agents, which could be the reason for a low recovery frequency of EPNs at CC or even the no recovery of EPNs in other crop sites evaluated in this study.
In terms of abundance, which gives an estimated about the distribution of EPNs between sampling sites, in this study the EPNs abundance, was lower than registered by López-Llano and Soto-Giraldo (2016) whom obtained 88.2% of abundance (15 positive sites for EPNs out of 17) from sugarcane crops (
Although we allegedly detect EPNs at two sites, it was only possible to multiply and maintain the isolate from NF. This may have been due to ignorance of biological, ecological, and temperature conditions required for these nematodes to infect susceptible hosts and indicate a need for additional studies in the area using other detection/extraction methods and/or host insects.
Even though EPNs were allegedly detected at both sites through using the two host insects evaluated, it was evident that
EPNs of the genera
Although it has been reported that
The results obtained for susceptibility of both pests to
These results are the first record of