CC BY
125Russian Journal of Nematology, 2013, 21 (2), 117-130
First record on the distribution of entomopathogenic nematodes (Rhabditida: Steinernematidae and Heterorhabditidae) in
Southern Benin
Lionel Zadji1' 3, Hugues Baimey1. Leonard Afouda^Fifame G. Houssou3, Lieven Waeyenberge , Nancy de Sutter , Maurice Moens ' and Wilfrida Decraemer '
University of Parakou, P.O. Box, 123 Benin, e-mail: [email protected]; 2Institute for Agricultural and Fisheries Research (ILVO) Crop Protection Department, Burg. Van
Gansberghelaan 96, 9820 Merelbeke, Belgium; 3Department of Biology Ghent University, Ledeganckstraat 35, 9000 Ghent, Belgium; 4Department of Crop Protection, Ghent University, Coupure Links 653, 9000 Ghent, Belgium; 5Royal Belgian Institute of Natural Sciences, Vautierstraat 29, 1000 Brussels, Belgium.
Accepted for publication 29 October 2013
Summary. For the first time, surveys of entomopathogenic nematodes (EPN) were conducted in five departments in the Guinean zone of Southern Benin. Out of 84 prospected sites and 280 collected soil samples from agricultural and natural vegetation, 26 (31.0%) and 32 (11.4%) were positive for EPN, respectively. Identification of the EPN was based on analyses of sequences of the ITS rDNA region and morphological/morphometric investigations. Two species were found, Heterorhabditis sonorensis and H. indica. This is the first record of H. sonorensis since its description from the Sonora desert in Mexico. Heterorhabditis sonorensis was the most common species, showing a preference for semi-closed habitats such as citrus orchards, other fruit production fields and woodland with soils having sand and organic matter content ranging between 53.6-89.5% and 0.1-4.7%, respectively, and a pH from acidic (4) to neutral (7.1). Entomopathogenic nematodes were not recovered from crop fields (maize, cassava, groundnut and bean) and soil samples with less than 50% sand content. Heterorhabditis indica was associated with citrus orchards and fruit fields on sand to sandy clay soils, with pH slightly acidic (pH = 5.4-6.4), but not with woodland. Discriminant analysis identified five major environmental variables, longitude, organic matter content and texture (silt, sand and clay content) to be the most important abiotic factors determining the occurrence of EPN in soil from Southern Benin. Using these parameters, redundancy analysis revealed that H. sonorensis and H. indica prefer soils with high sand or organic matter content located in the more eastern longitude. No significant difference was observed in EPN species preferences taken individually, in terms of studied ecological parameters. Key words: Benin, distribution, Guinean zone, Heterorhabditis, survey.
Entomopathogenic nematodes (EPN) are known since 1923 with the description of Aplectana kraussei Steiner, 1923, now Steinernema kraussei Travassos, 1927 (Nguyen & Hunt, 2007). Although nearly 40 nematode families have been isolated from soil inhabiting insects throughout the world, only two families, Steinernematidae Travassos, 1927 and Heterorhabditidae Poinar, 1976, are of major interest in agriculture because of their potential in regulating insect populations, particularly insect pests with a soil-dwelling phase (Kaya & Gaugler, 1993). They are associated with
symbiotic bacteria belonging to the genus Xenorhabdus (Steinernema spp.) and Photorhabdus (Heterorhabditis spp.) (Boemare et al., 1993). Entomopathogenic nematodes along with their bacterial symbionts are able to kill their insect hosts in a short period of time, usually within 24 to 48 h.
Numerous surveys have provided evidence of the omnipresence of these nematodes. Entomopathogenic nematodes have been isolated from many types of natural and managed habitats in a wide variety of soils throughout the world (Hominick, 2002); Antarctica is the only continent
from which they have not been recorded (Griffin et al, 1991). The African continent remains largely a fertile field for EPN exploration. At the end of the 20th century, only two Steinernema species, S. feltiae (Filipjev, 1934) Wouts, Mracek, Gerdin & Bedding, 1992 (Egypt) and S. karii Waturu, Hunt & Reid, 1997 (Kenya), and three Heterorhabditis species, H. bacteriophora Poinar, 1976 (Kenya and South Africa), H. indica Poinar, Karunakar & David, 1992 (Egypt and Kenya) and H. taysearae Shamseldean, El-Sooud, Abd-Elgawad & Saleh, 1996 (Egypt) had been recorded for this continent (Peters, 1996; Shamseldean et al., 1996; Waturu, 1998). More recent surveys in Africa revealed several new species: S. yirgalemense Nguyen, Tesfamariam, Gozel, Gaugler & Adams, 2005, S. ethiopiense Tamiru, Waeyenberge, Hailu, Ehlers, Puza & Mracek, 2012 (both from Ethiopia), S. khoisanae Nguyen, Malan & Gozel, 2006, H. safricana Malan, Nguyen, De Waal & Tiedt, 2008 (both from South Africa), S. citrae Malan, Knoetze & Moore, 2011 (South Africa), and S. cameroonense Kanga, Trinh, Waeyenberge, Spiridonov, Hauser & Moens, 2012 and S. nyetense Kanga, Trinh, Waeyenberge, Spiridonov, Hauser & Moens, 2012 (both from Cameroon) (Nguyen et al., 2006; Nguyen & Hunt, 2007; Malan et al., 2008; Malan et al., 2011; Kanga et al., 2012; Tamiru et al., 2012). New strains of H. indica and H. bacteriophora were reported from Kenya and Egypt (Stack et al, 2000; Hominick, 2002), new isolates of S. yirgalemense, S. karii and S. weiseri Mracek, Sturhan & Reid, 2003 were found in the Central Rift Valley Region of Kenya (Nyasani et al, 2008) and a population of S. yirgalemense was detected in South Africa (Malan et al, 2011). In Ethiopia, the dominant species detected was S. yirgalemense (6.3%) next to two isolates of H. bacteriophora (0.7%) (Mekete et al, 2005). Kanga et al. (2012) reported from Cameroon new strains of H. baujardi Phan, Subbotin, Nguyen & Moens, 2003, a species originally described from Vietnam and later also recorded from Brazil.
Thus far, no study has been published on the EPN distribution in Benin. However, within the framework of the VLIR-UOS Own Initiative 2010 project on Ecologically Sustainable Citrus Production in Benin, the potential of indigenous EPN as an environmental friendly alternative control agent to the commonly used synthetic chemicals is being investigated. In this respect, surveys for EPN were conducted in 2010 and 2011 throughout the Southern part of Benin.
The current contribution presents the first records of EPN from Benin. It reports the occurrence of two
Heterorhabditis species in Southern Benin and their distribution in agricultural and natural habitats.
MATERIALS AND METHODS
Site description and sampling characterisation. The Republic of Benin is situated in West Africa between the latitudes 6°10'N and 12°25'N and longitudes 0°45'E and 3°55'E. Three climate zones can broadly be distinguished (Akoegninou, 2004): i) the Northern zone located between 9°45'-12°25'N; ii) the transition zone located between 7°30'-9°45'N; and iii) the Southern zone located between 6°25'-7°30'N. Soil samples for our study were collected from the Southern zone where the climate is Guinean with two rainy seasons alternating with a long dry season (December-February). Two surveys of EPN were carried out during the rainy season in September 2010 and August 2011. In the prospected area, the mean annual rainfall varies from 1048.3 to 1604 mm; the mean annual temperature ranges from 26 to 28°C and the annual relative humidity from 75.5 to 81.7% (Table 1).
The first survey was mainly orientated towards citrus orchards (orange, lemon and grapefruit) with a high incidence of insect populations. During the second survey, samples were also taken in fields next to citrus orchards and included other fruit fields (mango, cashew, avocado, guava, banana, oil palm), annual and perennial crop fields (maize, cassava, groundnut, bean), and woodland (teak, acacia, eucalyptus). A total of 280 soil samples were collected from 84 sites distributed over 28 communities. At each site, a total of 3-4 samples, at least 10 m apart, were taken. Each soil sample (approximately 1.5 kg) consisted of a composite of 3-5 cores randomly taken in a 9-m2 area; always close a tree or plant, at a depth of 0-15 cm and using a hand trowel. Samples were placed in polyethylene bags to prevent water loss and kept in coolers (ca 15°C) during transit to the laboratory.
At each site, data on sampling location, habitat (vegetation), longitude, latitude and altitude were recorded. For each sampling site, a subsample (ca 300 g) was analysed for the following physical and chemical characteristics: pH, organic matter, sand, silt, and clay content. Soil samples were processed at the Soil Analysis Laboratory of the Faculty of Agronomy Sciences, University of Abomey Calavi, Benin.
Nematode isolation. Entomopathogenic nematodes were recovered from soil samples using the insect baiting method (Bedding & Akhurst, 1975). Within a week after the sampling, a
subsample of ca 350 cm3 was transferred to a 360-cm3 plastic container to which five larvae of Galleria mellonella were added as bait. The containers were inverted and kept in the dark at ambient temperature of 27±2°C. Five days after incubation, the dead larvae were removed, rinsed successively with alcohol (70%) and water. Dead larvae that exhibited signs of infection with EPN, i.e., flaccid, soft, odourless larvae with either light to dark brown or reddish colour, were washed and placed in modified White traps (White, 1927). The larvae on the White trap were checked for emergence of nematodes after 1 week and thereafter daily. All nematodes emerging from dead larvae of the same sample were bulked and considered as one isolate. In the case of negative results, the isolation was repeated once to confirm results of the first observation.
To verify the pathogenicity of the collected nematodes and to establish new cultures, emerging nematodes were used to infect fresh G. mellonella larvae (Kaya & Stock, 1997). Then, dead larvae were collected and separately placed on a White trap. The emerged nematodes were collected alive in distilled water over a 2-week period and stored at 13°C. Isolate stocks were maintained on G. mellonella larvae being re-inoculated on a 2-month basis.
Nematode identification. Both molecular and morphological/morphometric approaches were used for the nematode identification, starting with the molecular analysis (Joyce et al, 1994; Stock, 2009).
Molecular characterisation and phylogenetic analysis. Molecular characterisation of the isolates was performed by analysis of the ITS rDNA sequences. Genomic DNA was extracted from a single nematode and the ITS regions and the 5.8S rRNA gene of the ribosomal DNA (rDNA) was amplified by PCR according to procedures described by Joyce et al. (1994). The obtained 707-bp sequences (Fig. 1) were compared with all DNA-sequences of Heterorhabditis species available in Genbank using the Basic Local Alignment Search Tool (BLAST) of the National Centre for Biotechnology Information (www.ncbi.com).
An alignment of the ITS1-5.8S-ITS2 sequences was generated using Clustal W (Thompson et al., 1997) and used for phylogenetic analysis. A phylogenetic tree was produced using the Neighbour Joining method (Saitou & Nei, 1987). The analysis involved 48 nucleotide sequences (Fig. 1) and was conducted in MEGA5 (Tamura et al., 2011). In agreement with Nguyen et al. (2010) Caenorhabditis elegans (EU131007) was applied as outgroup.
Morphological characterisation. Nematodes were examined live or heat-killed in 60°C Ringer's solution. The heat-killed nematodes were placed in triethanolamine-formalin (TAF) fixative (Kaya & Stock, 1997) and processed to anhydrous glycerin for mounting (Seinhorst, 1959). Observations were made from live and mounted specimens using an Olympus BX51 microscope equipped with differential interference contrast optics and digital image software (CellD Soft Imaging System, Olympus Company, Japan). For morphological characterisation of the isolates, 20 second-generation males and 30 infective juveniles (IJ) were randomly selected from different G. mellonella cadavers (Nguyen & Smart Jr., 1995). According to their morphological traits, isolates were placed into similar species-groups using taxonomic criteria suggested by Stock & Kaya (1996) and Hominick et al. (1997).
Data analysis. Diversity patterns among sampling sites were assessed by means of Principal Component Analysis (PCA) performed with environmental variables (latitude, longitude, altitude, habitat, pH, soil texture, silt, sand, clay, and organic matter content of the soil). To scrutinise the ecological trends of EPN isolates, the occurrence of EPN related to the environmental variables was first assessed with their recovery frequency (number positive samples/total number samples) (Liu & Berry 1995), expressed as percentage. Afterwards, Discriminant Analysis (DA) was used to determine which of the environmental variables were the best predictors of the presence of EPN in soil samples. These latter variables were used in Redundancy Analysis (RDA) to investigate differences in ecological preferences of the Heterorhabditis species found (Van den Wollenberg, 1977). The species matrix data was characterised by EPN species presence/absence and the analysis was conducted on centred response variables because species frequencies do not require standardisation. The selected environmental variables were used as explanatory variables. Statistical analyses were performed using STATISTICA 7 for PCA and DA, and XL STAT 2012 for RDA agricultural and natural vegetation, 26 (31.0%) and 32 (11.4%) were EPN-positive, respectively. Molecular examination revealed that they all belonged to the genus Heterorhabditis. Twenty-nine isolates showed 100% sequence similarity with H. sonorensis Stock, Rivera-Orduno & Flores-Lara, 2009; 99% with H. taysearae; 98% with H. mexicana Nguyen, Shapiro-Ilan, Stuart, McCoy, James & Adams, 2004 and H. floridensis Nguyen, Gozel, Koppenhofer & Adams, 2006; and 97% with H. amazonensis Andalo, Nguyen
Fig. 1. Phylogenetic relationships of 15 Heterorhabditis species for which ITS sequences are available in Genbank, 32 Heterorhabditis isolates from Benin, and one outgroup species (Caenorhabditis elegans) based on analysis of ITS regions by Neighbour-Joining method. Tree length = 660.72. Numbers above the nodes indicate bootstrap value and numbers below branches represent base differences per sequence. Numbers after species name correspond to GenBank accession numbers, sample code.
Table 1. Sampled departments in Benin: geographic location and climate characteristics.
Department Latitude Longitude Altitude* (m) Annual precipitation* (mm) Mean annual temperature* (°C) Relative humidity* (%)*
Atlantique 02° 15'00" 06° 40' 00" 27 1604 28.4 81
Couffo 01° 48' 06" 06° 57' 43" 121 1326.5 28.2 75.8
Mono 01° 43' 00" 06° 38' 00" 12 1048.3 27.8 81.5
Oueme 02° 36'00" 06° 30'00" 31 1553.4 28.4 80.8
Plateau 02° 41' 00" 06° 58' 00" 75 1305.2 27.6 81.7
Zou 01° 59' 00" 07° 11' 00" 121 1114.07 28.2 75.5
*Source: Agence pour la Sécurité de la Navigation Aérienne en Afrique et à Madagascar (ASECNA).
& Moino, 2006 and H. baujardi. The remainder of the selected isolates shared sequence similarity of 99% with H. indica.
RESULTS
Identification of isolates. Out of 84 prospected sites and 280 collected soil samples from agricultural and natural vegetation, 26 (30.95%) and 32 (11.43%) were EPN-positive, respectively. Molecular examination revealed that they all belonged to the genus Heterorhabditis. Twenty-nine isolates showed 100% sequence similarity with H. sonorensis Stock, Rivera-Orduno & Flores-Lara, 2009; 99% with H. taysearae; 98% with H. mexicana Nguyen, Shapiro-Ilan, Stuart, McCoy, James & Adams, 2004 and H. floridensis Nguyen, Gozel, Koppenhofer & Adams, 2006; and 97% with H. amazonensis Andalo, Nguyen & Moino, 2006 and H. baujardi. The remainder of the selected isolates shared sequence similarity of 99% with H. indica.
In the phylogenetic tree inferred from the ITS sequences (sum of branch length = 660.72; Fig. 1), the 29 aforementioned isolates clustered with H. sonorensis (bootstrap value = 63%). The pairwise distance comparison (showed below branches) revealed the 29 isolates to differ from H. taysearae and H. mexicana by one and four bases, respectively. No sequence difference was found between these isolates and H. sonorensis. Hence, we concluded that these 29 isolates belonged to H. sonorensis. Likewise, three other isolates (Ayogbe1, Ayogbe2 and Dodji) clustered in a separate group (bootstrap value = 96%). They formed a monophyletic clade with H. indica supported by a high bootstrap value of 99% (Fig. 1). They therefore were considered conspecific with H. indica.
The morphology and morphometrics of the isolates conformed to the original description of the
species to which they were assigned. Both species are easily separated from each other by the position of the excretory/secretory pore of the male, which in H. indica is located posterior to the basal bulb, whereas in H. sonorensis it is usually posterior to the nerve ring at the level of the basal bulb (data not shown). Further, the gubernaculum of H. indica is flat, about half the spicule length in size, whereas the gubernaculum of H. sonorensis is slightly curved ventrally and about 60% of spicule length (data not shown).
Spatial distribution of EPNs and interrelated variables
Diversity patterns of sampled sites. The
correlation between features characterising the environment and major components 1 and 2 (Table 2) revealed that the first three components expressed 73.15% of data variability and are sufficient to describe reliably diversity patterns among sampled sites. The first component represented a gradient of decreasing organic matter content (-0.61), pH (-0.64), longitude (-0.89) and latitude (-0.89) with habitat (-0.60) changing progressively from semi-closed habitats (woodland, fruit fields and citrus orchards) to open habitats (crop fields) from left to the right. The second component represented increasing contents of sand (0.94) and decreasing contents of silt (-0.67) and clay (-0.83) from the bottom to the top. The third component represented soil texture (0.89) changing from sand, sandy loam, sandy clay loam and sandy clay from the bottom to the top.
When soil samples were projected on the plane of components 1 and 2 (Fig. 2A), samples from the more western longitude and the more southern latitude, with the highest pH and the lowest organic matter, silt, sand and clay content collected in open habitat (crop field) were located at the top left of the
quadrant I. Samples from the more eastern longitude and the more north latitude, with the lowest pH, organic matter, silt and clay content, and the highest sand content collected in semi-closed habitat (citrus orchards, fruit fields and woodland) were located at the top right of the quadrant II. Quadrant III contained samples from the more western longitude and western latitude, with the highest pH, organic matter, silt and clay content and the lowest sand content collected in opened habitat (crop field). When soil samples were projected on the plane of components 1 and 3 (Fig. 2B), samples from lighter-textured soils were located in quadrants I and II.
Occurrence of isolates with associated ecological parameters. In terms of recovery frequency, an unequal separation of EPN isolates was observed (Table 3). Entomopathogenic nematodes occurred in all the studied ecosystems, with the exception of crop fields and soils with more than 40% silt or clay content, or less than 50% sand content.
In terms of species diversity, H. sonorensis was the most prevalent species found in 90.6% of the positive samples located between latitudes 1°48' and 2°37', longitudes 6°25' and 7°30' and altitudes between 8 and 252 m. The soil samples positive for H. sonorensis had a pH ranging from 4 to 7, a silt content from 1.3 to 30.5%, a sand content from 53.6 to 89.5%, a clay content from 4.5 to 36.4%, and an organic matter content between 0.1 and 4.7%. This species was found at sites with a sandy, sandy clay, sandy loam, or sandy clay loam soil texture and occurred in semi-closed habitats, such as citrus orchards, fruit fields and woodland.
Heterorhabditis indica was found in 9.4% of the positive samples. This species was located between latitude 2°15' and 2°00' and longitude 6°41' and 7°17'. It was found associated with citrus orchards and fruit field habitats, at altitudes between 12-102 m, in soils with pH ranging from 5.4 to 6.4, silt content from 2.3 to 2.7%, sand content from 77.1 to 83.4%, clay content from 20.6-13.9% and organic
1 II
• III * * * IV
-6-5-4-3 -2 -1 0 1 2 345
• ^ » • • II ♦
* • • • * III • • 'V • *: . * IV
-6-5-1-3 -2 -1 012345 Component 1 (32.73%)
Fig. 2. Projection of soil samples on the planes defined by the component 1 and 2 (A) and the components 1 and 3 (B) of the principal component analysis of soil samples involving environmental variables (latitude, longitude, altitude, habitat, pH, silt, sand, clay and organic matter content and texture). Dots represent more than one soil sample.
Table 2. Correlation between variables characterising the environment of sampled sites in south Benin and the first three components of the principal component analysis (bold values indicate parameters dominating principal components 1, 2 or 3).
Variables Component 1 Component 2 Component 3
Silt -0.46 -0.67 0.51
Sand 0.29 0.94 -0.06
Clay 0.01 -0.83 -0.45
Soil texture -0.24 -0.06 0.89
Organic matter -0.61 -0.45 -0.32
pH -0.64 0.24 0.14
Altitude 0.45 0.04 0.10
Habitat -0.60 0.18 -0.28
Longitude -0.89 0.35 -0.08
Latitude -0.89 0.35 -0.08
Eigen values variance 3.27 2.56 1.48
Percentage of variance 32.73 25.57 14.85
Cumulative percentage of variance (%) 32.73 58.30 73.15
matter content from 2.4 to 2.9%. The soil textures were sand and sandy clay. Heterorhabditis sonorensis was found in all sub-ecosystems where H. indica was found. However, H. indica was not present in sub-ecosystems with sandy loam and sandy clay loam soil types, with pH < 5 located, and altitude > 150 m and latitude below 2°00', where H. sonorensis was present (Table 3).
Discriminant analysis. Five variables (longitude, organic matter, silt, sand, and clay content) discriminated, as best, positive soil samples from negative soil samples (Table 4).
Redundancy analysis. An overall test of significance showed that the canonical relationship between EPN presence and selected environmental variables is highly significant (P = 0.016 after 1000 permutations; Pseudo F = 0.115). The RDA axis 1 explains 96.3% of the total variance of the data, which is sufficient to describe the relation between environmental variables and EPN presence. Standardised canonical coefficients for explanatory variables are given in Table 5. Magnitudes of these coefficients represent their relative contributions to the related axis. All variables for the canonical axis 1 have negative coefficients while coefficient of sand, silt and clay demonstrate the highest contribution of these characteristics to the canonical axis in absolute value.
When the variables and species were projected on the plane of axis 1 and 2, EPN-positive soil samples, the arrows of the variables longitude, sand and organic matter pointed at the left direction, whereas the arrows of the variables clay and silt pointed at the opposite direction. Arrows indicate
the direction of increasing of either the values of the significant environmental variables or species presence. As a result, the presence of H. sonorensis and H. indica is correlated with increases of longitude, sand and organic matter content and a decrease of clay and silt content (Fig. 3). However, no difference in individual ecological preferences was observed between the two species.
DISCUSSION
The present study reports for the first time the occurrence of EPN in Benin. During the surveys conducted in 2010 and 2011, only the genus Heterorhabditis was recorded. This could be due to: i) the low prevalence of Steinernema genus as compared with Heterorhabditis genus; ii) the difference in biology of the two genera. One heterorhabditid is sufficient to multiply after invasion while at least two steinernematids (IJ to develop in male and female) must invade before reproduction can occur (Downes & Griffin, 1996);
iii) the restricted sampling; a more intensive sampling might have yielded additional species; and
iv) the use of G. mellonella only as the baiting insect; several different hosts might have yielded additional species. As a consequence, the Galleria-bait method may not have allowed us to identify all EPN present. Occasionally, the method does not detect EPN in positive samples (Spiridonov & Moens, 1999).
Out of 280 samples, 32 were EPN-positive (11.4%). Prevalence of EPN varies widely between different surveys, and ranges between 2% and 45% (Hominick, 2002). However, the recovery frequency
Table 3. Distribution of heterorhabditids in south Benin at ranges of different environmental variables.
Categories (total samples) Recovery frequency (%)a Positive samples
Nob Percentage0
Latitude
[1°39 - 2°00] (74) 5.4 4 (4-0) 12.5
[2°00 - 2°38] (206) 13.6 28(25-3) 87.5
Longitude
[6°24 - 7°00] (171) 9.4 16 (15-1) 50
[7°00 - 7°30](109) 14.7 16 (14-2) 50
Altitude (m)
[7 - 50] (146) 11.6 17 (15-2) 53.1
[50 - 150] (115) 12.2 14 (13-1) 43.8
[150 - 252](19) 5.3 1 (1-0) 3.1
Habitat
Citrus orchards (167) 9.6 16 (15-1) 50
Fruit fields (56) 17.9 10 (8-2) 31.3
Woodland (44) 13.6 6 (6-0) 18.8
Crop fields (13) 0 0 0
pH
[4 - 5] (24) 4.2 1 (1-0) 3.1
[5 - 6] (127) 9.5 12 (11-1) 37.5
[6 - 7] (106) 16 17 (15-2) 53.1
[7 - 8] (23) 8.7 2 6.3
Silt content % (0.002-0.05mm)
[0 - 10] (214) 12.2 26 (23-3) 81.3
[10 - 20] (36) 11.1 4(4-0) 12.5
[20 - 30] (21) 4.8 1 (1-0) 3.1
[30 - 40] (6) 16.7 1 (1-0) 3.1
[40 - 50] (3) 0 0 0.00
Sand content % (0.05 - 2mm)
[30 - 40] (8) 0 0 0.00
[40 - 50] (12) 0 0 0.00
[50 - 60] (13) 15.4 2 (2-0) 6.3
[60 - 70] (29) 13.8 4(4-0) 12.5
[70 - 80] (82) 13.4 11 (11-0) 34.4
[80 - 90] (136) 11 15 (12-3) 46.9
Clay content % (<0.002mm)
[4 - 10] (37) 13.5 5 (5-0) 15.6
[10 - 20] (189) 12.2 23 (22-1) 71.9
[20 - 30] (40) 7.5 3 (1-2) 9.4
[30 - 40] (6) 16.7 1 (1-0) 3.1
[40 - 50] (8) 0 0 0
Organic matter content %
[0 - 1] (37) 10.8 4(4-0) 12.5
[1 - 2] (85) 5.9 5 (5-0) 15.6
[2 - 3] (94) 14.9 14 (11-3) 43.8
[3 - 4] (37) 8.1 3 (3-0) 9.4
[4 - 5] (15) 26.7 4(4-0) 12.5
[5 - 6] (12) 16.7 2 (2-0) 6.3
Soil texture
sand (144) 11.1 16 (15-1) 50
sandy clay (100) 13 13 (11-2) 40.6
sandy loam (23) 8.7 2 (2-0) 6.3
sandy clay loam (13) 7.7 1 ü-°) 3.1
a Recovery frequency (number of positive samples/total number of samples). b Number of positive samples (number of isolate of H. sonorensis - number of isolate of H. indica) c Percentage positive samples (number positive samples per category variable/number total positive samples).
value recorded in south Benin is within the ranges reported in African countries: Egypt (10%) (Shamseldean & Abd-Elgawad, 1994), Ethiopia (6.9%) (Mekete et al, 2005), Central Kenya (24%) (Waturu, 1998), and south Cameroon (10.4%) (Kanga et al, 2012).
This is the second record of H. sonorensis originally described from the Sonoran desert in Mexico (Stock et al, 2009) and so the first record for Africa, expanding its currently known geographic range. The presence of H. sonorensis in these two different parts of the world is probably
because they both prefer a tropical climate. South Benin has a subtropical climate with two rainy seasons, whereas the Sonoran Desert has a dry tropical climate also with two rainy seasons. Moreover, in the Sonoran desert, about half of the biota is tropical in origin. The finding of H. indica in south Benin demonstrates its prevalence in tropical and subtropical zones (Hominick, 2002). The species was first isolated in Coimbatore, India (Poinar et al, 1992); later its wide distribution in the Asian continent was demonstrated by its detection in Malaysia (Mason et al, 1996), Japan (Yoshida et al., 1998), Indonesia (Griffin et al, 2000); Palestine (Sansour & Iraki, 2000), Vietnam (Phan et al., 2001), Saudi Arabia (Saleh et al., 2001), Pakistan (Anis et al, 2000; Shahina et al., 2001; Shahina & Mahreen, 2010). On the American continent, H. indica was reported from Cuba (Mrâcek et al, 1994), Guadeloupe, Jamaica, Dominican Republic, Martinique, Puerto Rico, and Trinidad (Constant et al, 1998; Fisher-Le Saux et al., 1998), Venezuela (Rosales & Suarez, 1998), the Virgin Islands and Florida (Stack et al, 2000). In Africa, it was only
detected in Kenya (Waturu, 1998) and Egypt (Grenier et al, 1996; Stack et al., 2000). The species was also reported in Australia (Akhurst, 1987).
Although the majority of the soil samples were taken from citrus orchards (164/280), the principal component analysis has revealed high diversity patterns among sampled sites. The area surveyed covered wide ranges of pH of the soil (4-8), silt (050%), sand (30-90%), clay (4-40%) and organic matter (0-6%) content, soil texture (sand, sandy loam, sandy clay loam and sandy clay), habitat (citrus orchards, fruit fields, woodland and crop fields), and altitude (7-252 m). However, no EPN were recovered from arable crop fields. This is in contrast to Akhurst & Brooks (1984), Hominick & Briscoe (1990) and Griffin et al. (1991) who observed more EPN in agricultural fields. Our observations might be biased by the survey periods, when fields were greatly disturbed by farmers' practices, including use of fertilisers and pesticides.
Like many other surveys (Kung et al, 1990b; Grffin et al, 1991; Hara et al, 1991; Rueda et al, 1993; Choo et al, 1995; Liu & Berry, 1995; Miduturi et
0.8 0.6 0.4 0.2
Ü2 0
X <
-0.2
-0.4
-0.6
-0.8
H. sonorensis
¿Pi/idica
Negative sample
-0.8 -0.6 -0.4 -0.2
0 0.2 AXIS 1
0.4 0.6 0.8
1.2 1.4 1.6 1.8
Fig. 3. Redundancy analysis triplot showing correlation between Heterorhabditis-positive samples, Heterorhabditis-negative samples and environmental variables (longitude, silt, sand, clay and organic matter content). Dots represent more than one sample.
al, 1996; Hazir et al., 2003; Kanga et al., 2012) our study showed that sandy soil is the preferred soil texture for EPN. Earlier it was shown that both mobility and survival of EPN are favoured in soils with a high sand content, whereas soils with high clay content restrict nematode movements
(Molyneux & Bedding, 1984; Kung et al, 1990b). In terms of pH-tolerance, H. indica was only isolated from slightly acidic (pH = 5.4-6.4) soils; H. sonorensis was isolated from acidic (pH = 5) to neutral (pH = 7.1) soils. This agrees with other studies in which the pH of Heterorhabditis-positive
soil samples varied from 4.3 to 7.0 (Canhilal & 1991; Griffin et al, 1994). In most agro-ecosystems Carner, 2006), and between 4.6 and 8 (Hara et al, the pH (range: 4-8) is not likely to have any significant
Table 4. Discriminant analysis of environmental variables predicting presence of entomopathogenic nematodes in soil
samples (bold values indicate variables in the model).
Parameters Wilks' Lambda Partial Lambda P-level 1-R-square
Longitude 0.961002 0.968678 0.012987 0.211826
Silt 0.950930 0.978939 0.054721 0.980739
Organic matter 0.942605 0.987585 0.181723 0.200838
Sand 0.945439 0.984624 0.120621 0.991339
Clay 0.943223 0.986937 0.166158 0.977789
pH 0.927415 0.996254 0.600206 0.181189
Altitude 0.925494 0.994190 0.452738 0.328629
Habitat 0.930714 0.999798 0.972891 0.141064
Latitude 0.926365 0.995126 0.514501 0.319167
effect on EPN presence; however, pH > 10 is likely to be detrimental (Kung et al., 1990a). Heterorhabditis indica was isolated from soils with 2.4-2.9% organic matter content, whereas H. sonorensis was isolated from soils with a larger range (0.1-4.7%). Canhilal and Carner (2006) reported that the organic matter content of Heterorhabditis-positive soils collected in South Carolina averaged 3% (0.7-7.8). In heterorhabditid-positive soil samples collected in the Central Rift Valley Region of Kenya a range of 2-3% was reported by Mwaniki et al. (2008). Earlier reports suggest that H. indica is not restricted by vegetation type (Griffin et al, 2000); however, during the present survey, H. indica was only observed from citrus orchards and fruit production fields, whereas H. sonorensis was observed from citrus orchards, fruit production fields and woodland. This suggests that the influence of agricultural activities on H. sonorensis seems to be less than on H. indica in our survey. Moreover, the differences in the distribution of
Table 5. Standardised canonical coefficients, eigenvalues and percentages of inertia from redundancy analysis.
these two species could be the result of the availability or differences in the distribution of suitable host insects.
Discriminant analysis identified longitude, organic matter content and soil texture (silt, sand and clay content) to be the most important abiotic factors determining the occurrence of EPN in soil from south Benin. Using these parameters, redundancy analysis results revealed H. sonorensis and H. indica to prefer soil with high sand or organic matter content located in the more eastern longitude; in other words, soil with decreasing silt and clay content. However, no significant difference was observed in ecological trends of EPN species taken individually. Soil texture is essential for the existence of some Heterorhabditis species and accordingly plays an important role in the EPN dispersal and persistence (Georgis & Poinar, 1983; Kung et al, 1990b; Sturhan, 1999).
This was the first attempt to study the occurrence and diversity of EPN in Benin. In comparison with other studies the diversity is rather low with no record of Steinernema. Within the on-going project, we expect further surveys in other areas to increase the number of EPN species of both genera.
ACKNOWLEDGEMENT
Funding for this study was provided by the Flemish Inter-university Council - University Development Co-operation (VLIR-UOS) Belgium, through the "Ecological Sustainable Citrus Production in Benin" Project. VLIR-UOS is gratefully acknowledged by the authors.
Variables AXIS 1 AXIS 2 AXIS 3
Silt -21.854 10.938 -2.916
Sand -33.342 16.551 -4.125
Clay -19.859 9.924 -2.410
Organic matter -0.243 0.118 0.060
Longitude -0.460 0.010 0.092
Eigenvalue 0.128 0.004 0.001
Constrained inertia (%) 96.254 2.802 0.944
Cumulative % 96.254 99.056 100.000
REFERENCES
Akhurst, R.J. & Brooks, W.M. 1984. The distribution of entomophilic nematodes (Heterorhabditidae and Steinernematidae) in North Carolina. Journal of Invertebrate Pathology 44: 140-145.
Akhurst, R.J. 1987. Use of starch gel electrophoresis in the taxonomy of the genus Heterorhabditis (Nematoda: Heterorhabditidae). Nematologica 33: 1-9.
Akoegninou, A. 2004. Recherches botaniques et écologiques sur les forêts actuelles du Bénin. Dissertation, Université de Cocody-Abidjan (Côte d'Ivoire) 326 pp.
Anis, M., Shahina, F., Reid, A.P. & Maqbool, M.A. 2000. Re-description of Heterorhabditis indica Poinar et al., 1992 (Rhabditida: Heterorhabditidae) from Pakistan. Pakistan Journal of Nematology 18: 11-27.
Bedding, R.A. & Akhurst, J.R. 1975. A simple technique for the detection of insect parasitic rhabditid nematodes in soil. Nematologica 21: 10-11.
BOEMARE, N.E., Boyer-Giglio, M.H., THALER, J.O. & Akhurst, R.J. 1993. The phages and bacteriocins of Xenorhabdus spp., symbiont of the nematodes Steinernema spp. and Heterorhabditis spp. In: Nematodes and the Biological Control of Insect Pests (R. Bedding, R. Akhurst & H. Kaya. Eds.). pp. 137145. CSIRO Publications, East Melbourne, Vic., Australia.
Canhilal, R. & Carner, G.R. 2006. Natural occurrence of entomopathogenic nematodes (Rhabditida: Steinernematidae and Heterorhabditidae) in South Carolina. Journal of Agricultural & Urban Entomology 23: 159-166.
Choo, H.Y., Kaya, H.K. & Stock, S.P. 1995. Isolation of entomopathogenic nematodes (Steinernematidae and Heterorhabditidae) in Korea. Japanese Journal of Nematology 25: 44-51.
Constant, P., Marchay, L., Fisher-Le Saux, M., Briand-Panoma, S. & Mauleon, H. 1998. Natural occurrence of entomopathogenic nematodes (Rhabditida: Steinernematidae and Heterorhabditidae) in Guadeloupe islands. Fundamental and Applied Nematology 21: 667-672.
Downes, M.J. & Griffin, C.T. 1996. Dispersal behaviour and transmission strategies of the entomopathogenic nematodes Heterorhabditis and Steinernema. Biocontrol Science and Technology 6: 347-356.
Fischer-Le Saux, M., Mauleon, H., Constant, P., BRUNEL, B. & BOEMARE, N. 1998. PCR ribotyping of Xenorhabdus and Photorhabdus isolates from the Caribbean region in relation to the taxonomy and geographic distribution of their nematode hosts. Applied and Environmental Microbiology 64: 4246-4254.
Georgis, R. & Poinar, G.O.Jr. 1983. Effect of soil texture on the distribution and infectivity of Neoaplectana carpocapsae (Nematoda:
Steinernematidae). Journal of Nematology 15: 308-311.
Grenier, E., Bonifassi, E., Abad, P. & Laumond, C. 1996. Use of species specific satellite DNAs as diagnostic probes in the identification of Steinernematidae and Heterorhabditidae entomopathogenic nematodes. Parasitology 113: 483-489.
Griffin, C.T., Moore, J.F. & Downes, M.J. 1991. occurrence of insect-parasitic nematodes (steinernematidae and Heterorhabditidae) in the Republic of Ireland. Nematalogica 37: 92-100.
Griffin, C.T., Joyce, S.A., Dix, I., Burnell, A.M. & Downes, M.J. 1994. Characterization of Heterorhabditis (Nematoda: Heterorhabditidae) from Ireland and Britain by molecular and cross-breeding techniques, and the occurrence of the genus in these islands. Fundamental and Applied Nematology 17: 245-253.
Griffin, C.T., Chaerani, R., Fallon, D., Reid, A.P. & Downes, M.J. 2000. Occurrence and distribution of the entomopathogenic nematodes Steinernema spp. and Heterorhabditis indica in indonesia. Journal of Helminthology 74: 143-150.
Hara, A.H., Gaugler, R., Kaya, H.K. & LeBeck, L.M. 1991. Natural populations of entomopathogenic nematodes (Rhabditida: Steinernematidae and Heterorhabditidae) from the Hawaiian islands. Environmental Entomology 17: 211-216.
Hazir, S., Keskin, N., Stock, S.P., Kaya, H. & Özcan, S. 2003. Diversity and distribution of entomopathogenic nematodes (Rhabditida: Steinernematidae and Heterorhabditidae) in Turkey. Biodiversity and Conservation 12: 375-386.
Hominick, W.M. & Briscoe, B.R. 1990. Occurrence of entomopathogenic nematodes (Rhabditida: Steinernematidae and Heterorhabditidae) in British soils. Parasitology 100: 295-302.
Hominick, W.M., Briscoe, B.R., Del-Pino, F.G., Heng, J., Hunt, D.J. & Kozodoy, E. 1997. Biosystematics of entomopathogenic nematodes: current status, protocols and definitions. Journal of Helminthology 71: 271-298.
Hominick, W.M. 2002. Biogeography. In: Entomopathogenic nematology (R. Gaugler. Ed.). pp. 115-143. CABI Publishing, Wallingford, UK.
Joyce, S.A., Reid, A., Driver, F. & Curran, J. 1994. Application of polymerase chain reaction (PCR) methods to the identification of entomopathogenic nematodes. In: COST 812 Biotechnology: Genetics of entomopathogenic nematode bacterium complexes (A.M. Burnell, R.-U. Ehlers & J.-P. Masson. Eds). pp. 178-187. Proceedings of symposium and workshop, St
Patrick's College, Maynooth, County Kildare, Ireland Luxembourg, European Commission, DGXII.
Kanga, F.N., Waeyenberge, L., Hauser, S. & Moens, M. 2012. Distribution of entomopathogenic nematodes in Southern Cameroon. Journal of Invertebrate Pathology 109: 41-51.
Kanga, F.N., Trinh, P.Q., Waeyenberge, L., Spiridonov, S.E., Hauser, S. & Moens, M. 2012. Two new species of Steinernema Travassos, 1927 from the humid forest of southern Cameroon. Russian Journal of Nematology 20: 15-36.
Kaya, H.K. & Gaugler, R. 1993. Entomopathogenic Nematodes. Annual Review of Entomology 38: 181-206.
KAYA, H.K. & STOCK, S.P. 1997. Techniques in insect nematology. In: Manual of techniques in insect pathology. (L. Lacey. Ed.). pp. 313-314. Academic Press, San Diego, CA, USA.
Kung, S., Gaugler, R., Kaya, H.K. 1990a. Influence of soil pH and oxygen on persistence of Steinernema spp. Journal of Nematology 22: 440-445.
Kung, S.P., Gaugler, R. & Kaya, H.K. 1990b. Soil type and entomopathogenic nematode persistence. Journal of Invertebrate Pathology 55: 401-406.
Liu, J. & BERRY, R.E. 1995. Natural distribution of entomopathogenic nematodes (Rhabditida: Steinernematidae and Heterorhabditidae) in Oregon soils. Environmental Entomology 24: 159-163.
Malan, A.P., Nguyen, K.B., De Waal, J.Y. & Tiedt, L. 2008. Heterorhabditis safricana n. sp. (Rhabditida: Heterorhabditidae), a new entomopathogenic nematode from South Africa. Nematology 10: 381-396.
Malan, A.P., Knoetze, R. & Moore, S.D. 2011. Isolation and identification of entomopathogenic nematodes from citrus orchards in South Africa and their biocontrol potential against false codling moth. Journal of Invertebrate Pathology 108: 115-125.
Mason, J.M., Razak, A.R. & Wright, D.J. 1996. The recovery of entomopathogenic nematodes from selected areas within Peninsular Malaysia. Journal of Helminthology 70: 303-307.
Mekete, T., Gaugler, R., Nguyen, K.B., Mandefro, W. & Tessera, M. 2005. Biogeography of entomopathogenic in Ethiopia. Nematropica 35: 31-36.
Miduturi, J.S., Matata, G.J.M., Waeyenberge, L. & Moens, M. 1996. Naturally occurring of entomopathogenic nematodes in the province of East Flanders, Belgium. Nematologia Mediterranea 24: 287-293.
Molyneux, A.S. & Bedding, R.A. 1984. Influence of soil texture and moisture on the infectivity of
Heterorhabditis sp. D1 and Steinernema glaseri for larvae of the sheep blowfly, Lucilia cuprina. Nematologica 30: 358-365.
Mräcek, Z., Hermandez, E.A. & Boemare, N.E. 1994. Steinernema cubana sp. n. (Nematoda: Rhabditida:
Steinernematidae) and the preliminary characterization of its associated bacterium. Journal of Invertebrate Pathology 64: 123-129.
Mwaniki, S.W., Nderitu, J.H., Olubayo, F., Kimenju, J.W. & Nguyen, K. 2008. Factors influencing the occurrence of entomopathogenic nematodes in the Central Rift Valley Region of Kenya. African Journal of Ecology 46: 79-84.
Nguyen, K.B. & Smart, G.C. Jr. 1995. Morphometrics of infective juveniles of Steinernema spp. and Heterorhabditis bacteriophora (Nemata: Rhabditida). Nematology 27: 206-212.
Nguyen, K.B., Malan, A.P. & Gozel, U. 2006. Steinernema khoisanae n. sp. (Rhabditida: Steinernematidae), a new entomopathogenic nematode from South Africa. Nematology 8: 157-175.
Nguyen, K.B. & Hunt, D.J. 2007. Entomopathogenic Nematode: Systematics, Phylogeny and Bacterial Symbionts. Brill, Leiden, the Netherlands. 816pp.
Nguyen, K.B., Ginarte, C.M., Leite, L.G., Santos, J.M. & HARAKAVA, R. 2010. Steinernema brazilense n. sp. (Rhabditida: Steinernematidae), a new entomopathogenic nematode from Mato Grosso, Brazil. Journal of Invertebrate Pathology 103: 8-20.
Nyasani, J.O., Kimenju, J.W., Olubayo, F.M. & Wilson, M.J. 2008. Laboratory and field investigations using indigenous entomopathogenic nematodes for biological control of Plutella xylostella in Kenya. International Journal of Pest Management 54: 355-361.
Peters, A. 1996. The natural host range of Steinernema and Heterorhabditis spp. and their impact on insect
population. Biocontrol Science and Technology 6: 389-402.
Phan, L.K., Nguyen, C.N. & Moens, M. 2001. Steinernema sangi sp. n. (Rhabditida: Steinernematidae) from Vietnam. Russian Journal of Nematology 9: 1-17.
Poinar, G.O., Karunakar, G.K. & David, H. 1992. Heterorhabditis indica n. sp. (Rhabditida: Nematoda) from india: separation of Heterorhabditis spp. by infective juveniles. Fundamental and Applied Nematology 15: 467-472.
Rosales, A.L.C. & Suarez, H.Z. 1998. Entomopathogenic nematodes as possible control agents of the banana root borer weevil Cosmopolites sordidus (Germar) 1824 (Coleoptera: Curculionidae). Boletin de Entomologia Venezolana, Serie Monografías 13: 123-140.
Rueda, L.M., Osawaru, S.O., Georgi, L.L. & Harrison, R.E. 1993. Natural occurrence of entomopathogenous nematodes in Tennessee nursery soils. Journal of Nematology 25: 181-188.
Saitou, N. & Nei, M. 1987. The neighbor-joining method: A new method for reconstructing
phylogenetic trees. Molecular Biology Evolution 4: 406-425.
Saleh, M.M.E., Hanounik, S.B., Al-Muhanna, U.E., Al-Dahir, H. & Al-Garrash, Z.H., 2001. Distribution of Heterorhabditis indica (Nematoda: Heterorhabditidae) in eastern Saudi Arabia. International Journal of Nematology 11: 215-218.
Sansour, M.A. & Iraki, N.M. 2000. RAPD-PCR characterization of two strains of the entomopathogenic nematode Heterorhabditis indica isolated from Bethlehem, Palestine. In: Cost 819 Developments in Entomopathogenic Nematode/ Bacterial Research (C.T. Griffin, A.M. Burnell, M.J. Downes & R. Mulder. Eds.). pp. 240. European Commission, DGXII, Luxembourg.
Seinhorst, J.W. 1959. A rapid method for the transfer of nematodes from fixative to anhydrous glycerin. Nematologica 4: 67-69.
Shamseldean, M.M. & Abd-Elgawad, M.M. 1994. Natural occurrence of insect pathogenic nematodes (Rhabditida: Heterorhabditidae) in Egyptian soils. Afro-Asian Journal of Nematology 4: 151-154.
Shamseldean, M.M., Abou El-Sooud, A.B., Abd-Elgawad, M.M. & Saleh, M.M. 1996. Identification of a new Heterorhabditis species from Egypt, Heterorhabditis taysearae n. sp. (Rhabditida: Heterorhabditidae). Egyptian Journal of Biological Pest Control 6: 129-138.
Shahina, F., Anis, M., Reid, A.P., Rowe, J. & MAQBOOL, M.A. 2001. Steinernema pakistanense sp. n. (Rhabditida: Steinernematidae) from Pakistan. International Journal of Nematology 11: 124-133.
Shahina, F. & Mahreen, G. 2010. Entomopathogenic nematode species with new codes from Pakistan. Pakistan Journal of Nematology 28: 145-148.
Spiridonov, S.E. & Moens, M. 1999. Two previously unreported species of steinernematids from woodlands in Belgium. Russian journal of Nematology 7: 39-42.
Stack, C.M., Easwaramoorthy, S.G., Metha, U.K., Downes, M.J., Griffin, C.T. & Burnell, A.M. 2000. Molecular characterisation of Heterorhabditis indica isolates from India, Kenya, Indonesia and Cuba. Nematology 2: 477-487.
Stock, S.P. & Kaya, H.K. 1996. A multivariate analysis of morphometric characters of Heterorhabditis species (Nemata, Heterorhabditidae) and the role of morphometrics in the taxonomy of the species of the genus. Journal of Parasitology 82: 806-813.
Stock, S.P. 2009. Molecular approaches and the taxonomy of insect-parasitic and pathogenic nematodes. In: Insect pathogens, molecular approaches and techniques (S.P. Stock, J. Vandenberg, I. Glazer & N. Boemare. Eds.). pp. 7375. Wallingford, UK. CABI Publishing.
Stock, S.P., Rivera-Orduno, B. & Flores-Lara, Y. 2009. Heterorhabditis sonorensis n. sp. (Nematoda: Heterorhabditidae), a natural pathogen of the seasonal cicada Diceroprocta ornea (Walker) (Homoptera: Cicadidae) in the Sonoran desert. Journal of Invertebrate Pathology 100: 175-184.
Sturhan, D. 1999. Prevalence and specificity of entomopathogenic nematodes in Germany. In: Application and Persistence of Entomopathogenic Nematodes (L. Gwynn, P.H. Smits, C. Griffin, R.-U. Ehlers, N. Boemare & J.P. Masson. Eds.). pp. 123132. European Commission, DG XII, Luxembourg.
Tamiru, T., Waeyenberge, L., Hailu, T., Ehlers, R.-U., PÙZA, V. & MRÂCEK, Z. 2012. Steinernema ethiopiense sp. n. (Rhabditida: Steinernematidae), a new entomopathogenic nematode from Ethiopia. Nematology 14: 741-757.
Tamura, K., Peterson, D., Peterson, N., Stecher, G., Nei, M. & Kumar, S. 2011. MEGA 5: Molecular Evolutionary Genetics Analysis using Maximum Likelihood, Evolutionary Distance, and Maximum Parsimony Methods. Molecular Biology and Evolution 28: 2731-2739.
Thompson, J.D., Gibson, T.J., Plewniak, F., Jeanmougin, F. & Higgins, D.G. 1997. The CLUSTAL_X windows interface: flexible strategies for multiple sequence alignment aided by quality analysis tools. Nucleic Acid Research 25: 4876-4882.
van den Wollenberg, A.L. 1977. "Redundancy Analysis. An alternative to canonical correlation analysis". Psychometrika 42: 207-219.
WATURU, C.N. 1998. Entomopathogenic nematodes (Steinernematidae and Heterorhabditidae) from Kenya. PhD dissertation, University of Reading, United Kingdom.
White, G.F. 1927. A method for obtaining infective nematode larvae from culture. Science 66: 302-303.
Yoshida, M., Reid, A.P., Briscoe, B.R. & Hominick, W.M. 1998. Survey of entomopathogenic nematodes (Rhabditida: Steinernematidae and Heterorhabditidae) in Japan. Fundamental of Applied Nematology 21: 185-198.
Zadji L., Baimey, H., Afouda, L., Houssou, F.G., Waeyenberge, L., de Sutter, N., Moens, M. and Decraemer, W. Первые данные по распределению энтомопатогенных нематод (Rhabditida: Steinernematidae и Heterorhabditidae) в Южном Бенине.
Резюме. Впервые проведено обследование почв пяти департаментов южной (Гвинейской) зоны в Южном Бенине на присутствие почвенных энтомопатогенных нематод (ЭПН). Из 84 исследованных природных и агроэкосистем из 280 собранных проб почвы, в 26 (31.0%) и 32 (11.4%), соответственно, были обнаружены ЭПН. Определение ЭПН было основано на анализе последовательностей ITS rDNA, а также морфологических и морфометрических исследованиях. Было обнаружено два вида ЭПН: Heterorhabditis sonorensis и H. indica. Это первое сообщение о H. sonorensis с момента первого обнаружения в пустыне Сонора в Мексике. Heterorhabditis sonorensis оказался наиболее распространенным видом, показывая предпочтение к полузакрытым пространствам, вроде цитрусовых плантаций, фруктовых посадок или древесных насаждений, при содержании песка и органического вещества в пределах 53.6-89.5% и 0.1-4.7%, соответственно, и pH от кислого (4) до нейтрального (7.1). ЭПН не обнаруживались в культивируемой почве полей (под кукурузой, кассавой, арахисом и бобами) и образцах почвы с содержанием песка менее 50%. Heterorhabditis indica встречался в цитрусовых садах и фруктовых посадках на кислых песчаных почвах или песчаных суглинках (pH = 5.4-6.4), но не покрытых лесом площадях. Дискриминантный анализ выявил несколько основных факторов среды, определяющих распределение ЭПН в почвах Южного Бенина: географическая долгота местности, содержание в почве органического вещества, текстура почвы (содержание песка, глины). По результатам анализа этих факторов было показано, что H. sonorensis и H. indica предпочитают почвы с высоким содержанием песка или органического вещества и тяготеют к восточных регионам страны. Не было выявлено видоспецифичных особенностей распределения каждого из двух выявленных видов.
