Stimulation of Nematode-Destroying Fungi by Organic Amendments Applied in Management of Plant Parasitic Nematode
A screenhouse experiment was conducted to evaluate the effect of cow manure, chicken manure and their combinations on nematode destroying fungi, nematode community and growth of tomato (Solanum lycopersicum L.). The amendments were applied at the rate of 5% w/w in all the treatments. Isolation of nematode destroying fungi was done using the soil sprinkle technique. Nematodes were extracted from soil using the modified Baermann technique. Tomato growth was estimated through plant height and dry weight. Application of the organic amendments resulted in significant differences (p≤0.05) in occurrence of nematode destroying fungi amongst the treatments. The nematode destroying fungi occurred at frequencies of 50, 29.4, 17.6 and 2.9% in soil amended with chicken manure, cow/chicken combination, cow manures and the control, respectively. Eight species of nematode destroying fungi were identified in this study. The fungus Arthrobotrys oligospora (Fresenius) was most dominant fungus in all the treatments including control pots with an isolation frequency of 38.2%. Addition of organic amendments into the soil also resulted in an increase of bacterial and fungal feeding nematodes and reduction of plant parasitic nematodes. Specifically there was a 225, 96 and 62% increase in bacterial feeding nematodes and 391, 96 and 74% increase in fungal feeding nematodes in soil amended with chicken manure alone, combination of chicken and cow manure alone in that order. Numbers of plant-parasitic nematodes were 92% lower in soil treated with chicken manure compared to the control. Plant height and leaf widths were highest in plants treated with combination of cow and chicken manures. The plants mean dry weight were 6.6, 5.6, 2.0 and 1.5 in combination of chicken and cow manure, chicken manure alone, cow manure alone and control, respectively. This study has therefore, revealed that organic amendments stimulate the occurrence of nematode destroying fungi in the soil and also reduce plant parasitic nematodes. In addition, the combination of cow and chicken manure stimulates plant growth.
Although nematodes are generally regarded as silent enemies, losses of up to
80% have been associated with them in vegetable fields that are heavily infested
(Siddiqi, 2000; Kaskavalci, 2007).
For decades, the control of plant-parasitic nematodes has mainly depended on
chemical nematicides (Akhtar and Malik, 2000). Although,
nematicides are efficient and fast-acting, they are currently being reappraised
with respect to the environmental hazards associated with them. In addition
they are relatively unaffordable to many small-scale farmers. The persistent
pressure on farmers to adopt strategies that do not pollute the environment
has increased urgency in the search for alternative sustainable methods to regulate
plant parasitic nematodes (Pinkerton et al., 2000;
Mashela et al., 2008).
One of the alternative strategies for management of plant pararsitic nematodes
is the application of organic amendments in the soil (Agyarko
and Asante, 2005). Oka et al. (2000) pointed
that organic amendments have consistently been shown to have beneficial effects
on soil nutrients, soil physical conditions, soil biological activity and thereby
improving the health of plants and reducing populations of plant parasitic nematodes.
On the other hand, populations of free-living nematodes have also been shown
to increase rapidly following the addition of organic substrates (Akhtar
and Malik, 2000). Kimenju et al. (2004) reported
that application of organic amendments stimulated the activity of natural antagonists
of plant parasitic nematodes. However, the available reports do not mention
the contribution of nematode destroying fungi in the reduction of plant parasitic
nematodes yet they are known to destroy nematodes in the soil. In vitro experiments
have shown that nematode destroying fungi increase in numbers or activity when
organic substrates are incorporated into the soil (Gomes
et al., 2000; Timm et al., 2001). In
a related study, Jaffee (2006) reported that alfalfa
(Medicago sativa L.) leaves enhanced the populations of Dactylellina
candidum (Nees) but the study did not mention other nematode destroying
Nematode destroying fungi are natural enemies of plant parasitic nematodes
(Nordbring-Hertz et al., 2002). Some of these fungi
use adhesive conidia, branches, knobs and mycelia to parasitize nematodes. These
devices are used to capture and destroy nematodes by means of an adhesive layer
covering part or all of the device surfaces (Yang et al.,
2007). Other fungi immobilize or kill nematodes by releasing toxins. This
group of fungi has recently drawn much attention because of their potential
as biological control agents of nematodes that are parasitic on plants and animals
(Jansson and Persson, 2000; Sanyal,
2000; Masoomeh et al., 2004).
This study was undertaken with the aim of determining the effects of chicken manure, cow manure and their combinations on occurrence of nematode-destroying fungi, nematode community in general and plant growth.
MATERIALS AND METHODS
Screenhouse experiments were carried out in the period between August 2007
and April 2008 at the University of Nairobi, Kenya. The amendments namely chicken
manure, cow manure and their combinations were dried at 70°C until a constant
weight was achieved. The amendments were then applied at the rate of 5% w/w
(Kimenju et al., 2004) into soil that was naturally
infested with nematodes and nematode-destroying fungi. The pots were irrigated
and two-week old tomato seedlings (cv. Moneymaker) were transplanted into them.
Un amended soil was used as a control. Treatments were arranged in a completely
randomized design with five replications.
Isolation of nematode destroying fungi was done using the soil sprinkle technique
as described by Jaffee et al. (1996). Tap water
agar was prepared by dissolving 20 g of agar in 1 L of tap water. The medium
was autoclaved and cooled to 45°C before amending it with 0.1 g LG1
of streptomycin sulfate to suppress bacterial growth. Approximately 1 g of soil
from each sampling point was sprinkled onto the surface of water agar in petri
dishes. Plant parasitic nematodes were added into the petri dishes as baits.
The plates were incubated at room temperature and observed daily from the third
week up to the 6th week under a microscope at low (40 x) magnification. The
examination was focused on trapped nematodes, trapping organs and conidia of
the nematode destroying fungi that grew from the soil. Nematodes were extracted
from 200 cm3 soil using the modified Baermann funnel technique as
described by Hooper et al. (2005). The nematodes
were identified to genus levels using the descriptions described by Bongers
and Bongers (1998) and Mai and Mullin (1996) and then
counted. Growth of tomato plants was monitored at the 4th and 7th weeks by assessing
the plant height, leaf width- apical leaf of 3rd branch, internodal length (between
3rd and 4th branch) and the type of flower/flowering pattern. Shoot and root
dry weights were taken at the end of the experiment after drying the samples
at 70°C to constant mass.
All the data were tested for homogeneity and subjected to analysis of variance
(Kindt and Coe, 2005). Where the overall F test was significant,
means were compared using the Tukey Honest Significance test (HSD) at p≤0.05.
The differences in occurrence of nematode destroying fungi was significant (p = 0.05) among the treatments with means of 3.4 in chicken manure alone, 2.0 in combinations of cow and chicken manure, 1.2 in cow manure and 0.2 in control (Table 1).
The nematode destroying fungi occurred in frequencies of 50, 29.4, 17.6 and 2.9% in chicken manure, cow/chicken combination, cow manures and control, respectively (Fig. 1). Out of the nematode destroying fungi isolated, 71% were in the category of nematode trapping fungi while 29% of them were endo-parasitic. 50% of all the nematode destroying fungi were recorded in the soil treated with chicken manure. The mean richness of nematode destroying fungi was 3.4 in chicken manure and 0.2 in the control. Combinations of cow and chicken manure had a mean richness of 2.0 while cow manure had 1. Soil amended with chicken manure was the most diverse in terms of nematode destroying fungi with mean shannon of 1.2. Combinations of cow and chicken was 0.64 diverse followed by cow manure alone with, 0.28 while the control had 0.
Of all the fungal isolates, Arthrobotrys oligospora (Fresenius) was
most dominant and its occurrence was significantly different (p≤0.05) across
the treatments with an isolation frequency of 38.2%.
Effect of organic amendments on occurrence of nematode destroying fungi
Effect of organic amendments on occurrence of nematode destroying fungi
The other nematode destroying fungi had isolation frequencies of 26.5, 17.6,
8.8, 5.9 and 2.9% in Harposporium aungulilae (Lohde), Arthrobotrys
dactyloides (Drechsler), Monacrosporium cionopagum (Drechsler),
Adhesive hyphae and A. superba (Corda), respectively.
Arthrobotrys superba, H. aungulilae, M. cionopagum
and the Adhesive hyphae did not seem to respond to the treatments. The occurrence
of Athrobotrys dactyloides was significantly different (p = 6.837H10G05)
in all the treatments. Soils amended with chicken manure alone were characterized
by presence of A. oligospora, H. angullilae, A. superba,
A. dactyloides, M. cionophagum and nematode trapping structures
such as adhesive hyphae. Soils amended with the combination of chicken
and cow manure harbored populations of A. oligospora, A. dactyloides,
H. angullilae and Adhesive hyphae. Nematode destroying
fungi, A. oligospora, H. angullilae and A. dactyloides were
isolated from soils amended with cow manure alone.
On nematode community, organic amendments resulted in a significant change
in composition of the nematode community (Fig. 2). Application
of the organic amendments caused an increase in numbers of bacterial and fungal
feeding nematodes. There was an increase of 225, 96 and 62% in bacterial feeding
nematodes in soils amended with chicken manure, combination of chicken and cow
manure and cow manure, respectively. Similarly, application of chicken manure
alone, combination of chicken and cow manure and cow manure alone led to a 391,
96 and 74%, respective increase in fungal feeding nematodes. In addition, application
of the amendments suppressed the numbers of plant parasitic nematodes. Chicken
manure led to 92% reduction in plant parasitic nematodes compared to 73 and
55% reduction after application of chicken and cow manure in combination and
cow manure alone, respectively. The populations of predacious nematodes increased
in response to application of the organic amendments. The highest number of
predacious nematodes was recorded in soils amended with chicken manure.
Influence of organic amendments on nematode community structure
Effect of organic amendments on plant height, leaf width, number of
branches, internode lengths and shoot widths
* Growth parameters not affected by the treatments
Further results showed that organic amendments caused significant differences
(p≤0.05) in the plant height. The mean heights were 46.8, 34.8, 31.5 and 32.1
cm in combinations of cow and chicken manure, chicken manure alone, cow manure
alone and control, respectively (Table 2). The number of branches
had significantly increased in all the treatments in the 7th week than 4th week
(p = 2.2H10G16). In the 7th week, the plants were significantly taller
and with thicker shoot than in 4th week. Flower induction was earliest and more
pronounced in tomato plants grown in soil amended with chicken manure, chicken/cow
manure, cow manure and least in control pots. The combination of chicken and
cow manure had the highest mean dry weight of 6.6 kg. Chicken manure alone recorded
5.6, cow manure alone 2.0 and 1.5 kg in control in descending order.
A similar trend was observed in the repeat experiment as shown in Table
3. The diversity and richness of nematode destroying fungi was higher in
soil amended with chicken manure alone, combination of chicken and cow manure
and cow manure alone as compared to the control. Plant parasitic nematode numbers
were significantly lower (p = 3.039H10G09) in soils amended with
chicken manure alone and all the other amendments compared to the control.
Effect of organic amendments on plant height, flower production, diversity
and richness of nematode destroying fungi and plant parasitic nematodes
PPN: Plant Parasitic Nematodes
Plant growth parameters were significantly higher in soils with organic amendments
compared to the control. The plant height and mean dry weight were higher in
chicken manure treatments, followed by a combination of cow and chicken manure,
cow manure and least in the control. Amendments with chicken manure also recorded
more flowers than cow manure alone and control.
In summary, the results from this study indicate that the organic amendments stimulated the occurrence of nematode destroying fungi, changed the nematode community by reducing the plant parasitic nematodes. In addition, amendments enhanced plant growth vigor. Specifically, chicken manure alone enhances the diversity and richness of nematode destroying fungi and reduction of plant parasitic nematodes. The combination of chicken and cow manure was the best in stimulation of plant growth.
This study has revealed that organic amendments and especially chicken manure
stimulated build-up of nematode destroying fungi, Arthrobotrys oligospora,
Harposporium angullilae, A. superba, A. dactyloides, Monacrosporium
cionopagum and related nematode-destroying structures in the soil.
The organic amendment supplies the needed food sources to the nematode trapping
fungi hence their enhancement. This is supported by the findings of Timm
et al. (2001), who suggested that the increase in nematode-trapping
fungi after addition of organic amendment is due to available carbon and energy
from the organic amendment and nitrogen from consumed nematodes. In a related
study, Jaffee (2006), also showed that organic amendments
enhanced build-up of nematode-trapping fungi Dactylellina candidum (Nees)
though no other fungi were mentioned and are thought to be influenced differently
depending on their feeding mechanism (parasitic of saprophytic).
The fungi Arthrobotrys oligospora was the most enhanced in this study
by the organic amendments and especially by the chicken manure. Probably compounds
containing ammonia also enhance the population of nematode destroying fungi.
From this study, chicken manure and then combination of chicken and cow manures
stimulated the buildup of nematode destroying fungi as well as reducing the
population of plant parasitic nematodes. The biological control efficacy of
ammonia like the one found in chicken manure, has been shown to be equivalent
to that of 1,3-D, chloropicrin, metam-sodium, cadusafos, or metam-sodium (Yucel
et al., 2002; Koenning et al., 2003).
In a related study (Jaffee, 2004) absent in the literature, reported that Arthrobotyrs
oligospora was enhanced by large quantities of alfalfa amendments. Alfalfa
leaves supplied nitrogen in the soil which in turn increased the population
of A. oligospora in the soil. Viaene et al.
(2006) reported that A. oligospora which immobilizes nematodes by
using mycelial traps such as non-adhesive knobs and constricting, rings, could
be used as a biological control agent of plant parasitic nematode. Other species
of Arthrobotrys have been used as biological control of plant parasitic
nematodes with recommendable success (Kiewnick et al.,
2004). What is not clear is whether it is the nematode destroying fungi
that reduces the population of plant parasitic nematodes in the soil. Although,
strong indications of nematode trapping fungi suppressing nematodes have been
demonstrated in the laboratory using Petri dishes (Elshafie
et al., 2006), it is till not clear with field and green house experiments
(Jaffee and Strong, 2005; Jaffee et
It has been demonstrated in this study that application of organic soil amendments
resulted in changes in nematode community structure by increasing the abundance
of free-living nematode populations and suppressing plant parasitic nematodes.
Application of soil amendments is becoming a conventional practice that helps
in the control of nematodes and other soil-borne diseases. Comprehensive studies
like those of Koenning et al. (2003) have revealed
the nematicidal potential of organic products used as soil amendments. When
incorporated into the soil, organic substrates undergo biologically mediated
decomposition to release NH4+, formaldehyde, phenols and
volatile fatty acids, among other compounds (Wang et al.,
2004). The involvement of soil micro-organisms in nematode control in amended
soils has been confirmed by the fact that soil irradiation disrupts the nematicidal
effect of these amendments (Kaskavalci, 2007). It has
been established that application of organic substrates leads to build-up of
micro-organisms which serve as are food substrates for free-living nematodes
hence their build-up. Populations of free-living nematodes such as bacteriovores,
fungivores and predacious have been shown to rapidly increase following the
addition of organic amendments (Akhtar and Malik, 2000;
Jaffee, 2002). In addition, free-living nematodes may
accelerate the decomposition of soil organic matter and increase mineralization
of nitrogen and phosphorous thus triggering a chain reaction that favours their
build-up (Widmer and Abawi, 2000; Kimenju
et al., 2004). Yucel et al. (2002)
categorical that organic amendments that have high nitrogen content and release
ammonia upon decomposition are more effective in nematode suppression.
In this study plants grown on soil amended with organic substrates grew and
differentiated faster reaching flowering stage earlier than the control. Unlike
the nematode destroying fungi and the nematode communities which were enhanced
by the chicken manure, the growth of the plants was more enhanced by the combination
of chicken and cow manures. The increase in growth is attributed to the release
of macro - and micronutrients, plant growth regulators and stimulation of beneficial
micro flora such as the mycorrhizae fungi (Kaskavalci, 2007).
In the current study, the plants grown on organic amendments were taller and
heavier compared to the control. Since dry weight is used to estimate productivity
(Opik et al., 2005) productivity would be expected
to be higher in plants treated with organic amendments. Though the inorganic
fertilizers were not tested in the current study, the findings are in agreement
with Widmer and Abawi (2000), who reported that plants
grown in plots receiving organic manures were always larger than those receiving
inorganic fertilizers. In a separate study, weights of tomato plants grown in
the ammonia-treated soils were about six fold greater than the control. Amendments
therefore represent important resource for the improvement of soil fertility
because decomposed materials ultimately serve as sources of nutrients for plants
and thus improve crop yields.
The increase in crop vigour may partly be attributed to reduced plant-parasitic
nematode populations, but nutrients availability cannot be ignored. In a earlier
study, decrease in populations of parasitic nematodes has been associated with
increased in crop yield (Zolda, 2006). In turn, the decline
in plant parasitic nematodes in this study could probably be attributed to the
high number of nematode destroying fungi. The association between nematode-trapping
fungi, organic matter, plant growth and nematodes community is complex. It would
be difficult to conclude that the increase of nematode destroying fungi would
lead to automatically reduction of plant parasitic nematodes hence health plants.
Akhtar and Malik (2000) suggested that free-living nematodes
reproduce rapidly when presented with organic substrate and play an important
role in recycling of plant nutrients making them available to plants. Such organic
substrates again have been seen to support high numbers of nematode destroying
fungi and reduced populations of plant parasitic nematodes. Therefore, low numbers
of plant parasitic nematodes coupled with high numbers of nematode destroying
fungi and high nutrient levels in the soil has a positive effect to plant growth.
It would be impossible to attribute the performance of the crop to either of
them. In order to access the contribution of nematode destroying fungi, there
is need to address the quantification and efficacy methods (Jaffee,
2006). More study should be devoted to the correlation between populations
of nematode destroying fungi, plant parasitic nematodes and the actual plant
This study has demonstrated the potential of organic amendments in stimulation of nematode destroying fungi for the management of plant-parasitic nematodes. The occurrence and diversity of nematode destroying fungi was associated with the decreased number of plant parasitic nematodes. Amendments cause improved plant growth and changes the nematode community structure particularly leading to decreased plant parasitic nematodes. However, such alternative nematode management strategies are unlikely to be as effective and fast-acting as nematicides. Although nematicides would reduce the plant parasitic nematodes, other environmental and soil fertility issues arise. Therefore, sustainable management of plant-parasitic nematodes from addition of organic amendments to the soil overrides all other considerations.
The researchers are grateful to the project on Conservation and Sustainable Management of Belowground Biodiversity (CSM-BGBD) Project, Grant number GF/2715-02 and DAAD in country study programme No. A/07/08932 for financial support towards a Ph.D study. The University of Nairobi is acknowledged for providing laboratory equipment and space.
Agyarko, K. and J.S. Asante, 2005. Nematode dynamics in soil amended with neem leaves and Poultry manure. Asian J. Plant Sci., 4: 426-428.
Direct Link |
Akhtar, M. and A. Malik, 2000. Roles of organic soil amendments and soil organisms in the biological control of plant-parasitic nematodes: A review. Bioresour. Technol., 74: 35-47.
Bongers, T. and M. Bongers, 1998. Functional diversity of nematodes. Applied Soil Ecol., 10: 239-251.
Elshafie, A.E., R. Mueini, S. Al-bahry, A.Y. Akindi and I. Mahmoud et al., 2006. Diversity and trapping efficiency of nematophagous fungi from Oman. Phytopathol. Mediterr, 45: 266-270.
Direct Link |
Gomes, A.P.S., M.L. Ramos, R.S. Vasconcellos, J.R. Jensen and M.C.R. Vieira-Bressan et al., 2000. In vitro activity of Brazilian strains of the predatory fungi, Arthrobotrys spp. on free-living nematodes and infective larvae of Haemonchus placei. Mem. Inst. Oswaldo Cruz, Rio de Janeiro, 95: 873-876.
Hooper, D.J., J. Hallmann and S.A. Subbotin, 2005. Methods for Extraction, Processing and Detection of Plant and Soil Nematodes. In: Plant Parasitic Nematodes in Subtropical and Tropical Agriculture, Luc, M., R.A. Sikora and J. Bridge (Eds.). 2nd Edn., CAB International Publisher, UK., ISBN: 9781845931445, pp: 53-86.
Jaffee, B.A. and D.R. Strong, 2005. Strong bottom-up and weak top-down effects in soil: Nematode-parasitized insects and nematode-trapping fungi. Soil Biol. Biochem., 317: 1011-1021.
Jaffee, B.A., 2002. Soil cages for studying how organic amendments affect nematode-trapping fungi. Applied Soil Ecol., 21: 1-9.
Jaffee, B.A., 2006. Interactions among a soil organic amendment, nematodes and the nematode-trapping fungus Dactylellina candidum. Phytopathology, 96: 1388-1396.
Jaffee, B.A., D.R. Strong and A.E. Muldoon, 1996. Nematode trapping fungi of natural shrubland: Tests for food chain involvement. Mycologia, 88: 554-564.
Direct Link |
Jaffee, B.A., J.L. Bastow and D.R. Strong, 2007. Suppression of nematodes in coastal grassland. Soil. Biol. Ferti. Soils, 44: 19-26.
Jansson, H. and C.O. Persson, 2000. Growth and capture activities of Nematophagous fungi in soil visualized by low temperature scanning electron microscopy. Mycologia, 92: 10-15.
Direct Link |
Kaskavalci, G., 2007. Effects of soil solarization and organic amendment treatments for controlling Meloidogyne incognita in tomato cultivars in Western Anatolia. Turk. J. Agric. For., 31: 159-167.
Direct Link |
Kiewnick, S., A. Mendoza and R.A. Sikora, 2004. Efficacy of Paecilomyces lilacinus strain 251 for biological control of the burrowing nematode Radopholus similes. J. Nematology, 36: 326-327.
Kimenju, J.W., D.M. Muiru, N.K. Karanja, M.W. Nyongesa and D.W. Miano et al., 2004. Assessing the role of organic amendments in management of root-knot nematodes on common bean, Phaseolus vulgaris L. Trop. Microbiol. Biotechnol., 3: 14-23.
Direct Link |
Kindt, R. and R. Coe, 2005. Tree Diversity Analysis. A Manual and Software for Common Statistical Methods for Ecological and Biodiversity Studies. 1st Edn., World Agro-Forestry Center (ICRAF)., Nairobi, pp: 203.
Koenning, S.R., K.L. Edmisten, K.R. Barker, D.T. Bowman and D.E. Morrison, 2003. Effects of rate and time of application of poultry litter on Hoplolaimus Columbus on cotton. Plant Dis., 87: 1244-1249.
Mai, W.F. and P.G. Mullin, 1996. Plant-Parasitic Nematodes: A Pictorial Key to Genera. 5th Edn., Cornell University Press, Ithaca, USA., ISBN: 0801431166.
Mashela, P.W., H.A. Shimelis and F.N. Mudau, 2008. Comparison of the efficacy of ground wild cucumber fruits, aldicarb and fenamiphos on suppression of Meloidogyne incognita in tomato. Phytopathology, 156: 264-267.
Masoomeh, S.G., R.A. Mehdi, R.B. Shahrokh, E. Ali and Z. Rasoul et al., 2004. Screening of soil and sheep faecal samples for predacious fungi: Isolation and characterization of the nematode-trapping fungus Arthrobotrys oligospora. Iran. Biomed., 8: 135-142.
Direct Link |
Nordbring-Hertz, B., H.B. Jansson and A. Tunlid, 2002. Nematophagous Fungi: Encyclopedia of Life Sciences. Macmillan Publishers Ltd., London.
Oka, Y., H. Koltai, M. Bar-eyal, M. Mor, E. Sharon, I. Chet and Y. Spiegel, 2000. New strategies for the control of plant-parasitic nematodes. Pest Manage. Sci., 56: 983-988.
Opik, H., S.A. Rolfe and A.J. Willis, 2005. The Physiology of Flowering Plants. 4th Edn., Cambridge University Press, Cambridge, UK., ISBN-13: 978-0-521-66251-6 Pages: 392..
Pinkerton, J.N., K.L. Ivors, M.L. Miller and L.W. Moore, 2000. Effect of solarozation and cover crops on populations of selected soil borne plant pathogens in Western Oregon. Plant Dis., 84: 952-960.
Sanyal, P.K., 2000. Screening for Indian isolates of predacious fungi for use in biological control against nematode parasites of ruminants. Vet. Res. Commun., 24: 55-62.
Siddiqi, M.R., 2000. Tylenchida Parasites of Plants and Insects. 2nd Edn., CAB International, Wallingford, UK., ISBN: 085199-202-1, pp: 848.
Timm, L., D. Pearson and B. Jaffee, 2001. Nematode trapping fungi in conventionally and organically managed corn-tomato rotations. Mycologia, 93: 25-29.
Direct Link |
Viaene, N., L.D. Coyne and B.R. Kerry, 2006. Biological and Cultural Management. In: Plant Nematology, Perry, R.N. and M. Moens (Eds.). CAB International, Wallingford, UK., ISBN: 978-90-5989-197-5, pp: 346-369.
Wang, K.H., R. McSorley and R.N. Gallaher, 2004. Effect of Crotalaria juncea amendment on squash infected with Meloidogyne incognita. J. Nematol., 36: 290-296.
Direct Link |
Widmer, T.L. and G.S. Abawi, 2000. Mechanism of suppression of Meloidogyne hapla and its damage by a green manure of Sudan grass. Plant Dis., 84: 562-568.
Yang, Y., E. Yang, A. Zhiqiang and X. Liu, 2007. Evolution of nematode-trapping cells of predatory fungi of the Orbiliaceae based on evidence from rRNA-encoding DNA and multiprotein sequences. Proc. Natl. Acad. Sci., 104: 8379-8384.
Direct Link |
Yucel, S., I.H. Elekcioglu, A. Uludag, C. Can, M.A. Sogut, A. Ozarslandan and E. Aksoy, 2002. The second year results of Methyl Bromide alternatives in the Eastern Mediterranean. Proceedings of the Annual International Research Conference on Methyl Bromide Alternatives and Emissions Reductions, November 5-8, 20002, Orlando, Florida, USA., pp: 1-4.
Zolda, P., 2006. Nematode communities of grazed and ungrazed semi-natural steppe grasslands in Eastern Austria. Pedobiol., 50: 11-22.