NE171: Biologically Based IPM Systems for Management of Plant-Parasitic Nematodes
- Duration:
- October 01, 1999 to September 30, 2004
- Administrative Advisor(s):
-
Louis A. Magnarelli
(CONH)
- NIFA Reps:
-
Robert M. Nowierski
Statement of Issue(s) and Justification:
Modern agriculture continues to rely on technological advances and off-farm inputs to increase yields and profitability. In particular, most crops rely heavily on fertilizers and pesticides to maintain acceptable production levels.Plant-parasitic nematodes are important pathogens on most food and fiber crops and without appropriate controls will cause loss of yield and quality. Chemical nematicides have been the primary management tool for over fifty years but many products have now been removed from the market or are under review. There is an urgent need for the development of alternative control options. Such work is necessary to develop environmentally sound agricultural systems that minimize chemical use while maintaining high production standards.
Related, Current, and Previous Work:
Crop rotation, soil amendments, genetic resistance:Nematode control tactics such as rotation, cover cropping, green manuring, organic amendments and plant resistance have been evaluated as alternatives to chemical nematicides. Crop rotation is perhaps the oldest and most effective cultural practice for controlling plantparasitic nematodes (Good, 1968). Rotation crops that reduce nematode populations have been shown to serve as either nonhosts, less suitable hosts, or as antagonistic plants (Johnson, 1982; Trivedi and Barker, 1986; Merwin and Stiles, 1989; Halbreridt, 1996). Nonhosts may simply not be parasitized and have an effect similar to fallow. Antagonistic plants may produce compounds which stimulate hatch without allowing reproduction or actively reduce nematode populations by the production of nematicidal or toxic compounds (Halbrendt, 1996). Nematode-suppressive plants which produce these compounds may be utilized to deliver them by means of rotation, inter-cropping, cover cropping, or soil amendment with either green manure or dry plant residue.
A number of rotation or cover crops which reduce nematodes more than fallow have been identified (Halbrendt, 1996; Ko and Schmitt, 1996; LaMondia, 1997; Rodriguez-Kabana, 1992). Crop rotations which include these antagonistic or allelopathic plants may be thought of as active and those that are simply non-hosts as passive (Rodriguez-Kabana, 1992). The list of plants antagonistic to nematodes has grown but research on the mechanism of allelopathy, resistance or antagonism has not kept pace. While an understanding of the mechanism involved is not necessary for control by either resistance or allelopathy, this information would be important for selection and development of breeding lines with increased efficacy.
Two promising grain crops for nematode reduction by rotation are diploid `Saia' oats (Avena strigosa) and sorgho-sudangrass (Sorghum bicolor x S. sudanense). These crops have been reported to be poor hosts of lesion and root-knot nematodes (Colbran, 1979, Fay and Duke, 1977). Grain or grass rotations and companion crops conserve soil, reduce compaction and increase water infiltration into soil (Newenhouse and Dana, 1989). The use of oats and sorghum as allelopathic rotation or companion crops can suppress a number of weed species (Neustruyeva and Dobretsova, 1972, Putnam and DeFrank, 1983). Some oat accessions exuded up to three times as much scopoletin, a root growth inhibiting compound, as standard 'Garry' oats (Fay and Duke, 1977). Oats and sorghum also have been shown to produce fungicidal root exudates toxic to soilborne fungi such as Fusarium and Gaumannomyces (Crombie and Crombie, 1986, Nimbal et al., 1996). Recently, resistance to lesion nematodes has been associated with greater production of avenocin in 'Saia' oats than in susceptible oats (B. B. Brodie, pers. comet.).
Because of the importance of developing non-chemical nematode controls, a number of antagonistic plants have recently been bred for increased efficacy against nematodes and other soilborne pathogens. These include selected varieties of Brassica spp and Tagetes spp. The nematode-suppressive effects of marigold (Tagetes spp.) have been documented for over 50 years (Tyler, 1938; Steiner 1941). The antagonistic effect is due to toxicity of metabolites in the root exudates (Siddiqui and Alarm 1987a, b; 1988a). Although the presence of nematicidal compounds has been well documented, there are conflicting reports concerning the efficacy for suppression of a number of nematodes and the compounds responsible (Gommers et al., 1980; Gommers and Bakker, 1988). The differential ability of Tagetes species to suppress nematodes may be due to variation in species, cultivars, edaphic factors, nematode populations, and the active nematicidal compounds (Eisenback, 1987; Arevalo and Ko, 1989; Alarn et al., 1990). Recently, marigold cultivars have been specifically selected for increased nematicidal efficacy.
A number of leguminous crops also have been reported to have nematode suppressive properties. Vicente and Acosta (1987) reported that velvetbean root exudates were nematicidal and Rodriguez-Kabana (1992) suggested that bacteria in the velvetbean rhizosphere were antagonistic to cyst and root-knot nematodes.
Other crops such as canola (rapeseed, Brassica napus L. and B. campetris L), also have been implicated in reducing soil densities of nematodes (Davis et al. 1993; Mojtahedi et al. 1993). These plants synthesize large quantities of sulfur-containing glucosinolates in all tissues (Sang et al. 1984). When these plants are incorporated into the soil as a green manure, the glucosinolates hydrolyze to fungicidal and nematicidal isothiocyanates (Ettlinger et al. 1968). The level of nematode control has been correlated with glucosinolate concentration in plant extracts (Jing and Halbrendt, 1994). The incorporation of canola shoots to soils heavily infested with Meloidog)ne chitwoodi reduced nematode populations more than fallow treatments (Mojtahedi et al. 1993), and the application of canola meal significantly reduced populations of P. neglectus and subsequent Verticillium wilt in potato (Davis et al. 1993).
Additional alternative practices include soil amendments and mulches. Green manure treatments with certain nematode antagonistic plants may provide even greater nematode control than when used solely as a cover or rotation crop. (Siddiqui and Alarm 1987c, 1988b). Composts have been widely used as peat substitutes in the nursery industry, resulting in disease suppression (Hoitink and Grebus, 1994). The mechanisms put forth for this suppression (Alam and Jairajpuri, 1990) have included: changes in the physical and chemical properties of soil, including nutrition and the production of nematotoxic substances released directly or by microbial breakdown; changes in the microbial ecology of soil that affect antagonistic organisms or the release of antagonistic microbial metabolites; and the induction of plant resistance or tolerance to nematodes as well as the induction of systemic acquired resistance (Zhang et al, 1996; Zhou and Paulitz, 1994). Lail~fondia et al. (in press) demonstrated over 4 years in field microplot studies that soil amendment with spent mushroom compost reduced potato early dying severity by 24% (AUDPC for symptomatic leaves), increased marketable tuber yields by 94%, increased leaf photosynthesis by 43%, and reduced lesion nematode densities in subsequent rye cover crops by 48%.
Plant resistance is the most economical and environmentally safe means of controlling plant-parasitic nematodes. Host plant resistance and tolerance are important when crops must be grown in the presence of potentially damaging populations of nematodes. Resistance refers to the suppressive effects of plant genes on nematode development and/or reproduction (Trudgill, 1991). Tolerance refers to the ability of a plant to grow and produce an acceptable yield while supporting moderately large numbers of plant parasitic nematodes. Ideally, plant resistance and tolerance could be combined.
Most host plant resistance has been identified for specialized host-plant relationships, such as the sedentary endoparasitic cyst and root-knot nematodes, but resistance to other nematodes such as the migratory endoparasite Pratylerrchus, also has been identified (Potter and Dale, 1994). Mechanisms of resistance to nematodes include both constitutive plant compounds and factors induced by nematode infection. Resistant plants may contain toxic compounds such as alpha terthienyl, present in marigolds (Veech, 1981), compounds which reduce egg hatch (Gapasin, 1988), or lectins which may affect host-finding ability (Martian-Mendoza et al., 1992). Incompatible host response to nematodes ranges from nonspecific tissue necrosis to necrosis around a feeding site or a hypersensitive response that prevents nematode development (Kaplan and Keen, 1980).
Genes conferring resistance have been identified and incorporated into many crop cultivars. Resistance to root-knot and cyst nematodes in vegetable crops and tobacco have been identified and developed as a part of this project (Thies et al. 1997; LaMondia, 1991). While resistance has been durable in many situations, selection by resistance genes has often resulted in a population shift to nematode races able to overcome plant resistance. It will be important to integrate resistance with other control tactics to maintain nematode control and reduce selection pressure against resistance gene(s).
Biological control agents:
Suppression of plant-parasitic nematodes with nematode predators, parasites or disease agents is a desirable alternative to chemicals. Deploying and managing biocontrols will likely become increasingly important components of integrated pest management programs and sustainable agricultural systems. Biological control agents occur in diverse taxa. and include nematode trapping or endoparasitic fungi, predatory nematodes, arthropods (e.g. mites and collembola), bacterial parasites, and predatory protozoa. Understanding this diversity will be a critical step in adapting management practices to realize the full potential of biological control. However, because of the large number of potential biocontrol agents it is desirable and beneficial to focus efforts on one organism.
Pasteuria penetrans is a promising biological control agent against root-knot nematodes in the southeastern United States and has been selected for detailed studies. The role of P. penetrans in the northern tier of states has not been evaluated. The use of this bacterium to suppress plant-parasitic nematodes has been tested on many crops, mostly in greenhouse pots (Chen and Dickson, 1998). Pasteuria penetrans suppressed Meloidogyne spp. on bean, brinjal, chickpea, cucumber, eggplant, gape, hairy vetch, kiwi, mung, okra, peanut, pepper, rye, soybean, tobacco, tomato, and wheat (Chen and Dickson, 1998). Some isolates of Pasteuria spp. have been reported to suppress Belonolaimus longicaudatus on bermudagrass (Giblin-Davis, 1990), Heterodera avenae and H. zeae on unspecified crops (Bhattacharya and Swarup, 1988), H. cajani on cowpea (Singh and Dhawan, 1994), H. elachista on rice (Nishizawa, 1987), and Xiphinema diversicaudatum on peach (Ciancio, 1995b).
While many strains of Pasteuria are nematode species-specific, cross-genetic suppression of nematodes also has been observed (Mankau and Prasad, 1972; Bhattacharya and Swarup, 1988). Pasteuria penetrans simultaneously reduced population densities of Pratylenchus scribneri and root galls induced by M. javanica and M. incognita in tomato (Mankau and Prasad, 1972). An Indian isolate of P. penetrans parasitized both Heterodera spp. and M. incognita (Bhattacharya and Swarup, 1988). Endospores of P. penetrans were mass-produced on M. incognita and when endospores were incorporated into soil, numbers of cysts of H. avenae on wheat roots were reduced.
A successful example of the biological control potential of P. penetrans for management of root-knot nematodes on peanut was reported recently (Chen, 1996; Chen et al., 1996). Endospores of P. penetrans were incorporated into field microplots in the first year only at 0, 1,000, 3,000, 10,000, or 100,000 endospores/g of soil. Root galls and pod galls were significantly reduced at 100,000 endospores/g of soil in the first year. In the second year, root galls and pod galls were reduced at 10,000 and 100,000 endospores/g of soil. Pod yields increased 58% and 94% at 10,000 and 100,000 endospores/g of soil, respectively (Chen et al., 1996). In the third year, root galls and pod galls were nil at 100,000 endospores/g of soil, and were reduced at 1,000, 3,000, and 10,000 endospores/g of soil. Pod yields were increased 180%, 291%, 221%, and 272% at 1,000, 3,000, 10,000, and 100,000 endospores/g of soil, respectively (Chen et al., unpubl.). Population densities of J2 in soil at harvest also were significantly reduced at 10,000 and 100,000 endospores/g of soil in the third year. Apparently, the establishment and amplification of P. penetrans in the field microplots played an important role in the increased suppression of root-knot nematodes over the 3-year period.
Isolates of Pasteuria spp. failed to suppress populations ofMeloidogyne spp. on sugarcane (Spaull, 1984), Helicotylenchus lobus on turfgrass (Ciancio et al., 1992), and Tylenchulus semipenetrans (Ciancio and Roccuzzo, 1992). A survey in sugarcane fields in South Africa revealed that population densities of Meloidogyne spp. were generally higher in fields infested with P. penetrans and that the level of nematode parasitism was greater at higher nematode densities (Spaull, 1984). On turfgrass, there was no correlation between the population density of Helicotylenchus lobus and the percentage of nematodes with endospores (Ciancio et al., 1992). However, an increase in parasitism was observed 2 months after a 10-fold nematode population growth (Ciancio et al., 1992).
Mode of action: Pasteuria penetrans reduced the number of JZ penetrating roots (Brown and Smart, 1985; Davies et al., 1988a; 1988b; Sekhar and Gill, 1990), number of females in roots (Davies et al., 1991), female fecundity (Bird, 1986; Bird and Brisbane, 1988), number of J2 in soil (Chen et al., 1997c; Davies et al., 1988a; 1988b), and number of eggs on roots (Ahmed and Gowen, 1991; Bird and Brisbane, 1988; Chen et al., 1997c; Weibelzahl-Fulton et al., 1996). Movement and mobility of J2 were reduced and their ability to locate host roots was affected when J2 were encumbered with endospores (Davies et al., 1991; Mankau and Prasad, 1977).
Pasteuria species are gram-positive, dichotomously branched, endospore-forming bacteria with septate mycelium (Mankau and Imbriani, 1975). Most of the species identified to date show great promise as biological control agents of several of the most important plant-pathogenic nematodes. To date four species of the bacterium have been described. These were differentiated by their host preference, developmental characteristics, and size and shape of sporangia and endospores (Sayre and Starr, 1989). Pasteuria ramosa, which parasitizes water fleas of the genera Daphnia, is the type species of the genus (Ebert et al., 1996). The other three species of Pasteuria are parasites of plant-parasitic nematodes: P. penetrans on Meloidogyne spp., P. thornei on Pratylenchus spp., and P. nishizawae on cyst nematodes of the genera Heterodera and Globodera (Sayre and Starr, 1989). The terminal hyphae of the mycelium elongate to form sporangia and eventually endospores. Endospores are nonmotile and resistant to desiccation.
The apparent utility of P. penetrans for biological control of root-knot nematodes has prompted several efforts to produce the organism in culture (Bishop and Ellar, 1991 ; Riese et al., 1988; Previc and Cox, 1992). At present, only limited production of Pasteuria has been attained in vitro. Major hurdles to the development of Pasteuria spp. as a biological agent include the definition and control of events necessary for the formation of infective spores. In the absence of protocols to mass produce spores of Pasteuria spp. for direct application, the development of strategies for their amplification via agronomic practice still holds great promise for the biocontrol of target nematode species (Dickson, unpublished). In order for spores to attach to juvenile root-knot nematodes, they must bear appropriate surface molecules that recognize and bind to receptors on the cuticle of the nematode host. Interference with spore attachment by lectins specific for N-acetylglucosamine and/or alpha-glucoside, alpha-mannoside residues suggests these ligands may participate in the recognition process (Bird et al., 1989). Proteins isolated from P. penetrans spores have been shown to react with wheat-germ agglutinin (WGA) and concanvalin A (ConA), which indicates the presence of potential ligand receptors on the spores. These findings have provided the basis for a model in which glycopeptides on the surface of the spores, designated as spore adhesins, are recognized by lectins on the cuticle of the nematode (Davies and Danks, 1993; Persidis et al., 1991). Antibodies directed against these adhesion proteins as well as the proteins themselves were able to inhibit attachment of the spores to the nematode cuticle (Charnecki et al., 1996; Davies et al, 1992; Davies and Danks, 1993, Davies and Redden, 1997; Persidis et al., 1991).
The surface coat of plant-parasitic nematodes carries a net negative charge (Spiegel and McClure, 1995). The spores of P. penetrans also bear an electronegative charge that is affected by pH and ionic strength, as well as ion valency (Afolabi et al., 1995). The pH and ionic composition of a medium will be considered as variables in performing attachment assays to characterize potential adhesions. More recent studies have implicated that hydrophobic forces also participate in the overall adhesion process (Davies et al., 1996). It is important to note that this overall process may be complex, with several different types of chemical interactions participating. The interaction of specific polypeptides with specific ligands may be most important in the recognition process as an initial step in the overall adhesion process.
Polyclonal antibodies have been prepared that react with several spore-specific proteins and which block the attachment of spores to the host cuticle (Charnecki et al., 1996; Chen et al., 1997b). These will be used to identify peptide and/or carbohydrate epitopes in specific proteins involved in the recognition processes. Also, two mouse monoclonal antibodies have been produced, one (2A4 IgM) which detects an epitope shared by several peptides resolved by SDS-PAGE, and the other (5F1) which detects an epitope on a single polypeptide. Both of these monoclonal antibodies are able to discriminate different spore isolates with respect to native surface antigens (detected by ELISA) and to denatured polypeptides (detected by Western Blots following SDS-PAGE).
The ZA4 IgM antibody was produced in ascites and purified by gel filtration. It detects a number of bands ranging in size from 23 to 205 KDa by Western blots. These were resolved by SDS-PAGE of endospore extracts, and it is probable that it recognizes a glycan epitope. The ability of the lectin, wheat-germ agglutinin (WGA), to detect these same bands indicates that they bear glycan moieties including either b(1-4)-finked N-acetyl gluosamine or sialic acid residues. The inability of the 2A4 monoclonal antibody to detect fetuin, ovalbumen or pancreatic ribonuclease B, all of which are readily detected with WGA, indicates that this antibody recognizes an epitope that includes but is not restricted to the glycans recognized by WGA. (Charnecki et al., 1998). Using ELISA with plated endospores from different isolates (P20, P 120, and B4) indicate that these epitopes are on the surface of the spores. This same antibody failed to react with plated Bacillus subtilus endospores (evaluated by ELISA) or with UDC extracts of these spores (evaluated by Western blot), which indicates that they are relatively unique to endospores of Pasteuria spp. (Harrison and Preston, unpublished).
Spores have been developed that can be lluorescently labeled with fluorescein isothiocyanate with no detectable loss of their ability to attach to second-stage juveniles (J2) of M. incognita (Charnecki et al., 1996). The labeling involves the conjugation to spore coat proteins different from most of those detected with antibodies that block the attachment of spores to nematodes. These labeled spores also are able to infect nematodes to provide progeny spores. These have been particularly useful in providing quantitative data on the ability of various ligands to block attachment of endospores to nematodes. With this approach, the 2A4 monoclonal antibody was shown to effect 50% inhibition of the attachment of P20 spores to M. arenaria race 1 at an IgM concentration of 1.3 x 10-I0 M. This antibody and its (Fab')2 and Fab fragments will be those first used for the isolation and characterization of the adhesin epitope(s).
The primary approaches to biological control of nematodes have been augmentation of indigenous control agents and inundation with specific organisms. Long rotations or monoculture of susceptible hosts can induce microflora suppressive to specific nematode pests that maintains the pest population at levels below economic thresholds. The best known example is the widespread control of Heterodera avenae in Europe by the fungi Nematophthora gynophila and herticillium chlamydosporium. In the US, suppression of Meloidogyne spp. by the bacterium Pasteuria penetrans has been reported (Weibelzahl-Fulton, et al., 1996). Augmentation of indigenous agents also has been proposed as a mode of action for a variety of organic soil amendments (Rodriguez-Kabana, 1986; Kaplan and Noe, 1993).
Inundative release of biocontrol agents has met with success in small plots (Hewlett, et al. 1998), but commercial successes in larger field-scale trials have not yet been achieved (Duncan and Noting, 1998). Major constraints include limited understanding of the ecological niche requirements for introducing organisms to soil and the cost of producing large quantities of the most fastidious parasites of nematodes. In most cases, the agents being considered for release are highly specialized for effectiveness against particular nematode species. For example, the bacterium Pasteuria penetrans occurs in a variety of races that differ in their ability to attack different species of nematodes. Attachment of the bacterium to the host appears to be a key step in regulating this specificity, with different strains attaching preferentially to different nematode species (Oostendorp, et al., 1990). Research into this and other aspects of the activity of this agent is difficult because of the obligate parasitic nature of Pasteuria, and little success has been achieved in attempts to grow the bacterium in pure culture.
One tactic to suppress nematodes with the potential for low-cost, broad application is the use of endophytic fungi in grasses. Endophyte-infected fescue significantly reduced reproduction ofMeloidogyne marylandii and Pratylenclnss scribrreri (Kimmons, et al., 1990) while an endophyte-infected ryegrass supported significantly fewer Xiphinema americanum than an endophyte-free cultivar (Dernoeden, et al., 1990). Because this agent is seed-borne, its use may be easily integrated into cropping systems using grasses as cover or rotation crops, however, a better understanding of the mode of action and the conditions promoting maximum efficacy is needed.
Integrated Pest Management:
Integrated Pest Management systems are a subset of cropping systems practices. These include integration of crop rotations, cover crops, organic amendments, tillage practices, crop protection practices (physical, chemical and biological), and economic and environmental considerations.
At its simplest, IPM programs for nematodes involve evaluating pest density relative to a damage or treatment threshold. Integration of genetic resistance may occur through adjusting the damage threshold to account for specific differences in tolerance among varieties or by suppressing nematode reproduction to maintain populations below the damage threshold. Integration of biological and cultural controls may involve either some measure of the biological control efficacy against the target pest, or implementation of recommended management practices that are known to reduce pest densities while simultaneously providing other cropping system benefits (e.g., rotations, organic soil amendments). Evaluation of these recommended management practices usually involves monitoring changes in nematode population densities. Although this empirical approach lacks the theoretical value of a mechanistic understanding, in many cases, it is the only practicable approach for assessing highly complex soil systems.
Crop rotations can reduce nematode population densities, but may increase populations of other nematode pests, particularly in mufti-species nematode communities (Noe, 1998). Integration must also consider economic returns of rotations crops, additional capital and labor requirements, and grower and market acceptance of the rotation crop. In the Northeast, rotations are already used as part of management programs for Globodera rostochiensis on potato (Brodie, et al., 1993; Mai and Lownsberry, 1952), Heterodera schachtii on sugar beet (Mai and Abawi, 1980), Meloidogyne hapla on carrot (Kotcon, et al., 1985) and Xiphinema spp. on peach. While crop rotations alone are unlikely to provide nematode control in all nematode-crop systems, their potential as one component of IPM systems has not yet been filly realized. This potential, when integrated with other non-chemical management measures, is likely to become increasingly important as traditional nematicide options are lost.
Biocontrol agents span a continuum between generalist polyphagous organisms and specialists adapted to a single nematode host species or even a limited number of nematode host races. Augmentation of indigenous communities often implicitly relies on a broad diversity of biocontrol agents, of which each is adapted to differing seasons, host life stages, and environmental conditions in the soil. This high biodiversity is needed to assure that at least some of the agents present in a field will be active against the right nematode stages at the right time to promote adequate levels of population suppression. Because of this complexity, understanding the roles and relative importance of individual agents in any particular field is difficult and more progress has been made in systems dominated by one or two highly effective specialists. An ideal agent for commercialization would have a relatively broad spectrum of activity against plant-parasitic nematodes and would be able to successfully colonize a variety of soil environments and cropping systems, but would simultaneously avoid environmental risks from significant non-target effects (Simberloff and Stiling 1996). The indigenous nature of agents such as Pasteuria penetrans, as well as the limited dispersal ability of both these agents and their host nematodes, are factors that demonstrate the inherent ecological safety of biological control as a nematode control strategy.
The patchy distribution and soil-borne nature of nematodes, coupled with the high cost of monitoring and the need to make nematode management decisions well in advance of planting, are special constraints to nematode IPM which emphasize the importance of additional research efforts to support nematode IPM (Duncan and Noling, 1998). Improvements in biological monitoring methods are needed to better assess the spatial distribution of plant-parasitic nematodes as well as the presence of biocontrol agents that may influence nematode population dynamics and yield loss relationships (Sikora, 1992). Long-term sustainability based on a rigid management system is difficult in the face of a rapidly changing economic environment, yet long-term commitments are needed to achieve the benefits of many cultural and biological control practices (Noe, 1998, Duncan and Noling, 1998). The solution to this paradox requires a range of management options that can be implemented as short-term economic conditions dictate, while still integrating the long-term agroecological "costs and benefits" to the cropping system so that the true worth of particular management practices is adequately considered. Mufti-year modeling efforts that integrate population dynamics, environmental variables, yield loss relationships, efficacy of management measures and economic factors have been touted as essential to optimize nematode management, but the research base to support such predictive models is lacking in all but a few cropping systems (Duncan and Noling, 1998). Thus, the challenge of sustainable nematode IPM programs is to understand the multifaceted impacts and interactions of multiple management tactics in order to allow growers to make optimum decisions for long-term nematode control while maximizing economic returns.
With the assistance of Mr. Alan Moore of USDA/CRIS, a search of the USDA Research (CRISTEL database) has been conducted for the field of plant nematology using the following key words and phrases: field crops (potatoes, carrots, lettuce, onions), fruits (peaches and strawberries), and integrated pest management. One hundred and forty-five studies were identified. There are other mufti-state research projects (W-186, 5-282 and NC-215) in the United States that address plant nematode problems, but these projects have different objectives and focus on other crop systems (e.g., alfalfa, field corn, sweetpotato, okra, cotton, wheat, soybean and melon). The proposed NE-171 project outline does not duplicate the efforts of other research projects to date. Comments by peer reviewers support this conclusion.
Objectives
- Evaluate the effects of rotational crops, organic amendments and host crop genetics on nematode community structure.
- Characterization of biological control agents for suppression of plant-parasitic nematodes.
- Comparison and evaluation of IPM system management of plant-parasitic nematodes based on crop rotation, organic amendments, host crop resistance and biological control agents.
