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Changes in nematode species composition
in response to environmental cues: a genomic approach

We
are using resident nematode populations sampled from the Konza
Tallgrass Prairie Biological Station near Manhattan,
Kansas to link the responses of organisms to environmental
change at the genetic level. We hypothesize that different
species may have varying genetic capacities to respond
to changes in the environment; either by differences
in the genes they possess or in how those genes are
regulated. We have been testing these possibilities
by examining the responses of bacterial feeding nematodes
to changes in soil chemistry caused by nitrogen addition
and fire. We are also addressing this in the laboratory
using the genetic model nematode Caenorhabditis
elegans (a Rhabditid). We are using C. elegans to
model nematode environments on Konza in order to discover
genes that are induced or repressed in response to environmental
changes. Our strategy is to document responses of the soil
nematode community to changes in the environment, identifying
potential drivers and mechanisms, then to model these interactions
in the lab with C. elegans to identify relevant
genes and to test these candidate genes in native soil nematodes.
This will lead to the identification of genes that are important
for interactions of nematodes with their biotic and abiotic
environment.
Our
field experiments aimed to set the stage for investigations
of gene functions responsible for the ability of different
nematode taxa to persist in different environments. Previous
observations at Konza documented changes at the taxonomic
level of family (Todd, 1996; Todd, 1999). However, to be able
to identify gene functions, we needed higher taxonomic resolution
and the extent to which differential responses occurs at the
genus level or below was unclear. Thus, we used molecular
methods to quantify the responses of microbial-feeding nematodes
to nitrogen addition and changes in fire frequency at the
lowest levels of taxonomic resolution. Using DNA sequencing
and quantitative polymerase chain reaction (PCR) probes for
the 18S ribosomal RNA gene and the ITS1 region (Jones, 2006a),
we identified 19 microbial-feeding nematode taxa across four
families. When nematodes were sampled across treatments, we
found that some taxa within a family responded similarly to
nitrogen and burning treatments, while other taxa within the
same family responded quite differently. Additionally, although
nematodes from different families on average responded differently
to nitrogen addition and burning, similar responses were seen
in nematode taxa that spanned three taxonomic families (Jones,
2006b).
In the
lab, C. elegans is normally grown on agar
plates seeded with E. coli. We have modeled both the
abiotic and biotic aspects of the environment in the laboratory
by examining the role of pH, ions and native soil bacteria
on nematode responses. For example, we used cDNA microarrays
to identify 204 candidate genes in C. elegans that
are induced in response to the microbial aspects of the biotic
environment. We have used loss of function mutants to test
contributions of some of these genes to fitness in a given
environment and found specific, significant correlations
between expression levels and mutant life history data. Thus
it seems that not only are the expression of specific genes
induced in response to a change in environment, but some
of these genes contribute to fitness traits. These results
demonstrate that assessing C. elegans gene functions
in more natural environments can allow new functions to
be assigned to genes of unknown function, validating a prediction
of Ecological Genomics. Interestingly,
genes implicated in innate immune response were over represented
in the genes identified and have used functional tests to
determine that this defense response was not specific to C.
elegans as we have found a variety of pathogen-associated
effects in native nematode taxa in response to the native
bacterial isolates. Overall our results suggest that
the nematode community responds to changes nutrient enrichment
by expressing genes that increase fitness and the ability
to defend against bacterial pathogens.
In addition,
the altered nitrogen and burning regimes appear to cause
changes in soil pH and ion concentration. We used
KSU
Targeted Excellence funding to explore the potential
direct effects of alterations pH and osmolarity on native
nematode fitness in the laboratory. Eventually, we plan
microarray and subtractive hybridization experiments to
discover the relevant genes involved.
References
and recent ecological genomics publications
Jones,
K.L., Todd, T.C., and Herman, M.A. 2006 Development of
taxon-specific markers for high-throughput screening of
microbial-feeding nematodes, Molecular Ecology Notes,
6, 712-714
Jones,
K.L., Todd, T.C., Coolon, J.D., Blair, J. M., and Herman,
M.A. 2006. Molecular approach for assessing responses
of microbial-feeding nematodes to burning and chronic
nitrogen enrichment in a native grassland, Mol. Ecol.,
15, 2601-2609.
Kammenga,
J.E., Herman, M.A., Ouberg. N.J., Johnson, L.C., Breitling,
R. (2007), Microarray challenges in ecology, TREE,
22,
273-279.
Ungerer,
M.C., Johnson, L.C., Herman, M.A. 2007 Ecological genomics:
understanding gene functions in the natural environment.
Heredity, 100, 178-183.
Todd,
T.C. 1996. Effects of management practices on nematode
community structure in tallgrass prairie. Applied
Soil Ecology 3: 235-246.
Todd,
T.C., J.M. Blair and G.A. Milliken. 1999. Effects of altered
soil water availability on a tallgrass prairie nematode
community. Applied Soil Ecology 13:45-55.
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