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Introduction:
The objective of this experiment is to determine how plant growth
and rhizosphere carbon availability change when roots are infected by parasitic
nematodes. Furthermore, we want to know how changes in the quantity
and quality of rhizosphere carbon influence the structure and function
of the soil microbial community.
Clover will be grown in sand with or without the presence of a parasitic
nematode. Rhizosphere carbon solutions will be collected from these
systems periodically for chemical analysis. These solutions will
drip from the plant into columns containing soil. After application
of the solutions, the microbial communities in the soils will be comparatively
analyzed. Changes in rhizosphere chemistry will be linked to any
microbial responses.
Future experiments involving grass and nematode complexes will provide
complementary data and an emerging understanding of how plant-parasitic
nematodes modify the rhizosphere environment and influence microbial diversity
and function in grasslands.
Hypotheses:
(1) Nematode infection will affect plant biomass negatively in this
experiment, where nutrients are not limiting and there is no positive microbial
feedback from the activity of rhizosphere organisms. We recognize
that in the soil environment, in the presence of a natural rhizosphere
microbial community, lower levels of nematode plant parasitism may have
a positive effect on plants by enhancing microbial activity and nutrient
availability in the rhizosphere. Furthermore, in a nutrient limiting
environment, root damage by nematodes may illicit a 'compensatory growth'
response below ground, such that nutrient acquisition by the plant is enhanced.
However, we predict that the overall effect of the nematodes in our system
will be negative.
(2) Rhizosphere carbon sources (including root exudation) will change
quantitatively and qualitatively when plants are infected with nematodes.
This hypothesis will be evaluated on the basis of (1) each individual plant
and (2) per unit of plant biomass. We predict that although plant
biomass is reduced by nematode infection, rhizodeposition per unit of plant
biomass will be enhanced due to root damage and leaking.
(3) Microbial communities receiving rhizosphere solutions from nematode
infected plants will have higher activity and biomass, reflecting increased
carbon supply. These microbial communities will also show changes
in substrate utilization patterns, reflecting qualitative changes in rhizosphere
chemistry. We predict that microbial responses will be specific to
particular microbial groups, as reflected in analysis of community PLFAs
and plate counts of important heterotrophic groups (psuedomonads, fungi).
Background:
Heterodera trifolii, the clover cyst nematode, is a sedentary
endoparasite of clover roots. Juveniles enter the roots around the
root hairs and can invade up through the root, causing cell damage and
death. At its final site in the root, the juvenile's feeding induces
an initial feeding cell to enlarge, and adjacent cells are incorporated
by wall dissolution to form a multi-nucleate cell complex called a syncytium.
The development of the nematode into an enlarged female often causes the
root to split open, exposing the female to the outside. When the
female dies, its body forms a protective sheath around the eggs that is
known as a cyst. The eggs within the cyst are contained within a
gelatinous matrix. The generation time (egg to egg) of this nematode
can range from 20 to 70 days, depending on temperature and other environmental
conditions.
Root penetration, feeding, cell enlargement, and rupture of the cortex
are all aspects of nematode infection that could trigger pulses of rhizodeposition.
Methods:
Clover plants will be subject to infection by H. trifolii while
growing in "Microcosms". Rhizosphere solutions will be collected
from the plants and chemically analyzed. Solutions will also be allowed
to drip onto soil to stimulate the soil microbial communities.
Microcosm Design:
(1) Top Chamber: 70 ml syringe barrel, containing muffled
(carbon-free) sand, with a small layer of muffled gravel on the bottom,
and a small layer of cotton wool in between. The cotton wool is to
prevent sand/nematode/root escape and the gravel is to promote drainage
through the system. Units will be autoclaved. Germinated seeds
will be transferred into this top 'plant' chamber. Each plant chamber
will be equipped with a single glass tube, 3 cm in length, embedded into
the sand, to facilitate nematode introduction to root systems. These
chambers will be contained on a rack with a polycarbonate cover that has
ports for pumping in sterile air and nutrient solutions.
(2) Lower chamber: Also syringe barrels. Will contain
fresh Sourhope soil (4mm sieved, plant material removed). Fresh soil
will be mixed 1:1 by weight with dry, muffled, autoclaved sand. Addition
of sand is to improve drainage, reduce the volume of soil that solutions
are being applied to. Solution dripping out of these lower chambers
will be collected in a 'waste' bottle and disposed. Application of
solutions to soils will commence when plants are introduced to system.
These chambers will be contained on a rack directly below the top chambers.
(3) Rhizosphere solution flow: Between the two chambers
will be a 3-way leur lock stopcock that will normally be set in a position
that allows any solution that drips out of the plant chamber to drip into
the soil chamber. In order to collect rhizosphere solutions for chemical
analysis, the stopcock will be set so that solution comes out of the side
port, through a section of tubing, draining into a poly bottle. To
collect solutions, pumps will be set to a high flow rate and bottles will
be left overnight to obtain approximately 60 ml of solution. Solution
volume will be estimated by weighing the bottles after collection of solutions
and subtracting the mass of the empty bottle.
Photos of system:
Experimental Design:
In order to quantify potential changes in rhizosphere chemistry it is
necessary to attempt to manipulate plants in an aseptic environment, where
there are no micro-organisms present to modify the compounds being released
by the roots. The challenge in this experiment is to design treatments
that allow for this to some extent, while at the same time acknowledging
the importance of the Rhizobium/Trifolium association and the difficulties
presented in introducing aseptic nematodes to the system. Our treatment
selection attempts to address this challenge.
Design: Randomized Complete Block (8 blocks)
Treatments (each replicated 8 times):
(1) Control Trifolium plants (no nematodes)
(2) Trifolium + Heterodera
(3) Trifolium + Rhizobium
(4) Trifolium + Heterodera and Rhizobium
(5) Heterodera only
(6) Non-plant Blanks
(7) (8) Extra plants for mid-experiment harvests to assess nematodes
(degree of infection, life stage, population growth). Will receive
Rhizobium.
Sterile clover plants will be established from para-acetic acid sterilized
seeds in petri plates on sand. The appropriate treatments will be
inoculated with Rhizobium at the time of seed germination.
Several days after germination, seedlings will be transferred to the microcosm
system, one plant per plant chamber. Plants will be grown for approximately
12 weeks, or until the root system is developed. All plants will
be supplied with 0.5 mM N nutrient solution at a flow rate of 12 ml/day.
This flow rate will represents an application of solution to the soils
that is higher than the Sourhope average daily rainfall of 2.3 mm/day (which
converts to 1.85 ml/day applied to chambers). Plants and soils will
be maintained at a growth room temperature of 20C, with a 16h photoperiod.
During the light part of the cycle, air temperature will be set at 5C.
The polycarbonate cover for the top chamber will elevate the temperature
within so that plant growth is occurring at a slightly higher temperature.
The chambers, including the root-containing top chamber, will be kept in
the dark by covering with plastic sheeting. Temperature and PAR will
be measured throughout. At the time of nematode addition, the dark
temperature for the chamber will be lowered to 12C to ensure cool conditions
for nematode establishment. After one week, temperature will be returned
to the original settings.
Once plants are established (8-12 weeks), nematodes will be added to
the appropriate treatments. Nematodes will be surface sterilized
briefly with antimicrobial solutions. Nematode density in solution
will be estimated and approximately 100 jjuvenile nematodes will be added
to each unit, 2 times over the first 4 days of the experiment. Rhizosphere
solutions will be collected every 7 days over the next 30-45 days.
The number of nematodes in the solutions will be assessed, to evaluate
the impact of solution collection.
At harvest the following measurements will be made:
Plant:
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Shoot biomass
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Root biomass
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Shoot C&N content
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Root C&N content
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Root architecture
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Assessment of nematode densities in sand and roots
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Nematode counts and life stage determination
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Nodule count
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Soil:
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Microbial biomass
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Microbial respiration
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PLFA characterizaton
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Biolog assessment of community-level physiological profiles
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Plate counts of bacteria, fungi, yeasts, pseudomonads
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Rhizosphere Solutions:
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Total organic carbon
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Total protein
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Phenolic Acids
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Amino Acids
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Free carbohydrates
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Plate counts
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Schedule:
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TASK:
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DATE COMPLETED:
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Microcosms constructed, sterilised, and on-line with full flow
of nutrient solution
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1.30 and 1.31.01
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Clover seeds sterilised
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5.2.01
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Appropriate seeds inoculated with Rhizobium
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8.2.01
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Pre-planting TOC and sterility test
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6.2.01
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Second pre-planting TOC test
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13.02.01
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Seedlings transfered to microcosms
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21.2.01
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Soil collected from Sourhope for receptors
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21.2.01
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Soil columns prepared and added to system
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22.02.01
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Increased N concentraction in plant nutrient supply to 2mM NH4NO3
(for 2 wks only)
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12.4.01
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Addition of nematodes to system
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2 May, 6 May
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Stolon removal to prevent overgrowth
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2 May
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Collection of rhizosphere solutions (A)
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Tuesday 1.5.01 (pre-treatment)
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Collection of rhizosphere solutions (B)
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Friday 11 May
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Collection of rhizosphere solutions (C)
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17 May
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Collection of rhizosphere solutions (D)
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25 May
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Stolon removal
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29 May
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Collection of rhizosphere solutions (E)
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1 June
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Collection of rhizosphere solutions (F)
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8 June
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Analysis of EXTRA plants; Stolon removal
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13 June
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Collection of rhizosphere solutions (G)
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22 June
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Collection of rhizosphere solutions (H)
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28 June
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Collection of rhizosphere solutions (I)
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5 July
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Collection of EXTRA plants
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9 July
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Collection of rhizosphere solutions (J)
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13 July
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Collection of rhizosphere solutions (K)
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19 July
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Destructive Harvest (n=47)
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Monday, 23 July
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References:
Bardgettt RD, Cook R, Yeates GW, and Denton CS. 1999. The
influence of nematodes on below-ground processes in grassland ecosystems.
Plant and Soil. 212:23-33.
Cook R and GW Yeates. 1993. Nematode pests of grassland
and forage crops. In: K Evans, DL Trudgill, & JM Webster
(Eds.) Plant Parasitic Nematodes in Temperate Agriculture.
Oxon, UK: CAB International, pp. 305-350.
Denton CS, Bardgett RD, Cook R, and Hobbs PJ. 1999. Low
amounts of root herbivory positively influence the rhizosphere microbial
community in a temperate grassland soil. Soil Biology & Biochemistry.
31:155-165
Pederson GA and Quensberry KH. 1998. Clovers and other forage
legumes. In: KR Barker, GA pederson, & GL Windham (Eds.)
Plant and Nematode Interactions. Madison, WI: American Society of
Agronomy, Crop Science Society of America, Soil Science Society of America,
pp399-425.
Yeates GW, Bardgett RD, Mercer CF, Saggar S, and Feltham CW. 1999.
The impact of feeding by five nematodes on 14C distribution in soil microbial
biomass and nematodes: initial observations. Proceedings of the New
Zealand Society for Parasitology.
Yeates GW, Saggar S, Denton CS, & Mercer CF. 1998. Impact
of clover cyst nematode (Heterodera trifolii) infection on soil microbial
activity in the rhizosphere of white clover (Trifolium repens) - a pulse-labelling
experiment. Nematologica 44:81-90.
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