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Differential analysis of active mychorrizae present among living and deceased Piñon (Piñus edulis) and Juniper (Juniperus monosperma) trees in the Los Piños Mountains New Mexico. Kimberly F. Elsenbroek. Climactic Influences.
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Differential analysis of active mychorrizae present among living and deceased Piñon (Piñus edulis) and Juniper (Juniperus monosperma) trees in the Los Piños Mountains New Mexico Kimberly F. Elsenbroek
Climactic Influences • It is predicted that the region will be greatly affected by climate change and see an increase of temperature by 4oC (Diffenbaugh et al. 2008; IPPC 2007) and become drier overall (Seager et al. 2007). • To predict how future environmental conditions will affect local biomes, we must understand how they function now.
Eddy Covariance Tower • United States Forest Service (USFS). • Monitors several different biomes • Carbon/water exchange with the atmosphere, productivity, evapotranspiration and ecosystem respiration. • Little is known about below-ground activities at these sites.
History of the sites • Tower Establishment • Experimental 2009 • Control 2007 • Towers are ~5km apart and experience similar environmental conditions • Piñon/Juniper(PJ) woodlands are a wide spread and significant biome of the southwest and cover ~30 million Hectares. • ¼ of New Mexico is covered in PJ woodlands. • They are refuge for wildlife and provided wood-fuel for humans in the past. http://tuvalu.santafe.edu/~pth/pj.html
Site Description biology.unm.edu/litvak/Pinyon%20Juniper/Pinyon%20Juniper.html
Simulating Future Conditions • The experimentalsite has simulated bark beetle attacks on piñon trees during high stress events by girdling the trees. • Bark beetles are a growing epidemic in the southwest. • Fungus • Stress • Continuing impacts of climate change • Future conditions
Timeline of tree response Sept 29, 2009 Nov 12, 2009 Apr 9, 2010 July 30, 2010
Fungi • Arbuscularmycorrhizal (AMF) and ectomycorrhizal fungi (ECM) play an important role in belowground and plant community functions and form symbiotic relationships. • Increase stomatalconductance • Alter plants response to drought • Alter hormone regulation (Auge 2004)
Fungi AMF are associated with Juniper (Root associated fungi [RAF]) ECM are associated with Piñon www.microbiologyprocedure.com/population-interactions/types-of-mycorrhizae.html www.tandjenterprises.com/images/EndoDiagram.jpgxt
Project Description • During this project we compared the microbial activity between: Dead piñon Living piñon Living juniper
Research Question/Hypothesis • R1: Which tree(s) will have the highest rates of microbial activity? • H1 : Microbial activity will be higher under the living piñon trees when compared to the dead piñon trees.
Methods • Six transects were established at each site (control and experimental) • 5 comparisons at the experimental site for each transect. • 3 comparisons at the control site for each transect. • Areas selected for transect establishment contain trees to satisfy the Piñon and Juniper comparisons.
Plot 1 Plot 2 Plot 4 Plot3 TOWER Plot 6 Plot 5 EXPERIMENTAL SITE
PLOT ONE LJ LJ DP S S S LJ S S S LP S S S LP S S S S DP LP S S LJ LP S= Sample (3cores/sample) DP=Dead piñon LP=Live piñon LJ=Live juniper *This graphic represents 1 plot There are 6 plots per sampling site Experimental Site Sampling
Plot 2 Plot 1 Plot 4 Plot 3 TOWER Plot 6 Plot 5 CONTROL SITE
PLOT ONE LJ S LJ LP S S S S S S S LP LP LJ S S= Sample (3cores/sample) LP=Live piñon LJ=Live juniper *This graphic represents 1 plot There are 6 plots per sampling site Control Site Sampling
Sample Collection • Soil samples were taken using a 2 X 10 cm core at a rate of 3 cores from beneath each tree and between the two trees being compared. • 3 samples per comparison. • ~ 15 samples from each plot. • Cores taken underneath and between each tree were combined and represent the average mycorrhizal community.
Sample Processing • Soil samples were sieved using a 4 and 2-mm mesh to collect living coarse roots . • ~8 mL KOH and MeOH solution was added to a sub-sample (~5mL) of soil in a falcon tube. • Sample was homogenized by shaking.
Water holding capacity and organic matter content • Water holding capacity (WHC)was determined gravimetrically. • A subsample of ~ 1g was placed in aluminum pans and weighed to calculate: weight of soil + water content. • Samples were then dried at 60o C for >/= 1hr and weighed to determine dry weight. • This tells us the WHC of each sample • Samples were combusted at 500o C to burn off organic matter (OM) and then weighed again to determine OM content (Stursova et. al 2006). • OM was burned off using a muffle oven.
Extracellular Enzyme Assays • Extracellular enzyme assays (EEA) were measured using 1.0 g soil/bicarbonate buffer slurry placed in microplates with substrates.
Ergosterol Extractions • Ergosterol occurs in yeast or fungal cell membranes only. • The ergosterol solution (KOH and MeOH) will stop all activity except those associated with ergosterol. • We then measure that to find out how much fungi is in each sample. • Presence of ergosterol will be measured using techniques from the Treseder Lab Protocol for Ergosterol Extraction.
Statistical Analyses • A one-way ANOVA analysis was used to compare the enzyme activity between living and dead piñon trees to living juniper trees. • Enzyme activities were analyzed between each comparison. • Analyses were made on activity per hour, per gram of dry weight.
Results • Junipers tend to have higher rates of microbial activity compared to living and dead Piñon trees for Bgluc and LAP EEA. • Differences were highly significant. • Patterns did not follow the same distribution for NAG and AlkP EEA. • Differences were not significant.
Results P = n.s P = n.s. Comparisons Between Trees Comparisons Between Trees
Discussion • Enzyme activities found in our study are similar to those found in Sinsabaugh et. al 2008. • The study was conducted on the Sevilleta National Wildlife Refuge in a PJ forest. • EEA were related to climactic gradients. • The experimental site in our study simulates predicted future climactic gradients. • Climactic treatments at our experimental site had a significant effect on the EEA.
For the future • Do pre and post monsoon season comparisons. • Sample at both control and experimental sites equally for a better comparison • Control site was only sampled once instead of 3X. • Finish ergosterol extractions and analyzing all of the data.
The Big Picture • The tower estimates belowground activity using data from soil respiration. • This project will allow us to determine the accuracy of those estimations. • Data will be pooled with existing ecosystem data: • Soil respiration • Ecosystem productivity • Contributes to a larger study in which these analyses are being conducted at each biome/tower site.
Acknowledgements • Robert Sinsabaugh • Jennifer Johnson • Daniel Warnock • 2011 REU Students • 2011 Interns • Scott Collins • Marcy Litvak • Don Natvig • SevilletaREU program