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Myster2009

Daniel Falster edited this page Nov 25, 2014 · 1 revision

Report for study: Myster2009

Contact Information

Data contributor: Randall W. Myster

Email: myster@okstate.edu

Address:

  • Biology Department, OSU-OKC, 900 N Portland Ave., Oklahoma City, OK 73107-6195, USA

Data source

Citation: Myster RW (2009). 'Tree seedling survivorship, growth, and allocation in the Cross Timbers ecotone of Oklahoma, USA.' Plant Ecology, 205(2), pp. 193-199.

DOI: 10.1007/s11258-009-9609-0

Abstract: In order to better understand tree dynamics and maintenance of the ecotone between eastern deciduous forest and tallgrass prairie, I planted seedlings of five different species into a Cross Timbers area in North West Oklahoma for one-year. The seedlings were planted in four different patch-types under two different herbivore treatments. I found that (1) out of the original 200 seedlings, 58 survived after one-year with lacebark elm ( Ulmus parrifolia ), osage orange ( Maclura pomifera ), and eastern redbud ( Cercis canadensis ) surviving the most and protection from herbivores increasing survivorship by more than an order of magnitude, (2) elm ( Ulmus parrifolia ) showed the slowest stem growth but protection from herbivory increased stem growth rate by approximately 50%, leaf area ratio was largest for elm ( Ulmus parrifolia ) but seedlings growing in sumac ( Rhus copallina ) patches had the smallest values, specific leaf area was the largest for orange ( Maclura pomifera ) seedlings with tree seedlings growing in grass patches showing greater values than those grown in other patches, and (3) leaf mass ratio was largest for elm ( Ulmus parrifolia ) with seedlings grown in sumac ( Rhus copallina ) patches showing the smallest values and rough-leaf dogwood ( Cornus drummondii ) had the most root biomass relative to shoot biomass compared to all other species. Results suggest tree invasion and establishment across this ecotone is influenced both by species identity and by the variation in resources associated with the distribution and patch dynamics of vegetation from both eastern deciduous forest and tallgrass prairie.

Overview of data provided

The dataset includes records for 58 individuals from 5 species belonging to 5 family(ies), presenting 1 functional type(s), growing in 1 condition(s) within 1 major type(s) of habitat, with data included for the following variables:

Variable Label Units N Min Median Max
latitude Latitude deg 58 37 37 37
longitude Longitude deg 58 -97 -97 -97
a.lf Leaf area m2 58 0.00096 0.0026 0.0063
h.t Height m 58 0.25 0.33 0.46
m.lf Leaf mass kg 58 0.00006 0.00018 0.001
m.st Total stem mass kg 58 0.00007 0.00028 0.00095
m.so Aboveground mass kg 58 0.00015 0.00047 0.0015
m.rt Total root mass kg 58 0.0003 0.00055 0.002
m.to Total mass kg 58 0.00047 0.001 0.0032

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And locally within the country:

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The sites sampled are:

Location Longitude Latitude Vegetation
Lake Carl Blackwell, Oklahoma USA -97.4667 36.65 Temperate forest

The growing conditions of sampled plants was:

Location growingCondition
Lake Carl Blackwell, Oklahoma USA plantation managed

Species sampled

Species Family Pft
Cornus drummondii Cornaceae deciduous angiosperm
Ulmus parrifolia Ulmaceae deciduous angiosperm
Maclura pomifera Moraceae deciduous angiosperm
Cercis canadensis Fabaceae deciduous angiosperm
Quercus shumardii Fagaceae deciduous angiosperm

Methods used

Tree seedlings were planted in 4 different microsites and 2 different herbivory treatments. After one year in the field surviving seedlings were harvested and measured for height: leaf area and root/shoot/leaf biomass.

Total leaf area was measured with a leaf area meter (LI-3100G ,LI-COR, Inc. Lincoln,:

All seedlings had an initial height ofapproximately 20 cm when planted. Final height measured with a ruler.:

Seedlings were dried at room temperature for a month in paper bages and then weighed for total leaf biomass, stem biomass and root biomass.:

Plots of data

This is how the study Myster2009 fits in the entire dataset (grey). each colour represents a species. A legend of species names with colours is included at the end for reports with 1 < n < 20 species.

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