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Title:
CSPs: Leaf litter decomposition in CSPs: decomposition rates (k-values)
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Private
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Published:
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Abstract:
This data set set belongs to the SP5 litter decomposition experiment that was structured in three parts. First we determined single-species litter decomposition constants of 26 woody species, second litter decomposition of Schima superba was assessed in all 27 CSPs to reveal inter-plot variability using a common standard litter substrate, and third litter diversity was manipulated in 27 plot-specific litter mixtures with species richness ranging from 7 - 17 species. In this dataset the decomposition constants (k-values) are reported. ---- Data on remaining mass, carbon and nitrogen concentration of each individual litter bag are located in the dataset "Leaf litter decomposition in Gutianshan: remaining litter mass, carbon and nitrogen concentration during decomposition.
Design:
Litter bags (15 cm x 15 cm) were made of nylon with 1 mm mesh size and filled with 5 g of dried leaf litter. The decomposition experiment was started in spring 2009. After carefully removing loose forest floor litter, bags were slightly anchored in 5 cm spacing at the ground with 10 cm long metal stakes puncturing the hem. Because an organic humus layer (Oh) was often absent, litter bags were placed directly on the mineral soil in most cases. Gaps between litter bags were refilled with the removed forest floor litter. Replicated litter bags were retrieved in six time steps after 92, 146, 205, 272, 333 and 383 days of decomposition in the field. Because CSPs were spread over the entire GNNR, litter bag retrieval took about seven days to finish. Thus, the given time intervals represent the mean number of days calculated for each sampling period after the start of the experiment. After retrieval, remaining litter was carefully cleaned from adherent mineral soil, ingrown roots and fecal matter, dried at 60 °C until constant mass and weighed after cooling down. We used three complementary approaches to study leaf litter decomposition (s. decription below) We calculated the annual exponential decay coefficient k (decomposition rate constant) for each of the 80 decomposition series (26 mono-specific, 27 Schima superba and 27 mixed-species series) based on the single exponential decomposition model of Olson (1963) where X is the proportion of litter mass remaining at time t; k is the exponential decay coefficient (decomposition rate constant), and t is the time in days. This model reflects well the observed exponential decline of litter mass with time (see Results section below): high mass loss during the initial phase of leaf litter decomposition when soluble compounds are removed easily by leaching to a more retardant decay of accumulating recalcitrant substances. The non-linear model was fitted via least-squares estimation with 100 % of litter present at time = 0. (i) Decomposition of single-species leaf litter (""single_species"" We determined litter decomposition rate of 26 sub-canopy and canopy tree species occurring in the CSPs under the same microclimatic and edaphic conditions. For each species, 12 litter bags were filled with dried leaf litter, and two replicated bags per species were retrieved at each time step. Owing to the large coverage (several square meters of forest floor) by litter bags, we decided not to conduct the experiment within a selected CSP but rather outside on undisturbed forest floor providing enough space. Hence, litter bags were placed on the ground a few metres next to one plot (CSP 9) in two blocks containing one replicated bag for each time step, respectively. Random arrangement of the 156 bags in each block ensured that species-specific decomposition rates were not affected by spatial variation of microclimatic conditions. (ii) Decomposition of Schima superba leaf litter (""common_substrate"") Leaf litter collected from one of the most dominant and abundant tree species (Schima superba) was used to study plot-specific litter decomposition along the tree diversity and successional forest gradient using a total number of 324 litter bags. 12 bags filled with Schima superba leaf litter were placed in every plot with 2 bags to be sampled at each of the 6 retrieval events. Bags were randomly positioned within an area of 1 m by 2 m in the central subplot of the corresponding CSP. (iii) Decomposition of mixed-species leaf litter (""mixed_litter"") In the litter mixture approach, the number of litter species per bag equalled the number of species found in the different CSPs based on 24 species for which sufficient quantities of litter could be collected. Hence, species number in plot-specific litter mixtures ranged from 7 to 17 with 0.294 g to 0.714 g of leaf litter per species contained in each bag, respectively (Appendix Table 4). Litter bag species richness was significantly related to plot species richness (Appendix Fig. 10). For each plot, 12 bags filled with a plot-specific mixture were prepared and placed next to the Schima superba litter bags in each CSP covering together an area of about 2 m2. After retrieval, separation into single species was not possible due to the large number of species involved and high fragmentation during decomposition. However, we managed to differentiate between broad-leaved and coniferous litter (Pinus massoninana, Pinus taiwanensis and Cunninghamia lanceolata). Dry mass was determined separately for broad and needle-leaved litter.
Spatial extent:
CSPs of the BEF China Experiment, Gutianshan Nature Reserve 29°08'-29°17'N 118°02'-118°11'E
Temporal extent:
from spring 2009 one year
Taxonomic extent:
Leaf litter from trees
Measurement cirumstances:
1) For Castanopsis tibetana the second replicated litter bag could not be relocated for time step 92 days (here only one litter bag retrieved) but was rediscovered at time step 146 days (here 3 litter bags retrieved). 2) In some bags caterpillars were discovered that consumed a large fraction of litter material (e.g. Castanopsis tibetana). As we used a mesh size if 1 mm, caterpillars hatched from eggs but could not escape anymore from the litter bags, thus reflecting unnatural conditions. For calculating k-values those litter bags with abnormal mass loss were excluded.
Data analysis:
Data on remaining mass, carbon and nitrogen concentration of each individual litter bag are located in the dataset "Leaf litter decomposition in Gutianshan: remaining litter mass, carbon and nitrogen concentration during decomposition."

Filter:
Dataset column

Name:
Study_Part
Definition:
Experimental design: this data is used for single litter bags and mixed litter bags; single_species; common_substrate; mixed_litter
Unit:
No information available
Datagroup:
Helper
Keywords:
No information available
Values:
litter_mixture
single_species
common_substrate
Contributors:
No information available

Dataset column

Name:
Species_acr
Definition:
Species acronym in single species litter bags
Unit:
No information available
Datagroup:
Helper
Keywords:
No information available
Values:
13
12
14
11
10
Contributors:
No information available

Dataset column

Name:
Species
Definition:
Species name
Unit:
No information available
Datagroup:
Scientific plant species name
Keywords:
species
Values:
Adinandra millettii
Castanopsis eyrei
Castanopsis fargesii
Camellia chekiangoleosa
Castanea henryi
Contributors:
No information available

Dataset column

Name:
richness
Definition:
Species richness in mixed litter bags
Unit:
count
Datagroup:
Litter diversity
Keywords:
species richness, explanatory, diversity
Values:
10
12
13
11
1
Contributors:
No information available

Dataset column

Name:
CSP
Definition:
Number of the Comparative Study Plot; Datagroup description: BEF research plot name; Datagroup description: Reasearch plots of the Biodiversity - Ecosystem functioning experiment (BEF-China). Comparative Study Plots (CSP) in the Gutianshan Nature Reserve, having a size of 30x30m^2, measured on the ground.
Unit:
No information available
Datagroup:
BEF research plot name
Keywords:
location
Values:
CSP02
CSP04
CSP03
CSP05
CSP01
Contributors:
No information available

Dataset column

Name:
k
Definition:
decomposition constant; We calculated the annual exponential decay coefficient k (decomposition rate constant) for each of the 80 decomposition series (26 mono-specific, 27 Schima superba and 27 mixed-species series) based on the single exponential decomposition model of Olson (1963) where X is the proportion of litter mass remaining at time t; k is the exponential decay coefficient (decomposition rate constant), and t is the time in days.
Unit:
per year
Datagroup:
Decomposition
Keywords:
response variable, decomposition
Values:
0.34
0.35
0.3
0.23
0.32
Contributors:
No information available

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5 scherer lorenzen medium

Michael
Scherer-Lorenzen

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Stefan
Trogisch

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