Canadian intersite decomposition experiment (CIDET)
- Introduction
- Research results: Measures of litter quality
- Research results: Comparison of 3rd-year results and model predictions
- Research results: Controls on litter decomposition
- Research results: Effects of climate change on litter decomposition
- CIDET Publications and Presentations
- CIDET working group
Research results: Comparison of 3rd-year results and model predictions
Third year mass loss averaged 35% (65% mass remaining) across all sites and litter types. Within foliar litters, fescue decayed the most rapidly (42% remaining), western red cedar the least (75% remaining) (Table 3). Highest decay rates were observed at Pacific Cordilleran sites (SHL=43%, PMC= 46% mass remaining) and least in high latitude sites (INU=87%, WHI=83% mass remaining). More variation in decay was observed within site (Std. errors 1.5 to 2.9) than within a litter type (Std. errors 1.0 to 2.3).
Litter quality data were used in three simple models of litter decay to predict how mass loss of the different litter types could vary. Model rankings of foliar litter types varied somewhat, Aber's was more different and had the lowest range of predicted mass loss compared Melillo's or Taylor's. Pearson correlations coefficients of model to third year data were highest for Mellilo's (0.87 p=.0004) and Taylor's (0.80 p=.0029) and low and not significant for Aber's (0.50 p=0.1178) Spearman's rank correlation coefficient for each model to data was large and significant for Melillo's (0.91 p=.0001) and Taylor's (0.90 p=.0002) and low and not significant for Aber's (0.37 p=0.2589). The higher overall mass losses predicted by Aber's and Melillo's model compared to Taylor's probably reflects the locations for which the models were derived.
Ranking of litter types based on predictions of remaining percent mass from three models of litter decay, Aber et al 1990 (3 year decay), Melillo et al 1982 (3 year decay), Taylor et al 1992 (3 year decay), and based on 3rd year results of actual remaining percent mass. Aber's is a summed exponential decay model for three litter fractions each k a function of a lignocellulose index; Melillo's is an exponential decay model with k a function of the lignin:N ratio; Taylor's is a piecewise linear model of lignin and N.
Table 3. (a) Percent mass remaining after the first 3 years, meaned across the 12 litter types.
Litter Type | Mean | std err | Max | Min |
---|---|---|---|---|
Whws | 90.4 | 1.8 | 108.0 | 32.4 |
Whwb | 86.8 | 2.3 | 112.8 | 12.2 |
Dbw | 49.4 | 2.0 | 82.0 | 16.5 |
Ctp | 75.3 | 1.9 | 110.6 | 32.0 |
Cdc | 67.6 | 2.0 | 93.8 | 24.6 |
Csb | 56.2 | 1.9 | 87.3 | 24.8 |
Dpt | 56.3 | 1.6 | 93.4 | 22.5 |
Cpj | 60.4 | 1.8 | 86.9 | 24.6 |
Dba | 70.9 | 1.6 | 91.1 | 39.0 |
Cll | 66.0 | 1.9 | 120.4 | 26.4 |
Gfh | 41.8 | 1.0 | 67.5 | 19.8 |
Fbf | 64.5 | 1.7 | 88.0 | 25.4 |
Table 3. (b) Percent mass remaining after the first 3 years meaned across 21 sites in CIDET.
Site | Mean | std err | Max | Min |
---|---|---|---|---|
BAT | 77.5 | 2.6 | 120.4 | 30.6 |
CBR | 52.2 | 2.8 | 100.4 | 24.6 |
CHA | 52.8 | 2.8 | 97.1 | 16.5 |
GAN | 55.5 | 2.9 | 103.3 | 28.4 |
GI1 | 80.1 | 2.2 | 103.1 | 39.9 |
GI2 | 71.7 | 2.4 | 100.6 | 38.2 |
HID | 59.1 | 2.6 | 96.9 | 30.6 |
INU | 86.9 | 1.5 | 106.5 | 54.6 |
KAN | 68.1 | 2.3 | 98.7 | 30.0 |
MAR | 44.1 | 2.4 | 83.3 | 12.2 |
MON | 60.0 | 2.9 | 100.0 | 32.9 |
NH1 | 79.8 | 2.2 | 112.8 | 43.8 |
NH2 | 73.4 | 2.4 | 102.1 | 37.8 |
PAL | 75.7 | 2.0 | 99.9 | 40.6 |
PET | 52.6 | 2.4 | 90.8 | 25.4 |
PMC | 46.5 | 2.9 | 95.8 | 17.8 |
SCH | 69.9 | 2.6 | 101.6 | 29.2 |
SHL | 43.4 | 2.4 | 92.8 | 22.2 |
TER | 71.9 | 2.4 | 100.2 | 34.7 |
TOP | 68.6 | 2.6 | 99.5 | 28.5 |
WHI | 82.3 | 1.8 | 100.8 | 52.1 |
All Sites | 65.4 | 0.7 | 120.4 | 12.2 |
Project status
- On-going