Table 1.
Comparison of methods available for assessing cross-scale structures necessary for studying systemic vulnerabilities to global change
| Method | Data sets | Advantages | Limitations |
|---|---|---|---|
| Discontinuity analyses (GRI, CA, CART, BCART, KDE) | Univariate, rank-ordered, log-transformed data (e.g., body size or mass) | Data easy to obtain either from available sources or through measurement | Species dominance patterns not explicitly accounted for |
| Simple assessment of non-linear (scale-specific) structures in data | Resilience assessment limited to the evaluation of cross-scale patterns | ||
| Limiting assessment of ultimate factors causing discontinuities | |||
| Time series and spatial modeling (Canonical ordinationsa,b; wavelet analysesc) | Multivariate; species abundance, biomass and/or presence–absence data | Species abundances accounted for | Data acquisition labor intensive, high resource demand |
| Separating the role of dominant and rare species | Higher analytical complexity relative to discontinuity analysis | ||
| Evaluation of complementary aspects of resilience and adaptive capacity | Scales and patterns of structure contingent on sampling frequency and length | ||
| Relating patterns to dynamic environmental change | Limited availability of adequate long-term data |
GRI gap rarity index, CA cluster analysis, CART classification and regression trees, BCART Bayesian CART, KDE Kernel density estimates (see text)
aAngeler et al. (2009), an example for time series modeling
bDray et al. (2006), showing the modeling framework for assessing spatial resilience
cKeitt and Fischer (2006), time series modeling