Return to Functional Indicators
| Functional Indicator Ranking Results | |||||||||
| Healthy Reefs for Healthy People | |||||||||
| Indicator | Overall Indicator Ranking | Caveats/ Limitations | Data gaps | Comments | |||||
| Ecological relevance | Feasibility | Limitations | Responsiveness | ||||||
| % Bioeroded | Moderate | Low | Low | N/A | Severe research gap | Too little known about taxa and internal v. external bioeroders | Potentially a proxy for eutrophication and degredation. Limit: Research Gaps. Has promise; seek funding | ||
| Coral Settlement | High | Moderate | High | High | Location and species specific; some of the best reef builders may broadcast over large distances | Large parrotfish promote CCA and settlement; lower w/ macroalgae; need larvae & propensity for settlement | |||
| Coral Recruits (4 cm) | High | High | High | High | Location and species specific; need to sample often | Intact trophic structure increases recruitment | |||
| Coral size frequency | High | High | High | High | Location and species specific | ||||
| Fish Settlement | High | Low | High | Moderate | Species specific methods; need for expertise | MAR baseline | Time & work intensive; F(x) of larval supply | ||
| Fish recruits | High | Moderate | High | High | Species specific methods; need for expertise | MAR baseline; need to standardize sizes | Time & work intensive; Possible freq. trends in recruitment | ||
| Fish size freq. | High | High | High | High | MAR baseline | Possible freq. trends in recruitment | |||
| % Recent dead | High | High | Moderate | Moderate | Separate from Old dead | ||||
| % Old dead | High | High | Moderate | Moderate | |||||
| % Standing dead | High | High | High | Low | Habitat specific | Can be good (adds rugosity and habitat) | |||
| Size Frequency | High | High | Moderate | Moderate | Locally and species dependent; data interpretation | ||||
| Disease | High | High | Moderate | gap | Diff. between incidence and prevalence | ||||
| Bleaching | High | High | Moderate | Low | Locally and species dependent; tied to GCC | LD50 for species and MAR; importance of repeat bleaching; % tolerant species | |||
| Predation | Low | High | High | varies | |||||
| Fish bites & herb. size | High | High | High | High | Habitat dependent; standardize depths | MAR | Can determine consumption rates; bites/m2 or bites/fish | ||
| Herbivorous fish biomass | High | High | High | High | |||||
| Diadema | High | High | High | Low | Size freq. | ||||
| Green turtle and manatee abundance | Moderate/High | Moderate | Moderate | Low/Moderate | Rarity makes surveys costly in time and money; manatees difficult, turtles more difficult | “normal” environmental (local) values | |||
| This file is a working draft from the Healthy Reefs workshop, Miami, June 2004. | © Healthy Reefs for Healthy People | ||||||||