Return to Structural Indicators
| Structural Indicator Ranking Results | |||||||||||
| Healthy Reefs for Healthy People | |||||||||||
| Indicator | Overall Indicator Ranking | Caveats / Limitations | Data gaps | Comments | |||||||
| Ecological relevance | Feasibility | Limitations | Responsiveness | ||||||||
| Total coral taxon eveness and Total fish evenness | High | High | High | Moderate | evenness might not be sensitive to species replacement | Could use a standard species list - measure evenness of that list | |||||
| Abundance of focal species (manatees, hawksbill turtles, whale sharks, Goliath grouper, sawfish) | Moderate | Moderate | Moderate | High | Promote shark research in region | ||||||
| % Benthic cover | High | High | Moderate | Moderate | targets ratios should be considered over large spatial scales, varies by habitat type, and avoiding sand areas | ||||||
| Rugosity (see AGRRA database) | High | High | High | Moderate | |||||||
| Aerial extent of coral reefs | High | Moderate | Moderate | Low | low responsiveness – reef extent doesn’t change much if coral dies. Need uniform classification scheme | Need better resolution of coral vs. algae and of different reef types | Some data available (30m resolution). Could use LIDAR from USGS (John Brock) Frequency: once for basis of monitoring scheme, then every 5 yrs or after a big event (hurricane) | ||||
| Aerial extent of mangroves | High | High | High | High | depends on depth and water clarity | - Corridors should be considered - Can’t just treat all the same | |||||
| Aerial extent of seagrass | High | Moderate | Moderate | High | trawling damage data needed | Quick negative response with pollution. Patch sizes should be considered (edge effects & corridors) | |||||
| Seagrass density | High | High | Low | Moderate | Gap in understanding | ||||||
| This file is a working draft from the Healthy Reefs workshop, Miami, June 2004. | © Healthy Reefs for Healthy People | ||||||||||