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11th ICRS Abstract book - Nova Southeastern University

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23-69<br />

Restore Or Not To Restore?<br />

Vladimir KOSMYNIN* 1 , Alison MOULDING 2 , Richard DODGE 2 , David GILLIAM 2<br />

1 Bureau of Beaches and Coastal Systems, Florida Department of Environmental<br />

Protection, Tallahassee, FL, 2 National Coral Reef Institute, NOVA <strong>Southeastern</strong><br />

<strong>University</strong>, Dania, FL<br />

Most coral reef scientists and managers would agree that coral reefs are degrading at ever<br />

increasing rates from a multitude of natural and anthropogenic stressors occurring at<br />

global, regional, and local scales. However, there is less agreement on the circumstances<br />

that warrant restoration and if costs outweigh benefits. In many cases observed recovery<br />

rates are slow, and new communities often have compositions differing from the original.<br />

Requirements for restoration of human-induced local damages often differ widely among<br />

countries. Efforts may involve reattachment of corals or their propagation (enhancement<br />

of recruitment) using various methodologies. The success of such local restoration is<br />

variable and depends on many natural and human induced factors. Nevertheless,<br />

published data and experimental results of projects in Southeast Florida demonstrate a<br />

high probability of success. Some would argue that restoration is insufficient to address<br />

large-scale degradation issues and, consequently, that limited funds should instead be<br />

directed at reducing impacts. While it is true that regional damages resulting from<br />

hurricanes, tsunamis, disease outbreaks, and bleaching events may involve areas too large<br />

for full-scale restoration, smaller scale restoration is an important management tool that<br />

could potentially benefit local and regional coral populations and speed recovery.<br />

Locally restored areas may serve as sources of coral propagation and stepping stones in<br />

connectivity between reefs. Restoration projects are also important in generating public<br />

awareness and support of conservation efforts. Additional research efforts directed at<br />

finding and testing new coral reef restoration methodologies should be continued.<br />

Unaided recovery of injured coral reefs now represents a much less likely scenario given<br />

the considerable local, regional, and global stressors.<br />

23-70<br />

The Management Of Coral Reefs – Where We've Gone Wrong; How We Can Fix It<br />

Peter F SALE* 1<br />

1 International Network on Water, Environment and Health, United Nations <strong>University</strong>,<br />

Hamilton, ON, Canada<br />

Ecologists studying coral reefs long ago shifted from an assumption that these were<br />

ecosystems essentially untouched by humans, to a recognition that human impacts have<br />

become pervasive and severe, but they have meanwhile been party to a disastrous<br />

separation of science from management – a separation that keeps their growing<br />

understanding from being integrated into management action. Managers, when they have<br />

moved beyond the wishful thinking of paper parks and public awareness campaigns, have<br />

put undue faith in the effectiveness of Marine Protected Areas while ignoring both the<br />

lack of scientific underpinning of many management practices and the elephant which is<br />

rampant and growing over-exploitation of reef resources. The result is a sad history of<br />

progressive decline. Reefs suffer a diversity of often synergistic stresses. There is a way<br />

forward if we first decide that we really want to have sustainable coral reef systems in our<br />

future. This path requires that we firmly embrace the precautionary principle, that we<br />

recognize and reduce over-exploitation, and that we vigorously apply the science we have<br />

in hand to improve management now. Along the way we need to develop new science to<br />

provide a basis for more sophisticated management than is now possible. There is hope<br />

for a future for coral reefs, but only if scientists and managers act now to reduce<br />

controllable stresses, freeing these ecosystems to better cope with less manageable<br />

pressures of climate change. Achieving this future will require far more effective<br />

demonstration than yet achieved of the value of coral reefs to coastal populations.<br />

Oral Mini-Symposium 23: Reef Management<br />

23-71<br />

Are There "Ten Commandments"for Coral Reef Management?<br />

Barbara BEST* 1<br />

1 Office of Natural Resources Management, U.S. Agency for International Development,<br />

Washington, DC<br />

In an effort to capture the essential management actions required for Ecosystem-Based Fisheries<br />

Management, several fisheries scientist have proposed 10 guiding principles or<br />

“commandments”. Could coral reef management benefit from a similar effort to capture<br />

critical management guidelines? To initiative a discussion within the coral reef community, an<br />

initial draft set of guidelines are presented. These commandments are based largely upon<br />

experience in less-consuming countries with weak governance and institutions but are widely<br />

applicable.<br />

The first cluster of guidelines involves spatial attributes: 1. look upstream – take a watershed<br />

approach. 2. look down -- establish depth refugia. 3. look near then far -- include associated<br />

habitats then other functionally-connected reefs.<br />

The second cluster focuses on the management process: 4. Understand the cultural, social,<br />

economic and governance context and work accordingly. 5. Focus on the consultative process<br />

early -- the science process should not outpace the stakeholder process. 6. Build management<br />

resilience – provide redundancy in leadership and capacity, strengthen management entities and<br />

organizations, and ensure revenue streams. 7. Address sea tenure and access rights – create<br />

incentives for environmental stewardship through clearly defined access and use privileges. 8.<br />

Focus on the decision-making process so that sound information and science is incorporated<br />

into decisions. 9. Create local economic incentives for conserving biodiversity and ecosystem<br />

services. 10. Address the drivers of international trade that threaten reefs, from fishing to<br />

tourism to other extractive industries.<br />

23-72<br />

Ecological Criteria For Prioritizing Wider Caribbean Reefs in Need Of Protection<br />

Judith LANG* 1,2 , Robert GINSBURG 3,4 , Kenneth MARKS 4,5<br />

1 Independent, Ophelia, VA, 2 Marine Geology & Geophysics, RSMAS, <strong>University</strong> of Miami,<br />

Miami, 3 Marine Geology & Geophysics, RSMAS, <strong>University</strong> of Miami, Miami, FL, 4 Ocean<br />

Research and Education Foundation, Coral Gables, 5 Independent, Boca Raton, FL<br />

Reefs with an abundance of healthy corals (including some that are large), ample crustose<br />

coralline algae and little macroalgae, are obvious candidates for protection and conservation.<br />

(Large corals provide habitat space for other organisms as well as larvae for future generations<br />

of framework builders or possible remediation efforts; abundant crustose corallines and sparse<br />

macroalgae signify the probable availability of larval recruitment sites.) To determine whether<br />

or not reefs with these characteristics are actually being protected, an easily calculated benthic<br />

condition index (BCI) based on the AGRRA project’s coral and algal indicators has been<br />

developed. BCI values have been calculated for the over 700 surveys conducted between 1998<br />

and 2004 on reefs in the wider Caribbean that had been stratified by zone (as bank, crest, fore,<br />

patch). This information will be posted online at www.agrra.org to help guide difficult decisions<br />

regarding where to focus local protection and management efforts. For example, sites rated<br />

overall as “well above average” (WAB) occurred in 15 of the 22 nations or territories and on 29<br />

of the 50 insular or continental shelf units that were surveyed. Nearly half of these WAB sites<br />

are presently located in a marine protected area (MPA) of some designation. High priority<br />

should be given to protecting the remaining WAB sites, particularly those in areas with few or<br />

no established MPAs. Sites with high values for the macroalgal indicator signify overfishing of<br />

herbivorous fishes or nutrification, and could be further examined for potential causes and<br />

remediation strategies, the efficacy of which could be assessed during future surveys. In the<br />

absence of recent hurricanes or other mechanical damage, a paucity of large corals indicates<br />

poor environments for net reef growth, although other reasons may exist for their conservation.<br />

213

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