11th ICRS Abstract book - Nova Southeastern University

More documents

Recommendations

Info

23.1009 Managing Coral Reef in Indonesia. Lesson Learn From Coral Reef Rehabilitation And Management Program suharsono SUHARSONO* 1 1 Resarch Center for Oceanography, Indonesian Institute of Sciences, Jakarta, Indonesia The Indonesian Government has launched Coral Reef Rehabilitation and Management Program (COREMAP) since 1998. It is aimed to enhance the health of coral reef and to increase the prosperity of costal community who depends much on the coral reefs ecosystem for their existence. Evaluation activities indicated that the success of the program of saving coral reef is primarily due to the success of the program component of community awareness, community surveillance, monitoring of coral reef health and training program. The components of community awareness and surveillance have given the most significant impact in reducing the rate of coral reef degradation. The most effective method for the community awareness program is trough television media as well as through the involvement of the community chief , be it an informal leader or government official, that actively campaigning on the importance of coral reef for the community. Handing over the right to manage and control the resource to the community has shown significant effect in increasing the catch which in turn increasing community income. Scientifically monitoring the coral reefs health as well as the socio-economic condition of the coastal people have been continuously done. The role of public communication component which produce a variety of dissemination products also has a big share in spreading up research products so that they can be absorbed and applied by the community. Training program without on the job guidance for certain period of time would surely fail. The success of training program and community guidance to do monitoring coral reef condition, supervision and training on how to diversify various fishery products and marketing constitute the main factor for the continuation of this program. Research Center for Oceanography, Indonesian Institute of Sciences Jl. Pasir Putih I, Ancol Timur Jakarta Utara 11048, Indonesia Email: director-rco@indo.net.id . 23.1010 An Ecological Correction to Marine Reserve Boundaries in the US Virgin Islands Rafe BOULON* 1 , Mark MONACO 2 , Alan FRIEDLANDER 3 , Chris CALDOW 2 , John CHISTENSEN 2 , Caroline ROGERS 4 , James BEETS 5 , William MILLER 6 1 Resource Management, VI National Park/Coral Reef NM, St. John, Virgin Islands (U.S.), 2 NOAA, Silver Spring, MD, 3 The Oceanic Institute, Waimanalo, HI, 4 USGS, St. John, Virgin Islands (U.S.), 5 Univ. of Hawaii, Hilo, HI, 6 National Park Service - I&M, St. John, Virgin Islands (U.S.) Marine reserves and other marine protected areas (MPAs) are important tools for management of marine ecosystems. Ecological and biological criteria are often not feasible to consider when establishing protected areas. In 2001, the Virgin Islands Coral Reef National Monument (VICR) in St John, US Virgin Islands, was established by Executive Order. The VICR boundaries were based on administrative determination of Territorial Sea boundaries and land ownership at the time of the Territorial Submerged Lands Act of 1974. The VICR prohibits almost all fishing and other extractive uses. Surveys of habitat and fishes inside and outside of the VICR were conducted in 2002– 2007. Based on surveys from 2002 to 2004, areas outside the VICR had significantly more hard corals; greater habitat complexity; and greater richness, abundance and biomass of reef fishes than areas within the VICR. The administrative (political) process used to establish the VICR did not allow a robust ecological characterization of the area to determine the boundaries of the MPA. Because of reduced habitat complexity within portions of the existing VICR, the enhancement of the marine ecosystem may not be fully realized and/or increases in economically important reef fishes may take longer to detect. Efforts are under way with the VI Delegate to Congress to increase amounts of complex reef habitat within the VICR by swapping a part of the VICR that has little hermatypic coral reef habitat for a wedge-shaped Territorially-owned area within the VICR that contains a coral reef with higher hermatypic coral cover. The simplification of the boundary will also enhance enforcement by reducing the confusion of fishermen and rangers as to where fishing is allowed. Poster Mini-Symposium 23: Reef Management 23.1011 St Croix East End Marine Park: The U.S. Virgin Islands’ First Territorial Marine Park Norman QUINN* 1 , John FARCHETTE 2 , Karlyn LANGJAHR 2 , Paige ROTHENBERGER 2 1 Department of Natural Resources, St Croix East End Marine Park, Frederiksted, Virgin Islands (U.S.), 2 Department of Natural Resources, St Croix East End Marine Park, Christiansted, Virgin Islands (U.S.) Established on January 15, 2003, the St. Croix East End Marine Park (STXEEMP) is the U.S. Virgin Islands’ first marine park and represents the culmination of three years of collaboration between the federal and local government, non-governmental organizations, business representatives and other stakeholders. The park will protect the largest island barrier reef system in the Caribbean. As well as protecting significant marine resources the park is designed to promote sustainability of marine habitats, including coral reefs, sea grass beds and mangrove habitats and to preserve significant natural areas for the benefit of future generations. The STXEEMP is on the eastern end of St. Croix extending from the high tide boundary to the three nautical mile territorial waters limit and encompasses 155.4km2. The multi use design has four different managed areas: Recreation Management, Turtle Wildlife Preserve, No-Take and Open. The Recreation Management Areas (2.8%) are designated for snorkeling, diving, recreational fishing, bait fishing and boating while preserving resources. The Turtle Wildlife Preserve Area (7.0%) protects turtle nesting beaches for Green, Hawksbill and Leatherback turtles. The No Take Areas (8.6%) protect spawning, nursery, and residence habitat for various species. A monitoring program is designed to collect scientific information to assist in the wise management of these habitats and species to ensure that these marine resources are available in the future. The Open Areas comprise 81.6% of the park, encompassing all areas that are not otherwise delineated. Existing territorial restrictions govern the use of these areas; the only marine park restriction is the prohibition of the removal of coral or live rock in these areas. The park’s education and outreach program’s goals are to facilitate environmental awareness opportunities for the community, encourage a sense of user stewardship regarding the marine environment and promote the awareness of and support for the park. 23.1012 The Use Of Simulated Visible/infrared Imager/radiometer Suite (Viirs) And Landsat Data Continuity Mission (Ldcm) Imagery For Coral Reef Monitoring Leland ESTEP* 1 , Joe SPRUCE 2 , Slawomir BLONSKI 2 , Roxzanna MOORE 2 1 SSAI, Midland, TX, 2 SSAI, Stennis Space Ctr, MS The use of Rapid Prototyping Capability (RPC) technology resident to NASA Stennis Space Center (SSC), MS, was used to spectrally and spatially simulate NASA next-generation sensor imagery and environmental data products over two well-known coral reef areas – Looe Key, FL, and Kaneohe Bay, HI. The study purpose was to perform a preliminary assessment on the capability of next-generation sensor systems, the Visible/Infrared Imager/Radiometer Suite (VIIRS) and the Landsat Data Continuity Mission (LDCM), to provide key data inputs to the National Oceanographic and Atmospheric Administration (NOAA) Integrated Coral Observing Network (ICON)/Coral Reef Early Warning System (CREWS) Decision Support Tool (DST). The DST data layers derived from the simulated imagery included maps depicting water quality parameters (chlorophyll (Chl) and the absorption coefficient (a)) and benthic habitat type. The input, or parent, imagery used by the RPC for simulation of VIIRS and LDCM imagery included spaceborne (Hyperion) and airborne hyperspectral data (AVIRIS). Water quality and benthic classification reference data (e.g., from field surveys) was used to validate simulated data products. The results of this study suggests that next generation NASA sensors can provide valuable data inputs to the NOAA’s ICON/CREWS DST, assuming data quality of the actual future sensors approximates original specifications. 489
23.1014 Second And Third Order Management Issues in South Sinai Protected Reef Areas Rupert ORMOND* 1 , Wera LEUJAK 2 , Mohammed SALEM 3 , Ayman MABROUK 3 1 SaveourSeas Foundation, West Lothian, United Kingdom, 2 <strong>University</strong> Marine Biological Station Millport, <strong>University</strong> of London, Isle of Cumbrae, United Kingdom, 3 South Sinai Protectorates, Egyptian Environmental Affairs Agency, Sharm El Sheikh, Egypt Over the last 15 years the whole of the Egyptian coast of the Gulf of Aqaba has been incorporated within a series of Marine Protected Areas. The relevant authorities (Egyptian Environmental Affairs Agency) have effectively implemented a series of first order management objectives. However the region has been promoted so successfully that some reef areas are now subject to a greater intensity of visitor use than any others worldwide. Quantitative studies have elucidated a series of second order management issues: i. The most popular reef sites are being so heavily used that, through incidental trampling and breakage, coral cover has declined, and at some sites the reef assemblage been changed. ii. Largely as a consequence of this impact, and Crown-of-thorns starfish outbreaks, coral cover now appears to be in decline across the region. iii. Public awareness initiatives have increased the care that visitors from traditional tourist source countries take to avoid coral damage, but there has been a recent large increase in the proportion of other tourists with little knowledge of or concern for marine life. iv. With even larger numbers of developments and visitors, infringements of MPA regulations are becoming increasingly evident. In response, the EEAA has supported research addressing a number of key third order issues: a) What are the carrying capacities of different types of reef area? Data suggest that ecological carrying capacities may not be clearly defined, while at heavily used sites social carrying capacity may be the more important issue. b) How can the behaviour of visitors with little concern for coral protection be more effectively controlled? Sanctions against tour operators and tour group leaders may be as important as positive publicity campaigns. c) How effectively can the tools of integrated coastal zone management be applied to mange visitor behaviour as well as tourist development? 23.1015 Community Participation in Coral Reef Management On Phuket Island, Thailand Pitul PANCHAIYAPHUM 1 , Hansa CHANSANG* 2 , Krawi ONGSORANACOMKUL 3 , Anuwat NATEEWATTANA 4 1 Department of Marine and Coastal resources, Phuket, Thailand, 2 Phuket Marine Biological Center, Phuket, Thailand, 3 Department of Fisheries, Phuket, Thailand, 4 Department of Marine and Coastal Resources, Bangkok, Thailand In Thailand a pilot project in community participation in managing reefs of Phuket Island has been initiated since 1992. The communities along the west coast have been benefit from tourism by changing their occupation from coastal fisheries to tourism related occupation. They were encouraged in setting up associations which participated in various activities i.e., installation and maintenance of mooring buoys and assisting authorities in surveillance of illegal activities. The network of associations has been formed to exchange information and experiences among various groups. Increasingly the network began to settle the conflicting issues of reef resources among themselves. Parts of the activities were also supported by local government and private sectors. At present, the communities still depend upon supports from authorities in various ways i.e. some financial and logistic supports, and information regarding successful management elsewhere. In conclusion it is shown that transferring management responsibility of reef resources to local communities is possible but it is a long term process. Close cooperation between government officials and communities is the key of success. Poster Mini-Symposium 23: Reef Management 23.1016 Improving Governance Of Marine Protected Areas Through Inter-Local Government Collaboration in Central Philippines Rizaller AMOLO* 1 , Rose-Liza EISMA-OSORIO 2 1 Local Governance for Coastal Management Project, Coastal Conservation and Education Foundation Inc., Cebu City, Philippines, 2 Coastal Conservation and Education Foundation Inc., Cebu City, Philippines Establishment of no-take marine protected areas (MPAs) in the Philippines has become an efficient approach to address coral reef degradation and decline in reef fishery production by numerous local governments. In Central Visayas, Philippines, over 400 MPAs both declared by local ordinances and through the National Integrated Protected Areas System Act were established to improve marine habitats and increase fishery resources. However, only 20-25% has been effectively managed by local government units (LGUs) along with their constituents. Achieving its objectives, there is a need for LGUs to collaborate strategies to improve MPA management and maximize benefits. This paper examines the effect of collaboration of the LGUs in Southern Cebu and Siquijor province, in improving reef management by looking into various outcomes of effective governance. A 3-year biophysical monitoring of MPAs showed significant changes in benthic community and reef fish population. MPA governance rating has improved overtime. Effective coastal law enforcement within and outside MPAs has increased. Various strategies such as collecting user fee, joint enforcement effort, and effective community education and information dissemination were found to also be an emerging approach to increase support in management. Lesson learned in inter-local government collaboration includes: clarify organizational requirement prior to effective program implementation and effective joint law enforcement plays a crucial role to sustain collaborative support. 23.1017 Recreational Diving Management in the Coral Reefs of Cozumel, Mexico Luis SANTANDER* 1 1 Division de Desarrollo Sustentable, Universidad de Quintana Roo, Cozumel, Mexico The general objective is twofold: i) a review of the management principles and actions aimed to reduce the negative impacts of recreational diving in coral reefs; and, ii) point out the shortcomings of such principles and actions in Cozumel’s MPA (Marine Protected Area). The paper has a presentation and discussion of two principles and strategies for MPA: zoning and carrying capacity. The study includes a selection of other specific measures and actions designed to reduce the environmental impacts of recreational diving and it also deals with the characteristics and tendencies of the industry of recreational diving. After the analysis of the international experiences in the management of recreational diving in coral reefs in MPA, the analysis is centered in Cozumel’s MPA, mainly with data obtained from monitoring over 350 divers and 82 diving groups. The quantitative results of physical contacts and sediment removals due to divers is explained in relation to behaviours and omissions of instructors and diving guides that fall beyond the scope of principles, policies and actions contained by management plans for recreational diving. The main conclusion is that general management principles of MPA are usefull and important but have shortcomings. For example, i) carrying capacity (number of divers) can change drastically with different divers’ profile and diving practices, or ii) restrictions in a zone not necessarily mean that the consequences of negative impacts in a nearby area of intensive use, are absent on the former. When it comes to standard actions to protect reefs from divers the main limitations come from the great diversity of physical and biological features of sites and from the different behaviours of divers. 490
Page 2 and 3:
Contents Sponsors..................
Page 4 and 5:
Sponsors 11th ICRS Co-Sponsors Barr
Page 6 and 7:
Mini-Symposium Co-Chairs Mini-Sympo
Page 8:
Mini-Symposium 23: Reef Management
Page 12 and 13:
Plenary Lessons from the Past Malco
Page 14:
Plenary Drivers of Coral Infectious
Page 18 and 19:
1-1 The R/v Alpha Helix Symbios Exp
Page 20 and 21:
1-9 Coral Community Change Over A C
Page 22 and 23:
1-17 Holocene Reef Development At T
Page 24 and 25:
1-25 Paleoecology Of Mio-Pliocene F
Page 26 and 27:
Oral Mini-Symposium 2: Biotic Respo
Page 28 and 29:
Oral Mini-Symposium 2: Biotic Respo
Page 30 and 31:
Oral Mini-Symposium 3: Calcificatio
Page 32 and 33:
Oral Mini-Symposium 3: Calcificatio
Page 34 and 35:
3-17 The Effect Of Depressed Aragon
Page 36 and 37:
Oral Mini-Symposium 4: Coral Reef O
Page 38 and 39:
Page 40 and 41:
Page 42 and 43:
Page 44 and 45:
Oral Mini-Symposium 5: Functional B
Page 46 and 47:
Page 48 and 49:
Page 50 and 51:
Page 52 and 53:
Page 54 and 55:
Page 56 and 57:
Oral Mini-Symposium 6: Ecological a
Page 58 and 59:
Page 60 and 61:
Page 62 and 63:
Page 64 and 65:
7-5 Coral Yellow Band Disease; Curr
Page 66 and 67:
7-13 Black Band Disease (BBD): A Po
Page 68 and 69:
7-21 Coral Host Processes Associate
Page 70 and 71:
7-29 Can the Presence of Disease Si
Page 72 and 73:
7-37 Developing An Expert System Fo
Page 74 and 75:
7-45 The Effect Of Sediment And Hea
Page 76 and 77:
8-1 From Bacterial Bleaching To The
Page 78 and 79:
8-9 Milkfish Feces Share Common Bac
Page 80 and 81:
8-17 Bacteria Associated With Symbi
Page 82 and 83:
8-26 Photosynthetic Microorganisms
Page 84 and 85:
8-35 Tissue Loss And Tropical Storm
Page 86 and 87:
9-5 Evaluation Of Biotic And Abioti
Page 88 and 89:
9-13 Is Allelopathy Involved in Cor
Page 90 and 91:
Oral Mini-Symposium 10: Ecological
Page 92 and 93:
Page 94 and 95:
Page 96 and 97:
Page 98 and 99:
Page 100 and 101:
10-41 Substrate Effects On Reef Fis
Page 102 and 103:
Page 104 and 105:
Page 106 and 107:
Page 108 and 109:
Oral Mini-Symposium 11: From Molecu
Page 110 and 111:
Page 112 and 113:
Page 114 and 115:
Page 116 and 117:
Page 118 and 119:
12-5 The Contribution Of Heterotrop
Page 120 and 121:
12-14 Ocean Dynamics Drive Coral Re
Page 122 and 123:
12-23 Coral Reef Resilience To Chro
Page 124 and 125:
13-1 Prioritizing Conservation Hots
Page 126 and 127:
Oral Mini-Symposium 13: Evolution a
Page 128 and 129:
14-6 Modelling Coral Larval Dispers
Page 130 and 131:
14-14 Environmentally-Mediated Vari
Page 132 and 133:
14-21 Same, Same, But Different: Co
Page 134 and 135:
14-29 Complex Patterns of Genetic C
Page 136 and 137:
14-37 Genetic Connectivity in Phili
Page 138 and 139:
14-45 Range-Wide Population Genetic
Page 140 and 141:
14-55 The Importance Of Behavior On
Page 142 and 143:
Oral Mini-Symposium 15: Progress in
Page 144 and 145:
Oral Mini-Symposium 15: Progress in
Page 146 and 147:
Oral Mini-Symposium 16: Ecosystem A
Page 148 and 149:
Page 150 and 151:
Page 152 and 153:
Page 154 and 155:
Page 156 and 157:
Page 158 and 159:
Oral Mini-Symposium 17: Emerging Te
Page 160 and 161:
Page 162 and 163:
Page 164 and 165:
Page 166 and 167:
Page 168 and 169:
18-5 Coral Reef Habitat Around New
Page 170 and 171:
18-13 Response Of High Latitude Her
Page 172 and 173:
18-21 Socio-Economic Monitoring (So
Page 174 and 175:
18-29 Extent And Timing Of Disturba
Page 176 and 177:
18-37 It Depends On Where You Look:
Page 178 and 179:
18-45 New Insights Into The Exposur
Page 180 and 181:
Oral Mini-Symposium 19: Biogeochemi
Page 182 and 183:
Page 184 and 185:
Page 186 and 187:
Page 188 and 189:
Oral Mini-Symposium 20: Modeling Co
Page 190 and 191:
Oral Mini-Symposium 20: Modeling Co
Page 192 and 193:
21-9 Integrated Economic Valuation
Page 194 and 195:
21-19 Towards Local Fishers Partici
Page 196 and 197:
21-27 The Political Aspects Of Resi
Page 198 and 199:
21-37 Exploitation And Trade Of Cor
Page 200 and 201:
22-1 Complex Ecological Effects Of
Page 202 and 203:
22-9 Comparative Evaluation Of Reef
Page 204 and 205:
22-17 Managing Fishing Gear To Enco
Page 206 and 207:
22-25 Estimating Harvest Pressure O
Page 208 and 209:
22-33 Are The Coral Reef Finfish Fi
Page 210 and 211:
22-41 Using Length-Frequency Data T
Page 212 and 213:
22-50 Changes in Ecosystem Structur
Page 214 and 215:
23-5 Measuring Success in Managing
Page 216 and 217:
23-13 Some Hints About The Impacts
Page 218 and 219:
23-21 Fishery Management For Artisa
Page 220 and 221:
23-29 “To Live With The Sea”; D
Page 222 and 223:
23-37 Challenges Facing An Mpa Mana
Page 224 and 225:
23-45 Assessing Global Coral Reef M
Page 226 and 227:
23-53 Developing A Model For Ecosys
Page 228 and 229:
23-61 Mitigating The Effects Of Cor
Page 230 and 231:
23-69 Restore Or Not To Restore? Vl
Page 232 and 233:
24-1 Fates Of Restored Acropora Pal
Page 234 and 235:
24-9 Sponge-Mediated Coral Reef Res
Page 236 and 237:
24-17 Coral Community Restorations
Page 238 and 239:
24-25 Development Of A Coral Nurser
Page 240 and 241:
24-33 Transplantation of Porites lu
Page 242 and 243:
24-41 Scleractinian Coral Relocatio
Page 244 and 245:
24-50 Gametogenesis in Cultured Ver
Page 246 and 247:
Oral Mini-Symposium 25: Predicting
Page 248 and 249:
Page 250 and 251:
Page 252 and 253:
Page 254 and 255:
Page 256 and 257:
Page 258 and 259:
Page 260 and 261:
Oral Mini-Symposium 26: Biodiversit
Page 262 and 263:
Page 264 and 265:
Page 266 and 267:
Page 268 and 269:
Page 270 and 271:
Page 272 and 273:
26-54 Gene Genealogies Reveal Phylo
Page 274 and 275:
Page 276:
Poster Session
Page 279 and 280:
1.13 Depth-Related Patterns of Infa
Page 281 and 282:
1.20 Grain Size And Sedimentary Con
Page 283 and 284:
1.3 Environmental Effects On Back-R
Page 285 and 286:
Poster Mini-Symposium 2: Biotic Res
Page 287 and 288:
Poster Mini-Symposium 3: Calcificat
Page 289 and 290:
Page 291 and 292:
Page 293 and 294:
Poster Mini-Symposium 4: Coral Reef
Page 295 and 296:
Page 297 and 298:
Page 299 and 300:
Page 301 and 302:
Poster Mini-Symposium 5: Functional
Page 303 and 304:
Page 305 and 306:
Page 307 and 308:
Page 309 and 310:
Page 311 and 312:
Page 313 and 314:
Page 315 and 316:
Page 317 and 318:
Page 319 and 320:
Poster Mini-Symposium 6: Ecological
Page 321 and 322:
7.162 Disease Ecology And Local Pat
Page 323 and 324:
7.170 Coralline Algal Disease in Th
Page 325 and 326:
7.179 Physiological Effects Of Aspe
Page 327 and 328:
7.187 Characterizing Surface Microo
Page 329 and 330:
7.195 How Quickly Does gorgonia Ven
Page 331 and 332:
7.203 Spatial and temporal variabil
Page 333 and 334:
8.210 Quorum Sensing Inhibitory Act
Page 335 and 336:
8.218 Bacterial Communities Associa
Page 337 and 338:
8.226 Bacterial Growth On Coral Muc
Page 339 and 340:
8.234 Functional Diversity of Micro
Page 341 and 342:
8.242 Microbial Community Profile O
Page 343 and 344:
9.248 Chemistry And Ecology Of A Co
Page 345 and 346:
Poster Mini-Symposium 10: Ecologica
Page 347 and 348:
Page 349 and 350:
Page 351 and 352:
Page 353 and 354:
Page 355 and 356:
Page 357 and 358:
Page 359 and 360:
Page 361 and 362:
Page 363 and 364:
Page 365 and 366:
Page 367 and 368:
Page 369 and 370:
Page 371 and 372:
Page 373 and 374:
Page 375 and 376:
Page 377 and 378:
Poster Mini-Symposium 11: From Mole
Page 379 and 380:
Page 381 and 382:
Page 383 and 384:
12.413 Spatial Patterns Of Stony Co
Page 385 and 386:
Poster Mini-Symposium 13: Evolution
Page 387 and 388:
Poster Mini-Symposium 13: Evolution
Page 389 and 390:
14.432 Gene flow of Symbiodinium on
Page 391 and 392:
14.441 Population Genetics Of Spott
Page 393 and 394:
14.449 Mitochondrial Phylogeography
Page 395 and 396:
14.457 Undirect Evidences On The Co
Page 397 and 398:
14.466 South East African, High-Lat
Page 399 and 400:
14.474 Population Genetic Structure
Page 401 and 402:
14.483 Influences Of Wind-Wave Expo
Page 403 and 404:
14.491 Distributions And Diversity
Page 405 and 406:
14.499 Do Mangroves And Seagrass Be
Page 407 and 408:
14.507 Genetic variation of the hyd
Page 409 and 410:
Poster Mini-Symposium 15: Progress
Page 411 and 412:
Poster Mini-Symposium 15: Progress
Page 413 and 414:
Poster Mini-Symposium 16: Ecosystem
Page 415 and 416:
Page 417 and 418:
Page 419 and 420:
Poster Mini-Symposium 17: Emerging
Page 421 and 422:
Page 423 and 424:
Page 425 and 426:
Page 427 and 428:
Page 429 and 430:
Page 431 and 432:
18.599 A Palaeoecological Perspecti
Page 433 and 434:
18.607 Susceptibility Of Corals To
Page 435 and 436:
18.616 Coral Reefs in Costa Rican C
Page 437 and 438:
18.624 Environmental Endocrine Disr
Page 439 and 440:
18.633 Northern Acehnese Coral Reef
Page 441 and 442:
18.641 The Status Of Coral Reefs in
Page 443 and 444:
18.649 The Effects of Increased Sea
Page 445 and 446:
18.658 “Changing Times, Changing
Page 447 and 448:
18.666 Assessing Land Based Inputs
Page 449 and 450:
18.674 Monitoring Of Coral Recovery
Page 451 and 452:
18.682 Seasonal Investigation On St
Page 453 and 454:
18.690 Assessment Of The Coral Reef
Page 455 and 456: 18.698 Distribution Of Seagrasses i
Page 457 and 458: 18.706 Coral Reef Monitoring in the
Page 459 and 460: 18.714 Pacific-Wide Status Of The R
Page 461 and 462: 18.722 Quantitative Underwater Ecol
Page 463 and 464: 18.730 Community Structure Of Reef
Page 465 and 466: 18.738 Morphological Variation In T
Page 467 and 468: 18.746 Decade-Long (1998-2007) Tren
Page 469 and 470: 18.755 Coral Community Composition
Page 471 and 472: 18.763 Changes in Coral Reef Ecosys
Page 473 and 474: 18.771 Bathymetric Distribution Of
Page 475 and 476: Poster Mini-Symposium 19: Biogeoche
Page 481 and 482: Poster Mini-Symposium 20: Modeling
Page 483 and 484: 21.807 The Recreational Value Of Co
Page 485 and 486: 21.815 Dilemma in Coral Conservatio
Page 487 and 488: 22.821 Estimating Populations Of Tw
Page 489 and 490: 22.829 Commercial Topshell, trochus
Page 491 and 492: 22.837 Trajectories Of Ecosystem Ch
Page 493 and 494: 22.845 Ornamental Fish Trade in The
Page 495 and 496: 22.854 Short-Term Recovery Of Explo
Page 497 and 498: 22.863 Marine Protected Areas: Boon
Page 499 and 500: 22.871 Rotary Time-Lapse Photograph
Page 501 and 502: 22.879 Assessing And Mapping The Di
Page 503 and 504: 22.887 Spatial Variations in Elemen
Page 505: 23.1004 Coral Reef Conservation Cam
Page 509 and 510: 23.1023 Why do Divers Dive Where Th
Page 511 and 512: 23.1031 The Colonial Tunicate tridi
Page 513 and 514: 23.1039 Effectiveness Of A Small Mp
Page 515 and 516: 23.893 Man Made Stress Reliever? An
Page 517 and 518: 23.901 Reef Monitoring Project For
Page 519 and 520: 23.909 Patterns Of Spatial Variabil
Page 521 and 522: 23.917 Culture And Updated Traditio
Page 523 and 524: 23.925 Scientific Monitoring And Cu
Page 525 and 526: 23.934 Characterizing Local Stakeho
Page 527 and 528: 23.942 Challenges in Coral Reef Man
Page 529 and 530: 23.951 Coral Reef-Based Tourism And
Page 531 and 532: 23.959 Marine Protected Area Report
Page 533 and 534: 23.967 Reef Watch Monitoring And Ho
Page 535 and 536: 23.975 A Comparison Of The Permanen
Page 537 and 538: 23.984 Damselfish Embryo Assay: Fie
Page 539 and 540: 23.992 The Decline Of Coral Reef Co
Page 541 and 542: 24.1043 Characteristics Of Seagrass
Page 543 and 544: 24.1051 Mass Culture Of acropora Co
Page 545 and 546: 24.1059 Identifying Sediment-Tolera
Page 547 and 548: 24.1067 Growth Of Newly Settled Ree
Page 549 and 550: 24.1076 Herbivore Effects On Coral
Page 551 and 552: 24.1084 Coral Reefs Conservation Pr
Page 553 and 554: 24.1092 Lessons Learned On Demonstr
Page 555 and 556: 24.1100 Proceedings in Shipgroundin
Page 557 and 558:
24.1108 Restoring An Artificial "En
Page 559 and 560:
24.1116 A Newly Established Coral R
Page 561 and 562:
24.1124 Is The Scale Of Your Coral
Page 563 and 564:
Poster Mini-Symposium 25: Predictin
Page 565 and 566:
Page 567 and 568:
Page 569 and 570:
Page 571 and 572:
Page 573 and 574:
Poster Mini-Symposium 26: Biodivers
Page 575 and 576:
Page 577 and 578:
Page 579 and 580:
Page 581 and 582:
Page 583 and 584:
Page 585 and 586:
Page 587 and 588:
Page 589 and 590:
Page 591 and 592:
Memo ..............................
Page 593 and 594:
Authors INDEX Author Session Page A
Page 595 and 596:
Page 597 and 598:
Page 599 and 600:
Page 601 and 602:
Page 603 and 604:
Page 605 and 606:
Page 607 and 608:
Page 609 and 610:
Page 611 and 612:
Page 613 and 614:
Page 615 and 616:
Page 617 and 618:
Page 619 and 620:
Page 621 and 622:
Page 623 and 624:
Page 625 and 626:
Page 627 and 628:
Page 629 and 630:
Page 631 and 632:
Page 633 and 634:
Page 635 and 636:
Page 637 and 638:
Page 639 and 640:
Page 641 and 642:
Page 643 and 644:
Page 645 and 646:
Page 647 and 648:
show all

11th ICRS Abstract book - Nova Southeastern University

You also want an ePaper? Increase the reach of your titles

Delete template?

Save as template?