Hi to all,
It has been heartening to get some positive comments from this forum about our work in Reef Check. I am including some preliminary results of MAQTRAC surveys we have done so far for those who are interested. This is just one of the areas that Reef Check has done some work on top of those in Indonesia.
This is just a section of an Area Profile that we have been preparing for each area. An Area Profile basically is a baseline study of an area. It covers a description of the area, status of coastal habitats and fisheries, socio-economic situation, the marine ornamental business, management initiatives and recommendations among others. The Reef Check section is still evolving but basically covers the Fisheries Management Report. The Area Profile will be the basis of the Collection Area Management Plan to be drafted by a local management commitee and the collectors.
The Area Profile is then fedback to the ornamental collectors in the area and the other local stakeholders (such as local government officials) for validation and discussion.
(The figures have been lost in pasting the file somehow.)
V. PRELIMINARY RESULTS OF THE MAQTRAC UNDERWATER SURVEYS IN NEW BUSUANGA, PALAWAN
A. Summary of Results
Total Coral Reef Area 15,661,056 m2
Catch limits set for fish species 208 species
Catch limits for invertebrate species 18 species/groups
Live Hard Coral Cover over the whole survey 38% (fair)
Number of species requiring close monitoring in catch records and in future surveys 15 fish species
B. Methods used to collect the data
The Marine Aquarium Trade Coral Reef Monitoring Protocol or MAQTRAC has been designed by Reef Check in partnership with the Marine Aquarium Council as a protocol to monitor coral reefs. It is also one of the tools in the management of the aquarium trade consistent with the principles of sustainable use.
The main objectives of MAQTRAC are:
1. to describe the stocks (e.g. abundance and size classes) of ornamental fish and invertebrates in the area;
2. to provide a scientific basis for collection limits (e.g. total allowable catch or TAC);
3. to measure over-all coral reef health;
4. to determine the impact of local collection; and
5. to recommend sites for no-take zones.
Manta tow surveys (large scale coral reef health survey)
Manta tows were conducted across the reef front of New Busuanga to determine coral reef condition over a large spatial scale. The manta tow survey involves towing the diver in snorkel in a slow boat speed. The diver records the per cent live hard coral cover (in categories) along the tow track usually following the edge of the reef’s crest. A single tow last about 3 minutes and covers around 150 m of reef front. Habitats and their spatial extent are also mapped during these tows. The latter data are important in determining the location of detailed underwater surveys.
Site Selection (for detailed underwater surveys)
Sites were identified before the actual surveys based on their degree of exposure and reef type. These initial sites identified are later verified during the manta tow surveys. The collectors also identified their traditional sites during initial interviews in the community workshop, that guided the survey scientists in the location of underwater surveys.
There was a need for a site sub-sampling routine since the linear extent of New Busuanga’s reef front was too long for the a two- week MAQTRAC survey. In the sub-sampling routine, a total number of 16 collection sites identified representing a wide range of habitats. There are no-take marine protected areas in New Busuanga. Therefore, surveys could not be conducted in no-collection sites.
Some of the reefs were also inaccessible to survey. For instance, surveys were not allowed within a large area in mid- to southern San Isidro Island because it is within a concession of a pearl farm. The whole western section of Black Island was inaccessible due to strong wave action that prevented the surveys.
Timed swim surveys (ornamental and reef health fish indicators)
Timed swims are stop-and-start surveys each covering 500 m2 of reef area. This survey protocol has been developed for mainly recording ornamental fish species and reef health fish indicators’ abundances. These surveys are conducted across the major coral reef zones (reef slope, crest and flat) and seagrass and algal beds. The per cent live hard coral cover (using categories during the manta tow surveys) is also estimated in each timed swim.
Three timed swims were conducted in each coral reef zone and in seagrass and algal beds in each of the identified site. All of the marine aquarium target fish both currently and potentially traded were counted and their sizes estimated in these detailed surveys. In addition, coral reef health fish indicators (Reef Check plus surgeonfishes, rabbitfishes and fusiliers) were also recorded.
Belt transect surveys (ornamental and reef health invertebrate indicators and coral cover)
Belt transect surveys involve deploying a transect line across the reef bottom. It is a ‘belt’ survey because an area is covered using the line as a ‘ruler’ guide. The line is laid parallel to the shore and is meant to survey a uniform habitat (usually of the same depth). In reefs that form spur-and-grooves, the transect line is laid following the reef as long as the widths along the line don’t overlap. If not, then the line is laid across the spurs-and-grooves.
The transect line is 100 m in length, 5 m in width (2.5 m on each side) and 2.5 m in height. It is divided into 4 segments: 0 – 20 m, 25 – 25 m, 50 – 70 m, and 75 – 95 m. These segments function as statistical replicates in later analyses.
Belt transect surveys were undertaken to survey the abundance of ornamental invertebrates and of reef health invertebrate indicators in two depths (< 5 m and 10-15 m) in each site. Detailed site coral reef health is determined from the reef substrate cover data of points systematically sampled along the line.
Calculating Total Stock Abundances
The abundances of ornamental stocks in an area were estimated based on average densities, standard deviation, 95% confidence interval and the coral reef area. The coral reef area was estimated from satellite maps and available navigational maps.
Locations of Potential No-Take Zones
Potential no-take zones were identified and recommended based on the high density of ornamental targets, live hard coral cover and the practicality of monitoring and enforcement (e.g. presence of a nearby settlement). Several potential no-take zones are identified as options.
C. Preliminary MAQTRAC Results
1.) The MAQTRAC underwater surveys recorded over 26,000 individuals belonging to 208 ornamental fish species within the waters of barangay New Busuanga.
Approximately 19 species/species groups of ornamental invertebrates were also recorded during the MAQTRAC underwater surveys
2.) The manta tow surveys indicated kilometer scale variabilities in hard coral cover. Live hard coral cover categories ranged from 1 to 4. However, these variabilities were not large. Categories did not change dramatically in adjacent reefs.
3.) The large scale live coral survey indicated an average of 2.3 in the category. This translates to around 30% live hard coral cover in the whole reef of New Busuanga. This means that the coral cover or health is considered fair. (0 to 25%= poor; 26 to 50% = fair; 51 to 75% = good; 76 to 100% = excellent). The information of live hard coral cover distribution across the New Busuanga reefs.
4.) The fine-scale substrate surveys in the 16 sites also indicated variability in the distribution of live hard coral cover. Live hard coral cover ranged from 9 to 61% with an average of 38%.
5.) The live hard coral cover estimates from the detailed surveys (point sampling technique) was highly similar to the data derived from the large scale surveys (manta tow technique), average of 38% versus 30%.
6.) Tagisi Reef had the highest live hard coral cover (61%) while Black Rock had the lowest cover (9%). Live hard coral cover categories ranged from 1 to 4. The reefs of Black Rock have been the sites of destructive fishing methods (e.g. trawling that scrape the reef substratum) to account for its low cover. Corollarily, some of the sites with relative protection had higher live coral cover. The latter include the reefs in San Isidro (in the vicinity of a pearl farm), and Panlalaitan and Bacbac (local monitoring)
7.) There are no no-take marine protected areas in New Busuanga. However, the community is in the process of establishing one in the vicinity of Kabilbil reefs. This is one of the sites with high ornamental fish densities.
8.) There is a need to expand no-take marine protected areas. We recommend San Isidro I as a site for expansion. The reef in this site is both high in densities of invertebrate and fish ornamentals. Enforcement is also practical given it is in the vicinity of a pearl farm. We also recommend the reefs of Panlalaitan as another expansion site given its high fish ornamental density and local enforcement banning destructive fishing methods.
Conclusion:
What we have noticed so far is that local stakeholders including collectors and government officials have been receptive of our management recommendations. Of course, recommendations are discussed among collectors and other villagers with the area managers and community organizers to promote collaboration towards managing the local ornamental trade.
Yours,
Domingo Ochavillo
Reef Check Scientist