Christopher Kri U (2001) Colonisation and growth of marine animals on
artificial reefs at Batu Penyu, Talang-Satang National Park, Malaysia. Hornbill
5:nn-nn
COLONISATION AND GROWTH OF MARINE ANIMALS ON
ARTIFICIAL REEFS AT BATU PENYU, TALANG-SATANG NATIONAL PARK, MALAYSIA
CHRISTOPHER KRI ANAK UBANG1
SUMMARY
The artificial reefs at Talang-Satang National Park
were constructed for marine conservation using concrete reef balls.
Since 1998 about one thousand reef balls have been deployed around the
coast of Sarawak. This is the first reef ball project in Asia and was
instigated for conservation purposes. The National Park has important
turtle nesting beaches, and reef balls are used to stop trawlers from
trawling within the resting areas used by turtles during the nesting
season.
This study focused on the presence and absence of
easily visible marine life on or using the reef balls at an artificial
reef at Batu Penyu within Talang-Satang National Park, and did not
attempt to identify organisms to species level. It was found that reef
balls are colonised by a range of marine animals and the colonisation
rate is very encouraging. The reef balls were tagged for future
monitoring. Future studies should include collection and identification
to species level to compare the diversity of artificial reefs with
natural reefs.
Reef balls appear to be successful as a basis for the
growth of new coral reefs. For the purpose of conservation, decisions on
the material used should be based on comparative studies of different
types of artificial reefs.
INTRODUCTION
The artificial reefs at Talang-Satang National Park
were created in 1998 using reef balls. Reef balls are constructed using
cement with the same pH as salt water, using special mixtures and micro
silica. This ensures that reef balls mimic the natural reef limestone
and remain stable. Reef balls can be used to promote regeneration of
damaged reef areas, to anchor mooring and marker buoys, and to create
recreational SCUBA diving sites, improved fish habitat and lobster
nurseries. Reef balls are also useful to stop trawling because they have
sharp textured surfaces, which are capable of ripping trawler nets.
The objective of this study is to collect information
on the presence and absence of marine organism living on the reef balls
deployed in 1998 at Talang-Satang National Park near Batu Penyu, about
two kilometres away from Pulau Talang-Talang Besar. No previous research
or monitoring programmes have been done by the Forest Department on reef
balls.
METHODOLOGY
Out of a total of 180 reef balls making up the
artificial reef, six reef balls of each size (small, medium and large)
were selected and tagged. Methods for random sampling were considered,
but proved impractical when diving.
Sessile animals
A piece of wire mesh 50 cm x 50 cm was placed on the reef balls
forming 25 squares each 10 cm x 10 cm. For hard and soft corals, sponges
and barnacles, the proportion of squares in which they were present was
recorded. Where a patch of coral was centred in one square but
overlapped an adjacent square, it was only counted once.
Mobile animals
The numbers of individual sea urchins, molluscs and fish seen on or
in the reef balls or using the reef balls (e.g. feeding on the surface)
were recorded.
For this study only the large and easily identified
animals were recorded. The observation did not count bivalves, which are
encrusted with other marine life (e.g. barnacles) and difficult to
distinguished separately. No specimens were taken for identification.
RESULTS
The number of sessile animals recorded is shown in
Table 1. The numbers for mobile animals seen are shown in Table 2; many
crabs and shrimps were seen, but it was impossible to count them
properly because they fled rapidly. No cuttlefish were seen.
Table 1: Percentage of reef balls colonised and
average cover
|
Sessile animals |
% of reef balls colonised |
% of 10 x 10cm squares colonised |
|
Small |
Medium |
Large |
Small |
Medium |
Large |
|
Hard coral |
100 % |
100 % |
100 % |
21 % |
46 % |
56.7 % |
|
Soft coral |
83 % |
100 % |
66 % |
7.3 % |
32 % |
16 % |
|
Sponges |
83 % |
16 % |
83 % |
11.3 % |
0.3 % |
20 % |
|
Barnacles |
100 % |
100 % |
100 % |
72 % |
80 % |
68 % |
Table 2: Total numbers and average of invertebrates
and fish per reef ball
|
|
Total |
Average numbers per reef ball |
|
Small |
Medium |
Large |
|
Invertebrates |
|
Sea urchin |
24 |
0.6 |
0.83 |
2.16 |
|
Lobster |
4 |
0 |
0.33 |
0.33 |
|
Molluscs |
34 |
4.0 |
0.5 |
1 |
|
Nudibranch |
2 |
0.17 |
0 |
0.33 |
|
Fishes |
|
Butterfly fish |
8 |
0.33 |
0.5 |
0.66 |
|
Angelfish |
11 |
0.5 |
0.66 |
0.66 |
|
Snapper |
17 |
0.8 |
0.5 |
1.5 |
|
Grouper |
2 |
0.17 |
0 |
0.16 |
|
Sweetlips |
2 |
0 |
0 |
0.33 |
|
Puffer fish |
1 |
0 |
0 |
0.16 |
|
Parrot fish |
17 |
0.83 |
1.16 |
0.83 |
DISCUSSION
Method
The method used is suitable for sessile and slow moving animals but
not good for lobsters and crabs because they flee. There is also a
problem of identifying early stages of growth, so only adults were
recorded. Because the reef balls were tagged, it will be possible to
repeat the survey in future years and track colonisation and growth.
This is the first reef balls project in Malaysia, so no comparisons are
available. Information from Marine Fisheries Department in Sarawak on
shipwreck and tyre reef monitoring is also unavailable.
Colonisation of reef balls
The results from the study are very promising as there is visible
growth of coral and other marine life on the reef balls. After two and a
half years, all the reef balls studied had been colonised by hard
corals, and barnacles, and most of them by soft corals and sponges. The
reef balls are used by large numbers of crabs and lobsters, and typical
reef fish such as angelfish and butterfly fish.
CONCLUSIONS
Reef balls can be very effective for marine
conservation, as a wide range of marine animals use them, either living
on them or using them for shelter or as feeding grounds.
Although this study only looked at the presence and
absence of easily visible marine life on the reef balls, this
information will help in planning more detailed research in the future.
Specimens should be collected and identified to species level to compare
diversity with natural and other types of artificial reefs. Long term
monitoring studies of the tagged reef balls would give information on
the rate of colonisation and growth of marine animals. Similar studies
on other types of artificial reefs, such as tyres, wrecks and building
waste should be carried out for comparison.
Reef balls are also effective for preventing
trawling, and are especially useful near turtle nesting beaches. More
reef balls could be deployed to build reefs for recreational SCUBA
diving, as they are used by attractive reef fish.
Reef balls appear to be successful as a basis for the
growth of new coral reefs.
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