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________________________________________________________________________
Survey report
Report on
surveys of the Capricorn-Bunker, Swain and Pompey sectors of
the Great Barrier Reef
Dates:
3rd - 22nd January 2010
Vessel: MV Iron Joy
Survey leader:
Mike Emslie
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Image 1.
Declines in coral cover were
recorded on six of eight reefs in the Capricorn-Bunker sector. The
declines were driven by large seas associated with the passage of severe
tropical cyclone Hamish that passed approximately100km to the east in
March 2009. This is a picture taken from the front of Fairfax Island Reef
in 2008 when the coral cover was high.Photo: AIMS LTMP |
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Image 2.
This is a picture taken on the
front of Fairfax Island Reef in 2010 when coral cover was low. This
graphically illustrates the physical damage caused by cyclones to coral
reefs.
Photo: AIMS LTMP |
Summary
Manta tow surveys were completed on eight reefs in the Capricorn-Bunker
sector, four reefs in the Swain sector and two in the Pompey sector of the Great
Barrier Reef (GBR). Detailed surveys for benthic organisms, visual census of
fishes and surveys for agents of coral mortality (SCUBA search) were made on the
same reefs. Preliminary results of the manta tow and SCUBA search surveys are
presented in this report.
Median reef-wide live coral cover declined on the majority of sampled reefs
since previous surveys. Coral cover declined on six reefs in the
Capricorn-Bunkers and on two reefs in the Swains and remained stable on two
other reefs in each sector. Coral cover declined at both reefs in the Pompey
sector. The declines in hard coral cover in the Swain and Pompey sectors were
attributed to severe tropical cyclone Hamish in March 2009; declines in hard
coral cover on Capricorn-Bunker reefs were due to the combined effects of a
large storm in 2008 and Cyclone Hamish in 2009. The manta tow results are
summarised in Tables 1, 3 and 5.
Six crown-of-thorns starfish (COTS) were recorded during manta tow surveys on
three reefs in the Capricorn-Bunkers, whilst three COTS were recorded during
SCUBA searches at Fairfax Reef. This is the second successive survey where COTS
have been recorded on this reef since it was first surveyed in 1991. One COTS
was recorded at Wade Reef in the Swains during manta tow surveys but none were
recorded on any reefs in this sector during the intensive SCUBA search surveys.
Five COTS were recorded at Reef 21-064 in the Pompey sector during manta tow
surveys and eight more were recorded at this reef during SCUBA search surveys.
On reefs surveyed in the Capricorn-Bunkers, with the exception of Erskine and
Fairfax Reefs, the incidence of "white syndrome" (a disease-like necrosis found
particularly on tabulate Acropora spp.) had declined since 2007. The
incidence of white syndrome increased slightly at three reefs in the Swains but
had declined at a fourth reef. The incidence of White syndrome had declined at
both reefs in the Pompey sector. The SCUBA search results are summarised in
Tables 2, 4 and 6.
Evidence of bleaching was minimal: a few individual pallid colonies were seen
on manta tow surveys of the back-reef areas of Lady Musgrave and Hoskyn Island
Reefs and on the front of Broomfield Reef in the Capricorn-Bunker sector. A few
pale colonies of Seriatopora hystrix were recorded in SCUBA searches at
North Reef in the Capricorn-Bunker group and a few pale Fungiids (mushroom
corals) were recorded at Reef 20-353 in the Pompey sector.
Details of the manta tow method can be found in the Standard Operational
Procedure No. 1 [ AIMS
Research - Crown-of-thorns Starfish and Coral Surveys - Standard Operational
Procedure 8] or in the Survey Manual for
Tropical Marine Resources (English et. al.1997). For a full explanation of the
COTS outbreak terminology used in this report, refer to COTS under "Reef Issues"
at the following web-page:
AIMS Research - Reef Monitoring
Capricorn-Bunker Sector
Perimeters of eight reefs were surveyed using manta tow (Table 1). Three
sites on each of these reefs were then surveyed in detail using SCUBA (Table 2).
During manta tows surveys six COTS were observed on three reefs, Boult, Fairfax
and Lady Musgrave, although densities were below outbreak levels and all reefs
in this sector have been classified as No Outbreak. Detailed surveys revealed
only three COTS on a single reef, Fairfax Reef, although these numbers were also
below outbreak levels. This contrasts with the last survey in 2008 when no COTS
were seen on any reef in the Capricorn-Bunker sector. No outbreaks have been
recorded from this sector over the entire history of survey by AIMS.
Since the last surveys in 2008, median reef-wide live coral cover (Table 1)
has declined on six reefs (Boult, Erskine, Fairfax, Hoskyn, Lady Musgrave and
North Reefs) and has remained stable on two others (Masthead Island,
Broomfield). The declines on these reefs were due to a combination of large
storms in 2008, which dramatically reduced cover, and Cyclone Hamish in 2009,
which then further reduced cover to its present level.
SCUBA searches on the intensive survey sites showed that white syndrome
disease was encountered on all reefs in this sector. However, the numbers of
affected colonies were lower than the previous surveys in 2008, though this was
mainly a result of the decline in hard coral cover; particularly table
Acropora colonies that are notably susceptible to this disease. Brown band
disease affected low to moderate numbers of colonies on most reefs, whilst
skeletal eroding band disease was seen on low numbers of colonies on Masthead
Reef.
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Image 3.
Declines in coral cover were
recorded on two of four reefs surveyed in the Swain sector and on both
reefs surveyed in the Pompey sector. These declines were due to the
effects of cyclone Hamish. In this photograph taken on Reef 21-064 a diver
inspects a large chunk of reef framework that has been broken off and cast
down the reef slope by wave action generated by Hamish.
Photo: AIMS LTMP |
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Image 4.
On reefs protected from
fishing coral trout populations appeared to be flourishing despite the
effects of Hamish.
Photo: AIMS LTMP |
Table 1. Summary of manta tow survey results for the Capricorn-Bunker sector.
|
Reef |
Shelf Position |
Tows |
COTS |
COTS per tow |
Median % Live Coral Cover |
Median % Dead Coral Cover |
Median % Soft Coral Cover |
Reef Status |
|
BOULT |
Outer |
41 |
1 |
0.02 |
5 to 10 |
0 to 5 |
0 to 5 |
NO |
|
BROOMFIELD |
Outer |
45 |
0 |
0 |
10 to 20 |
0 to 5 |
0 to 5 |
NO |
|
ERSKINE |
Outer |
23 |
0 |
0 |
5 to 10 |
0 to 5 |
0 to 5 |
NO |
|
FAIRFAX |
Outer |
38 |
4 |
0.11 |
5 to 10 |
0 to 5 |
0 to 5 |
NO |
|
HOSKYN |
Outer |
30 |
0 |
0 |
10 to 20 |
0 to 5 |
0 to 5 |
NO |
|
MASTHEAD |
Outer |
55 |
0 |
0 |
10 to 20 |
0 to 5 |
0 to 5 |
NO |
|
NORTH |
Outer |
39 |
0 |
0 |
10 to 20 |
0 to 5 |
0 to 5 |
NO |
|
LADY MUSGRAVE IS |
Outer |
56 |
1 |
0.02 |
5 to 10 |
0 to 5 |
0 to 5 |
NO |
|
Overall GBR average for last survey - 2008 |
All |
|
|
0.08 |
10 to 20 |
0 to 5 |
0 to 5 |
|
|
Long term average value |
Outer |
|
|
0 |
30 to 40 |
0 to 5 |
0 to 5 |
|
|
Average last survey - 2008 |
Outer |
|
|
0 |
30 to 40 |
0 to 5 |
0 to 5 |
|
Table 2. Summary of SCUBA search survey results for the Capricorn-Bunker
sector.
|
Reef |
Shelf |
COTS
<5cm
|
COTS >5 cm |
COTS >15cm |
COTS >25cm |
WS |
BBD |
BrB |
SEB |
Drupella |
|
North |
O |
0 |
0 |
0 |
0 |
4 |
0 |
0 |
0 |
3 |
|
Broomfield |
O |
0 |
0 |
0 |
0 |
3 |
0 |
1 |
0 |
8 |
|
Erskine |
O |
0 |
0 |
0 |
0 |
28 |
0 |
8 |
0 |
1 |
|
Masthead |
O |
0 |
0 |
0 |
0 |
2 |
0 |
2 |
4 |
5 |
|
Boult |
O |
0 |
0 |
0 |
0 |
6 |
0 |
4 |
0 |
8 |
|
Hoskyn |
O |
0 |
0 |
0 |
0 |
11 |
0 |
17 |
0 |
89 |
|
Fairfax |
O |
0 |
1 |
1 |
1 |
46 |
0 |
19 |
1 |
39 |
|
Lady Musgrave |
O |
0 |
0 |
0 |
0 |
9 |
0 |
1 |
0 |
1 |
|
Overall GBR average for last survey - 2008 |
ALL |
0 |
0.054 |
0.34 |
0.57 |
10 |
0.18 |
3.1 |
6.9 |
8.1 |
|
Long term average value |
O |
0 |
0.039 |
0.14 |
0.096 |
41 |
0.034 |
4.6 |
1.9 |
8 |
|
Average last survey - 2008 |
O |
0 |
0.13 |
0.63 |
0.25 |
20 |
0 |
9.5 |
5.3 |
7.4 |
WS = White Syndrome, BBD = Black Band Disease, BrB = Brown Band Disease, SEB
= Skeletal Eroding Band Disease.
For more information on white syndrome refer to the AIMS web site at:
AIMS Long Term Monitoring - Coral Diseases on the
Great Barrier Reef - Introduction
Swain Sector
Perimeters of four reefs were surveyed using manta tow (Table 3). Three sites
on each of these reefs were then surveyed in detail using SCUBA (Table 4). One
COTS was recorded at Wade Reef in the Swains during manta tow surveys, but none
were recorded on any reefs in this sector during the intensive SCUBA search
surveys. This suggests that the COTS outbreaks that occurred during the early
part of the decade have run their course and that the affected reefs are
beginning to recover.
Median reef-wide live coral cover declined at two reefs, 21-550 and 22-084,
but remained stable on the other reefs in this sector (Table 3). Cover at Reef
22-084 decreased from a moderate (10-20%) level to the very low (1-5%) level
since the last survey in 2008. Reef 21-550 declined from high levels (30-50%) to
moderate (10-20%) since 2008. These declines are most likely attributable to the
effects of severe cyclone Hamish in March 2009. The two reefs that showed little
change in coral cover also felt the effects of Hamish. However areas on these
reefs exposed to strong wave action (back reefs) already had a low coral cover
as a result of past recent COTS outbreaks.
SCUBA searches on the intensive survey sites showed that white syndrome
disease was encountered on all reefs in this sector. Compared to surveys in
2008, the number of infected colonies had increased on three of the reefs, but
declined on the remaining reef (Wade). Brown band disease occurred in low to
moderate numbers of colonies only on Wade and Chinaman Reefs, whilst skeletal
eroding band disease occurred in low numbers of colonies on all reefs except
Reef 21-550.
Table 3. Summary of manta tow survey results for the Swain sector.
|
Reef |
Shelf Position |
Tows |
COTS |
COTS per tow |
Median % Live Coral Cover |
Median % Dead Coral Cover |
Median % Soft Coral Cover |
Reef Status |
|
21-550 |
Mid |
35 |
0 |
0 |
10 to 20 |
0 to 5 |
0 to 5 |
NO |
|
22-084 |
Mid |
19 |
0 |
0 |
0 to 5 |
0 |
5 to 10 |
RE |
|
CHINAMAN |
Mid |
32 |
0 |
0 |
10 to 20 |
0 to 5 |
10 to 20 |
RE |
|
WADE |
Mid |
25 |
1 |
0.04 |
5 to 10 |
0 to 5 |
5 to 10 |
RE |
|
Overall GBR average for last survey - 2008 |
ALL |
|
|
0.08 |
10 to 20 |
0 to 5 |
0 to 5 |
|
|
Long term average value |
MID |
|
|
1.5 |
20 to 30 |
0 to 5 |
0 to 5 |
|
|
Average last survey - 2008 |
MID |
|
|
0 |
10 to 20 |
0 to 5 |
0 to 5 |
|
Table 4. Summary of SCUBA search survey results for the Capricorn-Bunker
sector.
|
Reef |
Shelf |
COTS
<5cm
|
COTS
>5 cm |
COTS >15cm |
COTS >25cm |
WS |
BBD |
BrB |
SEB |
Drupella |
|
21-550 |
M |
0 |
0 |
0 |
0 |
5 |
0 |
0 |
0 |
0 |
|
22-084 |
M |
0 |
0 |
0 |
0 |
8 |
0 |
0 |
1 |
12 |
|
CHINAMAN |
M |
0 |
0 |
0 |
0 |
23 |
0 |
2 |
1 |
6 |
|
WADE |
M |
0 |
0 |
0 |
0 |
58 |
0 |
12 |
5 |
22 |
|
Overall GBR average for last survey - 2008 |
ALL |
0 |
0.054 |
0.34 |
0.57 |
10 |
0.18 |
3.1 |
6.9 |
8.1 |
|
Long term average value |
M |
0.021 |
0.48 |
3.4 |
0 |
11 |
0.18 |
1.4 |
2.6 |
24 |
|
Average last survey - 2008 |
M |
0 |
0 |
0 |
0 |
12 |
0 |
0.5 |
2.2 |
6.8 |
WS = White Syndrome, BBD = Black Band Disease, BrB = Brown Band Disease, SEB
= Skeletal Eroding Band Disease.
Pompey Sector
Two reef perimeters were surveyed using manta tow (Table 5). Three sites on
each of these reefs were then surveyed in detail using SCUBA (Table 6). Five
COTS were recorded at a single reef, Reef 21-064, in the Pompeys during manta
tow surveys, and eight were recorded at this reef during the detailed SCUBA
search surveys. This reef has now been designated as undergoing an Incipient
Outbreak. COTS in these numbers (~ 53 COTS/hectare) would be expected to have a
local impact on live coral cover and are a cause for concern. No COTS were
recorded at Reef 20-353 during either manta or SCUBA surveys.
Median reef-wide live coral cover declined on both reefs surveyed. Reef
22-353 declined from high levels (30 to 50%) in 2008 to very low levels (0 to
10%) in this survey. Reef 21-064 declined from high (30 to 50%) to moderate
levels (10-30%). These declines are most likely attributable to the effects of
severe cyclone Hamish in March 2009 as both reefs lie near to the path of the
cyclone track. However, Reef 21-064 was further away (30km compared to 10km for
Reef 22-353) and somewhat more protected which accounts for the smaller decline
in coral cover.
SCUBA searches on the intensive survey sites showed that white syndrome
disease was encountered on both reefs in this sector, but in very low numbers.
The number of colonies infected decreased on both reefs compared to surveys in
2008. No Black or Brown Band disease occurred on either reef, whilst skeletal
eroding band disease occurred in low numbers of colonies on Reef 21-064 only.
Table 5. Summary of manta tow survey results for the Pompey sector.
|
Reef |
Shelf Position |
Tows |
COTS |
COTS per tow |
Median % Live Coral Cover |
Median % Dead Coral Cover |
Median % Soft Coral Cover |
Reef Status |
|
20-353 |
Mid |
25 |
0 |
0 |
0 to 5 |
0 |
0 to 5 |
NO |
|
21-064 |
Mid |
23 |
5 |
0.22 |
20 to 30 |
0 to 5 |
0 to 5 |
IO |
|
Overall GBR average for last survey - 2008 |
ALL |
|
|
0.08 |
10 to 20 |
0 to 5 |
0 to 5 |
|
|
Long term average value |
MID |
|
|
0.28 |
30 to 40 |
0 to 5 |
5 to 10 |
|
|
Average last survey - 2008 |
MID |
|
|
1.16 |
30 to 40 |
0 to 5 |
0 to 5 |
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Table 6. Summary of SCUBA search survey results for the Pompey sector.
|
Reef |
Shelf |
COTS
<5cm |
COTS
>5 cm |
COTS >15cm |
COTS >25cm |
WS |
BBD |
BrB |
SEB |
Drupella |
|
21-550 |
M |
0 |
0 |
0 |
0 |
2 |
0 |
0 |
0 |
13 |
|
22-084 |
M |
0 |
1 |
0 |
7 |
4 |
0 |
0 |
3 |
2 |
|
Overall GBR average for last survey - 2008 |
ALL |
0 |
0.054 |
0.34 |
0.57 |
10 |
0.18 |
3.1 |
6.9 |
8.1 |
|
Long term average value |
M |
0.14 |
0.36 |
0.86 |
1.9 |
13 |
0.23 |
5.5 |
4.5 |
15 |
|
Average last survey - 2008 |
M |
0 |
0.2 |
1.4 |
3 |
19 |
0.5 |
6.9 |
9.3 |
14 |
WS = White Syndrome, BBD = Black Band Disease, BrB = Brown Band Disease, SEB
= Skeletal Eroding Band Disease.
References
English, S., Wilkinson, C. and
Baker, V. (1997) Survey Manual for Tropical Marine Resources (2nd
Edition). Australian Institute of Marine Science. Townsville.
This
project is
partially
supported
by the
Marine and
Tropical
Sciences
Research
Facility
For further information contact
Dr. Hugh Sweatman, AIMS
Telephone: +61 7 4753 4470
Fax: +61 7 4753 4288
Email: h.sweatman@aims.gov.au
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