Escape Reef) and listed in Table l . This survey was carried out in concert with a survey of of survey a with in concert out was carried survey l . in This Table listed and Reef) Escape
the (coral trout) survey were adopted as "random' as were adopted survey trout) (coral the
from late January to late March 1983 and during two weeks of May 1983 are shown shown are 1983 May of weeks two during and 1983 March late to January late from
and "chosen" sites. Survey sites on the leeward sides of the 57 reefs selected randomly for for randomly selected reefs 57 of the sides leeward the sites on Survey sites. "chosen" and one another, yet many adjacent clams were unresponsive to the presence of gametes in the the in gametes of presence the to unresponsive were clams adjacent yet many another, one
transects across the continental shelf. Two types of sites were examined: "random" sites sites "random" examined: were sites of types Two shelf. continental the across transects
coral trout trout coral
(Fig. l) in the chronological order in which they were examined (except for reef no. 00, 00, no. reef for (except examined were they which in order chronological the in l) (Fig.
water (Braley, 1984). The density of these clams on a given coral reef may depend on on depend may reef coral given a on clams these of density The 1984). (Braley, water
gathered, particularly for the largest species species largest the for particularly gathered,
strategy. strategy.
relatively undisturbed clam populations where basic demographic information can be be can information demographic basic where populations clam undisturbed relatively
percent of of percent
many reefs within the GBR System is necessary to understand their overall reproductive reproductive overall their understand to necessary is System GBR the within reefs many
clam densities are lacking. The Great Barrier Reef (GBR) is the last large area having having area large last the is (GBR) Reef Barrier Great The lacking. are densities clam
gested by Beckvar (1981) and Gwyther and Munro (1981), are not yet known. Seventy Seventy known. yet not are (1981), Munro and Gwyther and (1981) Beckvar by gested
same or adjacent reefs. Knowledge of a broad-scale distribution of clam densities on on densities clam of distribution broad-scale a of Knowledge reefs. adjacent or same
availability of optimum substrata for settlement and a critical density of broodstock on the the on broodstock of density critical a and settlement for substrata optimum of availability
(Roeding). (Roeding).
Ricard, 1978), 1978), Ricard,
1969; Hester and Jones, 1974; Bryan and McConnell, 1976; Pearson, 1977; 1977; Hirschberger, 1976; Pearson, McConnell, 1974; and Bryan and 1969; Jones, Hester
1980). These cover individual coral reefs or lagoons, but broad-scale estimates of giant giant of estimates broad-scale but lagoons, or reefs coral individual cover These 1980).
derasa
Distribution and Abundance of the Giant Clams Clams Giant the of Abundance and Distribution
Fifty-seven reefs (over 817 km of the GBR; between 20°ll'S-l4°27'S) surveyed surveyed 20°ll'S-l4°27'S) between GBR; the of km 817 (over reefs Fifty-seven
The critical densities of giant clams required to assure success in fertilisation, as sug- as fertilisation, in success assure to required clams giant of densities critical The
be be
Previous clam density estimates include: include: estimates density clam Previous
the northernmost and southernmost areas. Distributions of of Distributions areas. southernmost and northernmost the
abundance decreased southwards: it is rare south of 19°S 19°S while of south rare is it southwards: decreased abundance
Abstract-Fifty-seven reefs were surveyed over 817 km of the Great Barrier Reef. Reef. Barrier Great the of km 817 over surveyed were reefs Abstract-Fifty-seven
temperature and seasonal currents, while salinity or turbidity may be factors which limit limit which factors be may turbidity or salinity while currents, seasonal and temperature
Giant Clam Project, Zoology, James Cook University, Townsville, QW 4811 AUSTRALJA AUSTRALJA 4811 QW Townsville, University, Cook James Zoology, Project, Clam Giant
. .
T. gigas gigas T.
(Plectropomus (Plectropomus
T. crocea crocea T.
neighbors which released gametes naturally occurred within 9-m of of 9-m within occurred naturally gametes released which neighbors
T. derasa derasa T.
(Hamner, 1978), 1978), (Hamner,
spp.) by the Great Barrier Reef Marine Park Authority on 7 7 on Authority Park Marine Reef Barrier Great the by spp.)
Materials and Methods Methods and Materials
on the Great Barrier Reef. Reef. Barrier Great the on
R. D. D. R.
Introduction Introduction
BRALEY BRALEY
T. gigas gigas T.
Tridacna gigas gigas Tridacna
'. '.
Tridacna maxima maxima Tridacna
sites for the clam survey. Surveys of all all of Surveys survey. for clam the sites
T. T.
gigas gigas
and and
T. derasa T. derasa
suggest that limiting factors may may factors limiting that suggest
T. derasa derasa T.
Tridacna gigas gigas Tridacna
(Linnaeus) and and (Linnaeus)
was bimodal with peaks in in peaks with bimodal was
(McMichael, 1972; 1972; (McMichael,
(Hardy and Hardy, Hardy, and (Hardy
Tridacna gigas gigas Tridacna
T. derasa derasa T.
and and T. T. 216 Micronesica
Table I. Reefs or Islands (Is.) visited for the survey. Numbers and names are given with an indication of inner (i), middle (m), or outer (o) reef. Mean no. clams/ha listed as (T. gigaslha, T. derasa/ha).
Mean no. clams per ha Reef Reef at random sites Transect No. Reef name position (Tg, Td)
Innisfail Feather m (0.89, 0.0) 2 Peart m (1.3, 0.67) 3 Gilbey 0 (0, 0) 4 Wardle 0 (9.0, 5.5) 5 So. Barnard Is. (0, 0) 6 No. Barnard Is. (4.0, 0)
Cairns 7 Fitzroy Is. (12.0, 0) 8 Green Is. m (5.3, 3.6) 9 Upolu m (14.2, 0.9) 10 High Is. (12.0, 0) II Russell Is. (12.0, 0) 12 Maori m (0, 0) 13 Channel 0 (4.0, 0) 14 Northwest 0 (4.0, 0) 15 Flynn 0 (1.8, 2.7) 16 Milin 0 (0, 0.7) 17 Arlington m (4.0, 0) 18 Michaelmas m (1.8, 0) 19 Hastings m (0, 0)
Port 20 Batt m (8.0, 0) Douglas 21 Low Is. (0, 0) 22 Snapper Is. (0, 0) 23 Opal 0 (1.3, 0) 24 Tongue m (2.0, 0) 25 St. Crispin 0 (0.6, I.I)
Cooktown 26 Hope Is. (12.0, 0) 27 Cowlishaw (18.0, 0) 28 Egret m (52.0, 0) 29 Boulder m (56.0, 0) sites required the use of SCUBA. At 19 reefs, additional sites were "chosen" for their high clam densities. At the "random" sites, several I-ha areas of reef crest and slope (or patch reefs) were surveyed by setting a 150-m rope parallel to the reef front; and a 67-m tape was placed perpendicular to, and bisected by, one end of the 150-m rope to designate the area. At all inshore reefs (<15 km from the coast), and some middle (25-35 km from the coast) and outer (35- 70 km from the coast) continental shelf reefs, five 50-m x 20-m quadrats were placed lengthwise from the reef crest down the slope and surveyed. Since I was the only one of 2 or 3 divers collecting the clam density data I was able to survey the following
empty shells were concentrated rather than scattered amongst living clams. Although such such Although clams. living amongst scattered than rather were concentrated shells empty
underwater. Counts began after the first group of clams was observed. Areas were deter- were Areas observed. was clams of group first the after began Counts underwater. present study. study. present
areas of disturbance were rare, these data were excluded from mortality counts in the the in counts mortality from excluded were data these rare, were disturbance of areas
reefs; for each 50-m 50-m each for reefs;
areas: for each I-ha plot, 0.3-ha was surveyed at mid-shelf reefs and 0.5-ha at outer-shelf outer-shelf at 0.5-ha and reefs mid-shelf at surveyed was 0.3-ha plot, I-ha for each areas:
mined with a measuring tape or estimated by speed of towing over a known distance. distance. known a over towing of speed by estimated or tape measuring a with mined
initially selected by a viewer from the surface, followed by an observer being towed towed being observer an by followed surface, the from viewer a by selected initially
Instances of probable clam poaching were encountered on outer-shelf reefs where where reefs outer-shelf on encountered were poaching clam probable of Instances
Townsville Townsville
Whitsunday Whitsunday
Cooktown Cooktown
Transect Transect
Lizard Lizard
Flattery-
x x
Reef Reef
20-m quadrat, 500 500 quadrat, 20-m
No. No.
57 57
56 56
55 55
49 49 54 54
48 48 53 53
47 47
52 52
46 46
51 51
50 50
44 44
43 43
42 42
41 41
45 45
40 40
38 38
37 37
36 36
35 35
34 34 39 39
33 33
32 32
31 31
30 30
Vol. Vol.
John Brewer Brewer John
Havana Is. Is. Havana
Pandora Pandora
Lodestone Lodestone
Stucco Stucco
Myrmidon Myrmidon
Dip Dip
Hook Is. Is. Hook
Two Is. Is. Two
Plaster Plaster
Carter Carter Hook Hook
Line Line
odr Is Border
Hicks Hicks
Macgillivray Macgillivray
al Is Eagle
Martin Martin
Linnet Linnet
Day Day
Low Low
Forrester Forrester
Lizard Is. Is. Lizard
Williamson Williamson
Ribbon no. 4 4 no. Ribbon
Ribbon no. 6 6 no. Ribbon
Ribbon no. 5 5 no. Ribbon
no. 15043 15043 no.
20. December 1987 1987 December 20.
Reef name name Reef
(continued) (continued)
Table I. I. Table
odd Is Wooded
. .
m
. .
2 2
was surveyed. The "chosen" sites were were sites "chosen" The surveyed. was
. .
position position
Reef Reef
m m
m m
m m
m m
m m
m m
0 0
m m
m m
m m
0 0
0 0 m m
m m
m m
0 0
0 0
0 0
0 0
0 0
0 0
0 0
Mean no Mean
at at
(36.0, 0) 0) (36.0,
(24
(0.5, (0.5,
(3.3 (4.5, 9.0) 9.0) (4.5,
(4.0, (4.0,
random random
(0.7, (0.7, (2
(1.3, 18.0) 18.0) (1.3,
20 7 (2.0, (6.2, 5.3) 5.3) (6.2,
53 6 (5.3,
07 4 (0.7,
(3.5, 1.2) 1.2) (3.5,
(2.7, 0.9) 0.9) (2.7,
(4.0, 0) 0) (4.0,
(Tg, Td) Td) (Tg,
0 26 (0,
(0, 8.5) 8.5) (0,
(0, 0) 0) (0,
(0, (0,
(0, (0,
(0, 2.0) 2.0) (0, (0, 0) 0) (0,
(0, 0) 0) (0,
(0, (0,
(0, (0,
(0, 0) 0) (0,
(0, (0,
.
.
. .
7
, 2 0,
clams per ha ha per clams
, ,
, ,
0) 0)
0) 0)
36
8.7) 8.7)
0) 0)
8
8.0) 8.0)
1.3) 1.3)
10
12
.
.
.
.
.
0) 0)
5) 5)
0) 0)
0) 0)
7) 7)
.
.
.
.
sites sites
0) 0)
0) 0)
0) 0)
7) 7) 217 217
' '
"\ "\
"-.. "-..
\. \.
\. \.
:u49 :u49
,~B ,~B
" "
--
' '
--
---
--
' '
' '
-
' '
('.~
HJ HJ
2qo 2qo
4
50 50
l l
REEF REEF
zi..·· zi..··
~5 ~5
u, u,
;a
1 1
. .
•• ••
contour-
~o ~o
1 1
RS RS
to to
12~ 12~
TE TE
bathymetric bathymetric
10.0 10.0
LOME LOME
' '
\ \
N N
t t
\ \
KI KI
1;; 1;;
100m 100m
'\ '\
I I
-.-52' -.-52'
CENTRAL CENTRAL
50 50
. .
NORTH-CENTRAL NORTH-CENTRAL
,zsl ,zsl
GREAT GREAT BARRIER
Qld
sampling sampling along sites central the north-central to GBR.
\. \.
2:; 2:;
\ \
'\ '\
55 55
.,
' '
_,.,54 _,.,54
9 9
'\ '\
derasa derasa
\ \
I I
I I
I I
• •
I I
T. T.
\ \
I I
I I
I I
\ \
2;;. 2;;.
\ \
.1•t .1•t
·1•3 ·1•3
and and
13 13
14 14
•
,
1,, 1,,
112 112
,1:; ,1:;
·
i,, i,,
~; ~;
\ \
J7, J7,
18\ 18\
:~ :~
\ \
::) ::)
:
.,15\ .,15\
"'~
I I
I I
I I
I I
I I
I I
.-oo .-oo
G)~3 G)~3
,
[tZ5 [tZ5
8:,-:
• •
5+ 5+
Tridacna gigas gigas Tridacna
, , ¾ '·<:
,:,;:-.···,,24\ ,:,;:-.···,,24\
•.:----.. •.:----..
-
. .
Barrier Barrier Reef Marine Park Authority's companion map of the GBR, November 1982.
Numbered Numbered reefs are named in legend of Table I. This figure is modified after the Great
I
. .
Fig
INGHAM INGHAM
--20°s --20°s
--18° --18° I I
vey (GBRMPA) in late 1984 found a single individual of of individual 1984 a single found late in vey (GBRMPA)
hl ef ot f 19°33 of south reefs shelf
These data exclude obvious mortalities from clam poaching at outer-shelf reefs no. 4 and and 4 no. reefs at outer-shelf poaching clam from mortalities obvious exclude data These derasa derasa
Tridacna gigas gigas Tridacna
31. The mean percentages of dead clams from the observed populations of of populations observed the from clams dead of percentages mean The 31.
p<0
cantly more abundant at Escape Reef than either combined "chosen" sites sites "chosen" combined either than Reef Escape at abundant more cantly
the Flattery-Lizard transect on an island reef reef island an on transect Flattery-Lizard the sities sities
borderline as a mid-shelf reef. Although there was no significant difference between den- between difference significant no was there Although reef. mid-shelf a as borderline
dom" sites sites dom"
reef (no. 00, Fig. 3) densities of of densities 3) Fig. 00, (no. reef and and
sites the highest densities of of densities highest the sites
High densities at "random" sites occurred in the Cairns and Cooktown transects. At At transects. Cooktown and Cairns the in occurred sites "random" at densities High reef sites. sites. reef
"chosen" "chosen"
see Figure 3. 3. Figure see
southernmost southernmost
sites (9 reefs) reefs) (9 sites Random Random
Chosen Chosen
.
(12 reefs) reefs) (12
2 southern transects transects southern 2 Random Random
(45 reefs) reefs) (45
5 5
5. 5.
4. 4.
2. 2. 3. No living living No 3.
01) 01)
Figures Figures
I. I.
of of
Table 2 Table
northern transects transects northern
were 10.4% and 12.7%, respectively. respectively. 12.7%, and 10.4% were
There were 47 dead dead 47 were There
T. derasa T. derasa
Four hundred and six live live six and hundred Four Tridacna derasa derasa Tridacna
Tridacna gigas gigas Tridacna
or combined "random" "random" combined or
sites high densities were found found were densities high sites
. .
(~
1 1
46
Mean and standard deviation of clam densities at 57 57 at densities clam of deviation standard and Mean
and 2 show clam densities at "random" sites at 57 reefs: for "chosen" sites sites "chosen" for reefs: at 57 sites "random" at densities clam 2 show and
,=9.998, ,=9.998,
is rare south of 19°S, but although no live live no although but 19°S, of south rare is
at "chosen" and "random" sites sites "random" and "chosen" at
transects. The only inshore reef on which which on reef inshore only The transects.
T. gigas gigas T.
was present on on (of 57) 36 was present
p
Number of clams per hectare hectare per clams of Number
was present at 25 "random" and 9 9 and "random" at 25 present was
1
S, one long-dead long-dead one S,
<
were found in the Whitsunday transect, south of 19°S 19°S latitude. of south transect, Whitsunday the in found were
0.001)
T. derasa derasa T.
T. gigas gigas T.
236.6 236.6
0
7.8 7.8
sites sites
T. gigas gigas T.
T
.
6 6
T. gigas gigas T.
. .
Vol. 20 Vol.
. .
± ±
± ±
± ±
gigas gigas
Discussion Discussion
196
1.4 1.4
(~
12
and 38 dead dead 38 and
occurred on outer-shelf reefs in the northernmost northernmost the in reefs outer-shelf on occurred
46
.
Results Results
6 6
. .
.
7 7
,=9
in in
December 1987 1987 December
eesgiiatyhge (3/a ta "ran- than (134/ha) higher significantly were
and 261 live live 261 and
T. gigas gigas T.
all five northern transects (Table 2). Escape Escape 2). (Table transects northern five all
.
(Two (Two
907, 907,
± ±
"random" "random"
s
(tm,=0.952 (tm,=0.952
.
p<0.001). p<0.001).
was found. A second coral trout sur- trout coral second A found. was
d. are shown. shown. are d.
ls., no. 45) that may be considered considered be may that 45) no. ls.,
T. derasa derasa T.
5.5 5.5
5.9 5.9
2
T. derasa derasa T.
.
9 9
T. gigas gigas T.
random random
T. derasa derasa T.
± ±
± ±
± ±
8
7.4 7.4
7.3 7.3
T
"chosen" "chosen"
.
sites and 17 (of 19) 19) 17 (of and sites
T. derasa derasa T.
. .
3 3
gigas gigas
ns), ns),
sites and 9 9 and sites
from the 57-reef survey. survey. 57-reef the from
at Hook ls. (reef no (reef ls. Hook at
were noted. noted. were
T. derasa derasa T.
were found at outer- at found were
sites. At "random" "random" At sites.
was present was in in was present was
239.4 239.4
chosen chosen
10
T. derasa derasa T.
T. gigas T. gigas
6.5 6.5
T
.
. .
7 7
Cton=4.249, Cton=4.249,
gigas gigas
± ±
± ±
± ±
was signifi- was
sites. sites.
7.8 7.8
"chosen" "chosen"
184 184
13
.
+ +
6 6
and and
. .
51) 51)
219 219 T. T.
ha ha
shells shells
25 25 ha
. .
ha ha
ha ha
5 5
empty empty
sampled: sampled:
Poachers) Poachers)
0 0 5-0
( (
.
1.00 1.00
0.25-1.00 0.25-1.00
0
Reefs Reefs are displayed
> >
~o.o ~o.o
. .
(no. (no. clams/ha) at 57
Area Area
+Many +Many
• •
o o
derasa derasa
T. T.
,;• ,;•
. .
.. ..
< <
,0.> ,0.>
and and
·
(no. (no. clams/ha) "chosen" ( reefs at 19
'o.°' 'o.°'
SITES SITES
and and inshore portions cross-shelf the of
-
, ,
~
-<.. -<..
derasa derasa
00, 00, Escape Reef, is included comparison for
. .
T. T.
mid-shelf
dacna dacna gigas
. .
i
, ,
and and
Tr
0 0
., .,
RANDOM RANDOM Tridacna Tridacna gigas 0 0 ., ., 0 0 € z z 0 0 u u ...J ...J < < l: l: II) II) D.. D.. ILi ILi D: D: :c :c ILi ILi u u < < I- D: D: ILi ILi Abundance Abundance of the giant clams Abundance of the the of Abundance . . . . with with other reefs. Numbered reefs are named Table in I sites) sites) on the GBR (refer to Fig 2). Reef no transects transects (see also Fig. I and Table I) reefs ( "random" "random" reefs ( sites) on the 'S GBR between and 20°11 14°27'E 2 from north to south and for for and outer-shelf from to north south 3 . . . . Fig Fig 6' 6' ., ., ~o ~o () () 0~ 0~ z z ci ci l: l: Ill Ill ..J ..J a:: a:: < < u u Q. Q. I- J: J: a:: a:: w w LLI LLI u u w w < < a:: a:: ,._: ,._: a, a, '°'q, '°'q, .,o .,o #;o #;o ~o ~o 1)1 1)1 'V. 'V. 0 0 .._o .._o CHOSEN CHOSEN !P"' !P"' ., ., € 0 ~o ~o 0 0 ,._,,.,, ,._,,.,, t t SI TES TES SI o"' o"' /1, /1, .r~ .r~ ~- ~ 0-i) 0-i) - b,(, b,(, ...... o o • • < < ?;,•, ?;,•, .-~ .-~ .. .. Area Area .,, .,, -i) -i) > > .. .. 0.05 0.05 o.o o.o 0.25 0.25 1.00 1.00 .r .r 5-0.25 5-0.25 sampled: sampled: - ha ha ha ha 1.00 1.00 ':, ':, ha ha ha ha - et et al., Ayling, Ayling, . . outer-shelf outer-shelf reef in in situ on the north- indicate indicate a steady 5 5 T. T. derasa. gigas gigas derasa derasa . . occurs occurs in spring to mid- T. T. T 30. 30. 227. 227. Tridacna Tridacna gigas, Tridacna derasa - - and and 24:21 3: 221 3: per per hectare at T. T. gigas individuals individuals on the extreme outer reefs of . . 1987) 1987) these current patterns and larval Tridacna Tridacna gigas . . Aquaculture Aquaculture T. T. gigas , , . . is is common at 19°S and as far south as the T. gigas gigas T. Micronesica Micronesica References References Cited T. T. derasa Larger Larger numbers of dead clams were found in the north- at higher higher at latitudes ultimately be may temperature, to due A A biological survey of selected reefs in the central section of the Great . . submitted submitted lo GBRMPA by Sea Research. 53 pp. ACKNOWLEDGMENTS ACKNOWLEDGMENTS . . . . spawning spawning and growth of the giant clams , , while while salinity and/or turbidity may limit Repl . . 1977), 1977), though it was not found in surveys in the Capricorn Braley, Braley, PhD Thesis in in Palau, Caroline Islands T. gigas gigas T. is common common is on inshore reefs potentially affected by seasonal fluc- ; ; , , University University of New South Wales 22°S), 22°S), the where Coral Sea water mass predominant is (A L. L. 1985 , , . . is restricted oceanic restricted primarily environments to is Heslinga, and (Munro - Reproduction Reproduction in the giant clams out of of out T. T. gigas - . . T. T. gigas Reproduction Reproduction and Recruitment Giant of Clams and Some Aspects of their Larval Juvenile and . . Ayling, Ayling, A ., ., M Tridacna Tridacna squamosa . . comm., comm., 1986). Conversely, Biology. Biology. PhD Thesis central central Great Barrier Reef and Papua New Guinea. Coral Reefs and and Barrier Barrier Reef Marine Park I thank the Great Great thank I the Barrier Marine Reef Park Authority for making possible this survey A A GBRMPA coral trout survey of the Far-North section (Lizard Is.-Torres Strait) Currents Currents in the GBR lagoon at 19°S, 147°50'E (near Townsville) set from west to Population Population densities of these species are higher further north (from Cairns to Lizard Tridacna Tridacna derasa . . . . 1977). At At 1977). 16°23'S, 145°34'E (near Batt Reef and Low Isles) the current north flows from Braley, Braley, R. D. 1984 Beckvar, Beckvar, N. 1981. Cultivation Ayling, Ayling, A School School of Zoology, University of New South Wales for use of equipment. --. --. 1987. 1983), whereas whereas 1983), increase increase from my southernmost transects toward the Far Northern areas (Ayling and use of equipment equipment of use travel and to reef Escape aboard his research vessel Torito, El to and the in in 1984 also recorded numbers of live/dead transects. transects. Densities of combined live/dead varied from 14-24/ha, while densities of live of giant clams in conjunction conjunction clams giant coral of in trout the with survey. thank also I Starck Dr. for Walter 1985). They They also scattered found several 1985). seasonal seasonal spawning and southerly drift of the larvae. Ayling, Ayling, 1985) ernmost ernmost areas presumably due to poaching. These densities for February-October February-October and south (but less intensely) from October-February (Orr, 1933; only only /ha clams varied from 0-17 north north from January June to and from south to east from July to December (Pickard but but the minor recruitment in the southern part of the GBR may have resulted from the Cresswell Cresswell and Greig, 1978). Since gamete release in survival survival of young The The apparent fade drift drift could be accounting a factor the observed for distribution of this species GBR. the on Is.) summer summer (Braley, 1984 Bunker Bunker group (A. Ayling, pers. comm., 1986) tuations tuations in salinity and turbidity. These distributions suggest that temperature may limit Swains Swains Reefs (Pearson pers the Swains group group Swains the (2l 222 222 and and another at a small outer-shelf reef in the Whitsunday transect (Ayling and Ayling, Ricard, G Ricard, Orr, A. P. P. A. Orr, Pickard, G. G. Pickard, etr F Hester, ero, R Pearson, cihe, D McMichael, Hamner, Hamner, rswl, G Cresswell, Hardy ishegr W Hirschberger, Gwyther, J., Munro, Munro, J., Gwyther, Bryan, Bryan, Great Barrier Reef and Western Coral Sea. Austr. Gov't Pub!. Serv Pub!. Gov't Austr. Sea. Coral Western and Reef Barrier Great ceedings of the Third International Coral Reef Symposium. pp pp Symposium. Reef Coral International Third the of ceedings dacna maxima maxima dacna dacnidae). Aquaculture Aquaculture dacnidae). , , Br. Mus Br. tl. a. Fish Mar. atoll. Rev International Coral Reef Symposium Reef Coral International Western Caroline Islands, April April Islands, Caroline Western 34:267-281. 34:267-281. during the south-east trade wind season wind trade south-east the during J. T J. P . . W. W. M . . . . . . 0 J . . . . 42(2):8-15 , Hardy , L., L., G . , , 1933. 1933. . . , McConnell, D. B D. McConnell, , 1978 oe, E Jones, . . R. . . . . . . ogy .R, ei,C, ogre F Rougerie, C., Henin, R., J. Donguy, ra Br. ReefExped Barr. Great F. F. . . , , 1977 . . Greig 1978 , , 1980 Physical and chemical conditions in the sea in the neighbourhood of the Great Barrier Reef. Reef. Barrier Great the of neighbourhood the in sea in the conditions chemical and Physical S 1975. 1975. Quantitative balance and production of of production and balance Quantitative J. J. (Roeding), at One Tree Island, Capricorn Group, Queensland. Proceedings of the Second Second the of Proceedings Queensland. Group, Capricorn Island, Tree One at (Roeding), . . . . . . . . . . Rev. Rev. L. L. A. A. C. C. . . , , . . Impact of foreign vessels poaching giant clams giant poaching vessels foreign of Impact M lntraspecific competition in in competition lntraspecific rdci ca tcs nHlnRe, aa, etr aoie Islands Caroline Western Palau, Reef, Helen on stocks clam Tridacnid . 1981. 1981. 36: 17-22. 17-22. 36: rwh rate Growth 1969 A 1974. 1974. 24 . . . . : : . . 197-217 1978. 1978. 1976 Spawning induction and rearing of larvae of tridacnid clams (Bivalvia: Tri- (Bivalvia: clams tridacnid of larvae of rearing and induction Spawning Ecology of of Ecology A survey of giant clams, Tridacnidae, on Helen Reef, a Western Pacific Pacific Western a Reef, Helen on Tridacnidae, clams, giant of survey A 1975 . . . . , , 1928-1929 Currents and water properties in the north-central Great Barrier Reef Reef Barrier Great north-central the in properties water and Currents population size and mantle coloration in the small giant clam, clam, giant small the in coloration mantle and size population . . . . Vol. Vol. . . Status of giant clam stocks (Tridacnidae) on Helen Reef, Palau, Palau, Reef, Helen on (Tridacnidae) stocks clam giant of Status I Mar . . : : 241-254. 241-254. Austr 20 Tridacna Tridacna . . Fish. Rev. Rev. Fish. . . December December . . . . J. Mar J. Tridacna crocea Tridacna c. Rep Sci. . . 1977 in Palau. Pacif Palau. in Tridacna maxima maxima Tridacna . . 38(4): 15-18. 15-18. 38(4): Freshw . . . . 1987 1987 2:37-86. 2:37-86. A review of the physical oceanography of the the of oceanography physical the of review A 599-605 . . Res. Res. , , a burrowing bivalve. Oecologia (Berl.) (Berl.) Oecologia bivalve. burrowing a . . . . . . Austr Sci. Sci. Canberra. Canberra. 29 . . : in the Takapoto lagoon Takapoto in the 23 23 345-353 . . Fish. Fish. : 467 - 36(7) 472 . . . . : : 8-11 . . . . Mar. Fish. Fish. Mar. . . In : : Pro- Tri- 223 223